CN112694915A - Organic solid waste double-layer furnace body wet type ash discharge fixed bed gasification furnace and gasification method - Google Patents
Organic solid waste double-layer furnace body wet type ash discharge fixed bed gasification furnace and gasification method Download PDFInfo
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- CN112694915A CN112694915A CN202011616418.7A CN202011616418A CN112694915A CN 112694915 A CN112694915 A CN 112694915A CN 202011616418 A CN202011616418 A CN 202011616418A CN 112694915 A CN112694915 A CN 112694915A
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/02—Fixed-bed gasification of lump fuel
- C10J3/20—Apparatus; Plants
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/72—Other features
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/72—Other features
- C10J3/82—Gas withdrawal means
- C10J3/84—Gas withdrawal means with means for removing dust or tar from the gas
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/16—Integration of gasification processes with another plant or parts within the plant
- C10J2300/1625—Integration of gasification processes with another plant or parts within the plant with solids treatment
Abstract
The invention discloses a wet ash-discharging fixed bed gasifier with an organic solid waste double-layer furnace body and a gasification method, wherein the gasifier comprises a feeding device, a reaction zone furnace body comprising an upper section furnace body and a lower section furnace body, a furnace top gasification agent air inlet, a middle section gasification agent air inlet, a furnace bottom gasification agent air inlet, a coal gas air outlet and a slag discharging device, an annular cavity is formed between the upper section furnace body and the lower section furnace body, the coal gas air outlet is arranged on the side wall of the lower section furnace body corresponding to the annular cavity and is positioned between the furnace top gasification agent air inlet and the middle section gasification agent air inlet, and the slag discharging device is arranged in water and comprises an ash tray, a slag crushing ring, a grate supporting. The gasifier can be applied to the gasification treatment of various carbon-containing organic solids, solves the problems of high tar content and coal gas leakage at a feed inlet of a counter-flow gasification device with coal gas moving in the opposite direction of a material layer, and simultaneously solves the problem of high carbon content in solid-phase ash slag of a downstream gasification device with coal gas moving in the same direction of the material layer.
Description
Technical Field
The invention relates to the field of solid waste treatment and recycling, in particular to a wet ash discharge fixed bed gasification furnace with an organic solid waste double-layer furnace body and a gasification method.
Background
At present, domestic organic solid waste with higher heat value or treated organic solid waste with higher heat value is treated by a thermochemical conversion mode, and reduction, recycling and harmlessness of the organic solid waste can be realized by the thermochemical conversion mode. The main thermochemical conversion modes include incineration, pyrolysis and gasification, wherein the incineration means that excessive air is introduced to completely oxidize organic solid waste into flue gas and incombustible solid product ash and fly ash at high temperature, the heat energy in the high-temperature flue gas is converted into electric energy for utilization, and nitrogen, sulfur and chlorine elements contained in the organic solid waste can be converted into polluting gases such as nitrogen oxide, oxysulfide, hydrogen chloride and the like under the completely oxidizing atmosphere; meanwhile, heavy metals can migrate partially into the flue gas under the high-temperature oxidation atmosphere. The pyrolysis adopts an external heating mode to crack organic components in the solid waste to generate pyrolysis gas, pyrolysis oil and pyrolysis carbon, and as the organic solid waste components are complex and a large amount of nitrogen, sulfur, chlorine and oxygen elements are transferred into the pyrolysis oil, the pyrolysis oil has low quality and is difficult to be economically utilized; meanwhile, ash in the organic solid waste raw material can be enriched in the pyrolytic carbon.
At present, organic solid waste gasification furnaces are mainly a down-flow gasification furnace with gas in a material layer moving in the same direction as the material layer and a counter-flow gasification furnace with gas in the material layer moving in the opposite direction to the material layer, wherein in the down-flow gasification furnace, materials and a gasification agent simultaneously enter a furnace body from the upper end, and combustible gas is led out of the furnace body from the lower end; in the counter-flow gasification furnace, materials enter the furnace body from the upper end, a gasification agent enters the furnace body from the lower end, combustible gas is led out of the furnace body from the upper end, and the counter-flow gasification device has the problems of high tar content and coal gas leakage at a feed inlet.
The domestic gasification furnace commonly used for organic solid waste adopts a negative pressure state to realize the discharge of gas in the furnace and the control of reaction conditions in the furnace, so that the combustible gas of the device is possibly mixed with air to reach explosion conditions to generate potential safety hazards, and meanwhile, the negative pressure state is difficult to promote the reaction rate of a series of gasification reactions in which the gas participates so as to limit the treatment capacity of the gasification furnace.
Disclosure of Invention
The present invention is directed to solving, at least to some extent, one of the technical problems in the related art. Therefore, the invention aims to provide a wet ash discharge fixed bed gasification furnace with an organic solid waste double-layer furnace body and a gasification method. The organic solid waste double-layer furnace body wet ash discharge fixed bed gasification furnace can be applied to gasification treatment of carbon-containing organic solids such as household garbage, medical waste, organic hazardous waste, industrial organic solid waste, biomass, coal and the like, solves the problems of high tar content and coal leakage at a feed inlet of a counter-flow gasification device with coal gas moving in the opposite direction of a material layer, and simultaneously solves the problem of high carbon content in solid-phase ash slag of a concurrent gasification device with coal gas moving in the same direction of the material layer.
In one aspect of the invention, the invention provides a wet ash discharge fixed bed gasification furnace with an organic solid waste double-layer furnace body. According to the embodiment of the invention, the organic solid waste double-layer furnace body wet type ash discharge fixed bed gasification furnace comprises:
a feeding device;
the reaction zone furnace body is arranged below the feeding device and comprises an upper section furnace body and a lower section furnace body, the diameter of the upper section furnace body is smaller than that of the lower section furnace body, the upper section furnace body is sleeved in the lower section furnace body, an annular cavity is formed between the upper section furnace body and the lower section furnace body, and a sealing piece is arranged at the top of the annular cavity; a grate is arranged at the bottom in the lower section furnace body;
the furnace top gasifying agent air inlet is arranged on the side wall of the lower section furnace body corresponding to the top of the annular cavity, penetrates through the annular cavity and extends into the upper section furnace body;
the middle-section gasification agent air inlet is arranged below the furnace top gasification agent air inlet, is arranged on the side wall of the lower-section furnace body corresponding to the annular cavity, penetrates through the annular cavity and extends into the upper-section furnace body;
the furnace bottom gasification agent inlet is communicated with the lower part of the grate;
the gas outlet is arranged on the side wall of the lower-section furnace body corresponding to the annular cavity and positioned between the furnace top gasifying agent inlet and the middle-section gasifying agent inlet, and the gas outlet is communicated with the annular cavity;
arrange the sediment device, arrange the sediment device setting in aqueous and be located the below of hypomere furnace body, arrange the sediment device and include ash tray, disintegrating slag circle, grate support piece, first grey sword, the ash tray sets up the below of grate, disintegrating slag circle is cyclic annular and overlaps and establish in the ash tray in the water seal and disintegrating slag circle and upper portion furnace body press from both sides the cover welding together, grate support piece sets up the below of grate just is located in the disintegrating slag circle, first grey sword is the setting of coulter shape on the inside wall of ash tray.
According to the organic solid waste double-layer furnace body wet ash discharge fixed bed gasification furnace provided by the embodiment of the invention, the multi-stage supply of the gasification agent is realized through the furnace top gasification agent air inlet, the middle section gasification agent air inlet and the furnace bottom gasification agent air inlet, the stable control of the oxidation layer is realized through the accurate and stable multi-stage oxidation, and the tar in the fuel gas is fully cracked, so that the quality of the produced combustible gas is improved, and the lower carbon content of the furnace slag is ensured. The gasification requirements of the carbon-containing organic solids with different volatile matter contents and fixed carbon contents can be met by adjusting the supply amount of the gasification agent at different positions and the position of the middle section gasification agent air inlet. The upper and lower furnace bodies form a higher annular cavity area, so that sufficient settling space can be provided for particles in fuel gas, the particles in the combustible gas are reduced, the temperature of the combustible gas at a gas outlet is reduced, and the gas flowing mode of the upstream and downstream of the upper and lower sections can avoid the environmental pollution caused by the gas leakage at the top feed inlet of the traditional counter-flow gasification furnace. Simultaneously, the ash tray and the disintegrating slag circle constitute the ash tray water seal jointly, because there is certain pressure in the stove, extrude the water in the ash tray to the take the altitude and realize having pressure liquid seal, thereby gaseous can emerge safe pressure release from the aquatic when the stove internal pressure is too big, adopt the ash tray liquid seal wet process to arrange the malleation state in can effectual control stove, reduce the potential safety hazard of gasifier. Therefore, the organic solid waste double-layer furnace body wet ash discharge fixed bed gasification furnace can be applied to gasification treatment of carbon-containing organic solids such as household garbage, medical waste, organic hazardous waste, industrial organic solid waste, biomass, coal and the like, solves the problems of high tar content and coal leakage at a feed inlet of a counter-flow gasification device with coal gas moving in the opposite direction of a material layer, and simultaneously solves the problem of high carbon content in solid-phase ash slag of a downstream gasification device with coal gas moving in the same direction of the material layer.
In addition, the organic solid waste double-layer furnace body wet ash discharge fixed bed gasification furnace according to the above embodiment of the invention may further have the following additional technical features:
in some embodiments of the invention, the gasifier further comprises a gasification agent distribution regulator, and the gasification agent distribution regulator is movably arranged at the outlet end of the bottom gasification agent inlet up and down and is positioned in the grate. Therefore, the gasification agent distribution regulator can better adapt to the uniform gas distribution under the condition of small flow of the gasification agent inlet at the bottom of the furnace.
In some embodiments of the invention, the furnace further comprises a material distribution device, and the material distribution device is arranged above the upper section furnace body. From this, the distributing device realizes the even cloth of material in the dry layer.
In some embodiments of the present invention, the slag discharging device further comprises a second ash knife disposed at the bottom of the grate support and a broken slag block disposed on the sidewall of the grate support.
In some embodiments of the invention, the outside of the upper furnace body and the lower furnace body is a membrane water wall or a jacket water wall. Therefore, the membrane type water-cooled wall reduces the outward radiation heat of the furnace body, effectively avoids the slag bonding phenomenon caused by high temperature in the furnace, also reduces the gas temperature of the gas outlet, and can effectively avoid the safety problem of jacket explosion caused by bulging compared with the traditional mode of adopting a water jacket.
In some embodiments of the invention, the membrane water wall is a shell and tube membrane water wall or a coil membrane water wall.
In some embodiments of the present invention, the number of the top gasifying agent inlets is plural, and the plural top gasifying agent inlets are symmetrically arranged in the circumferential direction.
In some embodiments of the present invention, the number of the middle-stage gasifying agent gas inlets is plural, and the plural middle-stage gasifying agent gas inlets are symmetrically arranged in the circumferential direction.
In some embodiments of the present invention, the gas outlets are multiple, and the multiple gas outlets are symmetrically arranged along the circumferential direction.
In some embodiments of the invention, the inner diameter of the upper furnace body is 0.3-8.0 m, and the inner diameter of the lower furnace body is 0.4-8.0 m.
In some embodiments of the present invention, the feeding device includes a feeding port, an upper valve of a feeding buffer bin, a lower valve of the feeding buffer bin, and an inert gas purging inlet, which are sequentially arranged from top to bottom, and a charging and pressure-releasing port of the feeding buffer bin is arranged at a side portion of the feeding buffer bin. Therefore, the safety of the operation of the gasification furnace can be effectively ensured by the design of the inert gas purging air inlet and the charging and discharging pressure of the feeding buffer bin.
In some embodiments of the invention, the height of the upper furnace body is 40% -80% of the total height of the reaction zone furnace body. From this, can guarantee that the toroidal cavity that forms between upper segment furnace body and the hypomere furnace body has sufficient height, further be favorable to cooling down the combustible gas product to particulate matter in the combustible gas provides sufficient settlement space, reduces the particulate matter in the combustible gas.
In some embodiments of the invention, the height of the upper furnace body from the grate is 20% -60% of the total height of the reaction zone furnace body. Therefore, carbon dioxide generated by the oxidation layer reacts with the carbon layer of the reduction section to generate required carbon monoxide, and the distance between the upper-section furnace body and the grate is set to be within the range, so that the carbon dioxide and the carbon layer have reasonable reaction contact time.
In some embodiments of the invention, the ratio of the thickness of the annular cavity to the inner diameter of the reaction zone furnace body is (0.1-0.3): 1.
In another aspect of the invention, the invention provides a gasification method by adopting the organic solid waste double-layer furnace wet ash discharge fixed bed gasification furnace of the embodiment. According to an embodiment of the present invention, the organic solid waste gasification method comprises:
(1) organic solid waste is supplied to the furnace body of the reaction zone through the feeding device, and inert protective gas is blown to the lower part of the feeding device through the inert gas blowing inlet;
(2) supplying a gasification agent to the reaction zone furnace body through a furnace top gasification agent air inlet, a middle section gasification agent air inlet and a furnace bottom gasification agent air inlet, wherein the reaction zone furnace body comprises a drying layer, a dry distillation layer, an upper oxidation layer, a reduction layer, a lower oxidation layer and an ash residue layer which are sequentially arranged from top to bottom;
(3) gasifying the organic solid waste to obtain combustible gas and ash, and discharging the combustible gas out of the reaction zone furnace body through a gas outlet;
(4) and discharging the ash into an ash tray, crushing the ash through extrusion of a grate support and a slag crushing ring and rotation of the grate support, and discharging the crushed ash out of the ash tray along the direction of a first ash knife.
Therefore, the organic solid waste gasification method can be applied to gasification treatment of carbon-containing organic solids such as household garbage, medical waste, organic hazardous waste, industrial organic solid waste, biomass, coal and the like, solves the problems of high tar content and coal leakage at a feed inlet of a counter-flow gasification device with coal gas moving in the opposite direction of a material layer, and solves the problem of high carbon content in solid-phase ash slag of a co-flow gasification device with coal gas moving in the same direction of the material layer.
In addition, the organic solid waste gasification method according to the above embodiment of the present invention may further have the following additional technical features:
in some embodiments of the invention, a pressure is present in the reaction zone furnace in the range of 0 to 20.0 kPa. Therefore, potential safety hazards in the negative pressure operation process are avoided by controlling the furnace to maintain the positive pressure state, and meanwhile, compared with the negative pressure state, the gasification reaction rate is higher and the gasifier treatment capacity is larger when the positive pressure reaction condition is adopted in the furnace.
In some embodiments of the invention, the gasification agent comprises at least one of steam, carbon dioxide, air, oxygen rich (oxygen concentration 21 v% to 100 v%).
In some embodiments of the invention, the gasifying agent is a mixed gas of water vapor and oxygen-enriched air, and the ratio of the mass of the water vapor to the volume of the oxygen in the oxygen-enriched air is 0-8.0 kg/Nm3Therefore, the gasification temperature of materials with different ash melting points can be maintained below the softening point temperature of ash, and the influence of ash slagging on the normal operation of the gasification furnace is prevented.
In some embodiments of the invention, the gasifying agent is a mixed gas of steam and air, and the temperature of the gasifying agent is 40-70 ℃, so that the air can bring a proper amount of steam into an oxidation-reduction layer of the gasification furnace to carry out water-gas reaction of carbon and steam, and carbon monoxide and hydrogen are generated.
In some embodiments of the invention, the gasifying agent is a mixed gas of carbon dioxide and oxygen-enriched air, and the ratio of the mass of the carbon dioxide to the volume of oxygen in the oxygen-enriched air is 0-19.5 kg/Nm3. Therefore, carbon dioxide and carbon can be subjected to reduction reaction to generate carbon monoxide, the heat of the reaction layer is absorbed, the temperature of the reaction layer is maintained in a reasonable range, and the quality of coal gas and slag are kept from slagging.
In some embodiments of the present invention, the air inflow of the top gasifying agent inlet and the middle gasifying agent inlet is 30% to 90% of the total air inflow of the gasifying agent, wherein the air inflow of the top gasifying agent inlet is 70% to 90% of the total air inflow of the top gasifying agent inlet and the middle gasifying agent inlet, the air inflow of the middle gasifying agent inlet is 10% to 30% of the total air inflow of the top gasifying agent inlet and the middle gasifying agent inlet, and the air inflow of the bottom gasifying agent inlet is 10% to 70% of the total air inflow of the gasifying agent. Therefore, by controlling the air inflow of each air inlet of the gasification furnace within the range, the volatile matter in the upper oxidation layer, which generates tar, can be directly oxidized into coal gas by the oxygen in the gasification agent, thereby avoiding the generation of tar, and simultaneously, the carbon in the lower oxidation layer is oxidized by the oxygen in the gasification agent to generate coal gas.
In some embodiments of the present invention, the temperature of the drying layer is 20 to 200 ℃, the temperature of the carbonization layer is 200 to 600 ℃, the temperature of the upper oxidation layer is 600 to 1200 ℃, the temperature of the reduction layer is 600 to 1100 ℃, the temperature of the lower oxidation layer is 600 to 1100 ℃, and the temperature of the ash layer is 200 to 600 ℃. Therefore, by controlling the temperature of each reaction area in the gasification furnace within the range, the reaction layer of the oxidation layer can maintain reasonable reaction temperature, the coal gas quality is ensured, and meanwhile, the reaction temperature of ash slag is lower than the softening point, and no slagging occurs.
In addition, it should be noted that all the features and advantages described for the organic solid waste double-layer furnace wet ash discharge fixed bed gasification furnace in the present invention are also applicable to the organic solid waste gasification method, and are not described herein again.
Additional aspects and advantages of the invention will be set forth in part in the description which follows and, in part, will be obvious from the description, or may be learned by practice of the invention.
Drawings
The above and/or additional aspects and advantages of the present invention will become apparent and readily appreciated from the following description of the embodiments, taken in conjunction with the accompanying drawings of which:
fig. 1 is a schematic structural view of a wet ash discharge fixed bed gasification furnace of an organic solid waste double-layer furnace according to an embodiment of the invention.
Fig. 2 is a front view of the slag discharging device according to the embodiment of the present invention.
Fig. 3 is a plan view of a slag discharge device according to an embodiment of the present invention.
Detailed Description
Reference will now be made in detail to embodiments of the present invention, examples of which are illustrated in the accompanying drawings, wherein like or similar reference numerals refer to the same or similar elements or elements having the same or similar function throughout. The embodiments described below with reference to the drawings are illustrative and intended to be illustrative of the invention and are not to be construed as limiting the invention.
In the description of the present invention, it is to be understood that the terms "center", "longitudinal", "lateral", "length", "width", "thickness", "upper", "lower", "front", "rear", "left", "right", "vertical", "horizontal", "top", "bottom", "inner", "outer", "axial", "radial", "circumferential", and the like, indicate orientations and positional relationships based on the orientations and positional relationships shown in the drawings, and are used merely for convenience in describing the present invention and for simplicity in description, and do not indicate or imply that the device or element so referred to must have a particular orientation, be constructed and operated in a particular orientation, and therefore, should not be construed as limiting the present invention.
Furthermore, the terms "first", "second" and "first" are used for descriptive purposes only and are not to be construed as indicating or implying relative importance or implicitly indicating the number of technical features indicated. Thus, a feature defined as "first" or "second" may explicitly or implicitly include at least one such feature. In the description of the present invention, "a plurality" means at least two, e.g., two, three, etc., unless specifically limited otherwise.
In the present invention, unless otherwise expressly specified or limited, the terms "mounted," "connected," "secured," and the like are to be construed broadly and can, for example, be fixedly connected, detachably connected, or integrally formed; can be mechanically or electrically connected; they may be directly connected or indirectly connected through intervening media, or they may be connected internally or in any other suitable relationship, unless expressly stated otherwise. The specific meanings of the above terms in the present invention can be understood by those skilled in the art according to specific situations.
In the present invention, unless otherwise expressly stated or limited, the first feature "on" or "under" the second feature may be directly contacting the first and second features or indirectly contacting the first and second features through an intermediate. Also, a first feature "on," "over," and "above" a second feature may be directly or diagonally above the second feature, or may simply indicate that the first feature is at a higher level than the second feature. A first feature being "under," "below," and "beneath" a second feature may be directly under or obliquely under the first feature, or may simply mean that the first feature is at a lesser elevation than the second feature.
In one aspect of the invention, the invention provides an organic solid waste double-layer furnace body wet ash discharge fixed bed gasification furnace, and referring to the attached drawing 1, the gasification furnace comprises a feeding device, a reaction zone furnace body, a furnace top gasification agent air inlet 6, a middle section gasification agent air inlet 15, a furnace bottom gasification agent air inlet 14, a coal gas air outlet 10 and a slag discharge device. The organic solid waste double-layer furnace wet ash discharge fixed bed gasification furnace according to the embodiment of the invention is further described in detail below.
According to an embodiment of the invention, referring to fig. 1, the feeding device comprises a feeding hole 1, a feeding buffer bin upper valve 2, a feeding buffer bin 3, a feeding buffer bin lower valve 4 and an inert gas purging air inlet 16 which are sequentially arranged from top to bottom, specifically, the feeding hole 1 is a conical feeding hole with a wide top and a narrow bottom, and a circular flange is welded at the lower part of the feeding hole. The feeding device is characterized in that the lower part of the feeding port 1 is a feeding buffer bin upper valve 2 and is connected through a flange, the furnace body at the lower part of the feeding buffer bin upper valve 2 is a feeding buffer bin 3, the lower part of the feeding buffer bin 3 is a feeding buffer bin lower valve 4, the feeding buffer bin upper valve, the feeding buffer bin and the feeding buffer bin lower valve are connected through flanges, the feeding buffer bin 3 is a narrow-upper wide-middle cylindrical structure, the feeding buffer bin side edge is provided with a feeding buffer bin pressure charging and discharging port 5, and the feeding buffer bin pressure charging and discharging port is horizontally arranged. Therefore, the safety of the operation of the gasification furnace can be effectively ensured by the design of the inert gas purging air inlet and the charging and discharging pressure of the feeding buffer bin.
According to an embodiment of the invention, referring to fig. 1, the reaction zone furnace body is arranged below the feeding device, the reaction zone furnace body comprises an upper section furnace body 8 and a lower section furnace body 9, the top end of the upper section furnace body is connected with a lower valve of the feeding buffer bin through a circular flange interface, the diameter of the upper section furnace body 8 is smaller than that of the lower section furnace body 9, the upper section furnace body 8 is sleeved in the lower section furnace body 9, an annular cavity is formed between the upper section furnace body and the lower section furnace body, and a sealing member (such as a flange) is arranged at the top of the annular cavity; the bottom in the lower section furnace body is provided with a grate 12.
In the embodiment of the present invention, specific values of the inner diameter of the upper furnace body and the inner diameter of the lower furnace body are not particularly limited, and those skilled in the art can optionally select the values according to actual situations, and as a preferable scheme, the inner diameter of the upper furnace body is 0.3 to 8.0m, and the inner diameter of the lower furnace body is 0.4 to 8.0 m.
Further, the height of the upper furnace body is 40% -80% of the total height of the reaction zone furnace body, such as 40%, 50%, 60%, 70%, 80% and the like. From this, can guarantee that the toroidal cavity that forms between upper segment furnace body and the hypomere furnace body has sufficient height, further be favorable to cooling down the combustible gas product to particulate matter in the combustible gas provides sufficient settlement space, reduces the particulate matter in the combustible gas.
Further, the height of the upper furnace body from the grate is 20% to 60%, for example, 20%, 30%, 40%, 50%, 60%, etc., of the total height of the reaction zone furnace body, so that carbon dioxide generated from the oxidation layer reacts with the carbon layer of the reduction zone to generate carbon monoxide as required, and the distance between the upper furnace body and the grate is set to the above range, so that carbon dioxide and the carbon layer can have reasonable reaction contact time.
Furthermore, the ratio of the thickness of the annular cavity to the inner diameter of the furnace body of the reaction zone is (0.1-0.3): 1, such as 0.1:1, 0.2:1, 0.3:1 and the like. The inventor discovers, if toroidal cavity's thickness is too big, can reduce the reaction space in the stove, lead to gasifier throughput to show and reduce, and if toroidal cavity's thickness undersize, neither do benefit to subsiding of particulate matter, also do not benefit to the staff and overhaul toroidal cavity, and be above-mentioned thickness scope through controlling toroidal cavity, can compromise the throughput of gasifier simultaneously and the effect of subsiding of particulate matter in the gas, avoid appearing the problem that influences the gas quality because of the ash and slag come-up when the gas flow is great, still be convenient for realize toroidal cavity's installation and maintenance. It should be noted that the thickness of the annular cavity refers to the horizontal width of the single-sided annular cavity.
Further, the outer sides of the upper furnace body and the lower furnace body are membrane water walls 11 or jacket water walls, and the membrane water walls can be tubular or coil type, and can also be replaced by water jackets. The upper furnace body, the lower furnace body and the membrane water-cooled wall are fixed through flanges. Therefore, the membrane type water-cooled wall 11 reduces the outward radiation heat of the furnace body, effectively avoids the slag bonding phenomenon caused by high temperature in the furnace, also reduces the gas temperature of the gas outlet, and can effectively avoid the bulge problem compared with the traditional mode of adopting a water jacket.
According to the embodiment of the invention, referring to fig. 1, the furnace top gasification agent inlet 6 is horizontally arranged on the side wall of the lower furnace body 9 corresponding to the top of the annular cavity, penetrates through the annular cavity, and extends into the upper furnace body 8.
Furthermore, a plurality of top gasification agent inlets 6 are provided, and the top gasification agent inlets are symmetrically arranged along the circumferential direction. Therefore, the plurality of furnace top gasifying agent air inlets are uniformly arranged in an annular mode, and uniform air distribution is realized through the plurality of furnace top gasifying agent air inlets and the cavity area in the furnace top.
According to the embodiment of the invention, referring to fig. 1, the middle-section gasifying agent inlet 15 is horizontally arranged below the furnace top gasifying agent inlet 6, and the middle-section gasifying agent inlet is arranged on the side wall of the lower-section furnace body corresponding to the annular cavity, penetrates through the annular cavity and extends into the upper-section furnace body.
Furthermore, the number of the middle-section gasifying agent air inlets is multiple, and the middle-section gasifying agent air inlets are symmetrically arranged along the circumferential direction, so that uniform air distribution is realized.
Furthermore, the number of the gas outlets is 1-3, and considering that the structure of the gasification furnace is more complicated when the number of the gas outlets is large, one gas outlet can be preferably arranged; in order to avoid the furnace type structure being too complex, when a plurality of gas outlets are arranged, the number of the gas outlets which can be optimized is 2 or 3, and the gas outlets can be uniformly and horizontally arranged along the circumferential direction of the furnace wall, so that uniform gas outlet can be effectively realized, and the problem of nonuniform reaction of the furnace layer caused by the gas outlets on one side is avoided.
In accordance with an embodiment of the present invention, and with reference to FIG. 1, the bottom gasification agent inlet 14 communicates with the lower portion of the grate 12. The air inlet of the furnace bottom gasification agent is connected with an external air source through a pipeline positioned below the furnace bottom gasification agent, and air distribution ports are distributed on the grate to realize the uniform air distribution of the air inlet at the furnace bottom.
According to the embodiment of the invention, referring to fig. 1, the gas outlet 10 is horizontally arranged on the side wall of the lower furnace body 9 corresponding to the annular cavity and is positioned between the furnace top gasification agent inlet 6 and the middle section gasification agent inlet 15, and the gas outlet is communicated with the annular cavity.
According to the embodiment of the invention, referring to fig. 2 and 3, the slag discharging device is arranged in water and located below the lower furnace body 9, the slag discharging device comprises an ash tray 13, a slag crushing ring 18, a grate support member 20 and a first ash knife 19, the ash tray 13 is arranged below the grate 12, the slag crushing ring 18 is welded with an upper membrane wall in a ring shape and is sleeved in the ash tray 13, the grate support member 20 is arranged below the grate 12 and is located in the slag crushing ring 18, and the first ash knife 19 in a plow shape is arranged on the inner side wall of the ash tray. Further, referring to fig. 2 and 3, the slag discharging device further includes a second ash knife 21 and a clinker block 22, the second ash knife 21 is disposed at the bottom of the grate support 20, and the clinker block 22 is disposed on the side wall of the grate support 20, thereby better breaking the ash. It should be noted that the first plaster cutter refers to a large plaster cutter, and the second plaster cutter refers to a small plaster cutter. Specifically, ash is discharged from the reaction zone furnace into the ash tray 13, the ash in the ash tray 13 is crushed by the co-extrusion crushing action of the clinker ring 18, the grate support 20, the second ash knife 21 and the clinker block 22 simultaneously with the rotation of the grate support 20, and the crushed ash is discharged from the ash tray in the direction of the first ash knife. From this, the ash tray water seal is constituteed jointly with the disintegrating slag circle to the ash tray, because there is certain pressure in the stove, extrudees the water in the ash tray to take the altitude and realize having the pressure liquid seal, thereby gas can emerge safe pressure release from the aquatic when the stove internal pressure is too big, thereby the mode that adopts ash tray liquid seal wet process to arrange the sediment can effectual control the malleation state in the stove, reduces the potential safety hazard of gasifier.
Further, referring to fig. 1, the gasification furnace further comprises a gasification agent distribution regulator 17, wherein the gasification agent distribution regulator 17 is vertically movably arranged at the outlet end of the furnace bottom gasification agent air inlet 14 and is positioned in the furnace grate 12, and the gasification agent distribution in the furnace grate is regulated by vertically moving the gasification agent distribution regulator 17, so that the uniform air distribution under the condition of small flow of the furnace bottom gasification agent air inlet is better adapted.
Further, referring to fig. 1, the gasification furnace further includes a material distribution device 7, and the material distribution device 7 is disposed above the upper-stage furnace body. From this, distributing device 7 realizes the even cloth of material in dry layer.
Compared with the prior art, the wet ash-discharging fixed bed gasification furnace with the organic solid waste double-layer furnace body has the advantages that: an organic solid waste gasification furnace pass through furnace roof gasification agent air inlet, middle section gasification agent air inlet and stove bottom gasification agent air inlet at the reaction zone, realize the multistage supply of gasification agent, realize the stable control of oxide layer through accurate stable multistage oxidation, make the tar in the gas fully schizolysis improve the combustible gas quality, guaranteed the lower carbon content of slag again. The gasification requirements of carbon-containing organic solids with different volatile matter contents and fixed carbon contents can be met by adjusting the supply amount of the gasification agents at different positions and the position of the middle section gasification agent air inlet, and the grate gasification agent distribution regulator can better adapt to uniform air distribution under the condition of small flow of the furnace bottom gasification agent air inlet. The intermediate layer between upper segment furnace body and the hypomere furnace body forms the cavity of take the altitude to let the subside of particulate matter in the gas, effectively reduce particulate matter content, be malleation reaction condition in the stove, it is faster than gasification reaction rate than negative pressure state, the gasifier handling capacity is bigger, adopts the malleation state in ash tray liquid seal wet process row sediment mode can effectual control stove simultaneously, reduces the potential safety hazard of gasifier. The membrane type water-cooled wall is used for more stable cooling operation of the furnace body, the bulging phenomenon of a water jacket can not occur, and the safety of the operation of the gasification furnace can be effectively guaranteed by the aid of the filling and pressure-relief design of the inert gas purging air inlet, the feeding buffer bin and the slag bin.
In another aspect of the present invention, the present invention provides a gasification method using the above-mentioned embodiment of the organic solid waste double-layer furnace wet ash discharge fixed bed gasification furnace, the method comprising the following steps:
(1) organic solid waste is supplied to the furnace body of the reaction zone through the feeding device, and non-combustible gas is swept to the lower part of the feeding device through the inert gas sweeping air inlet.
(2) And the gasification agent is supplied to the reaction zone furnace body through a furnace top gasification agent air inlet, a middle section gasification agent air inlet and a furnace bottom gasification agent air inlet, and the reaction zone furnace body comprises a drying layer, a dry distillation layer, an upper oxidation layer, a reduction layer, a lower oxidation layer and an ash residue layer which are sequentially arranged from top to bottom.
In this step, a gasifying agent is fed into the furnace by a blower to bring the pressure inside the furnace into a positive pressure state, the pressure inside the reaction zone furnace body is 0 to 20.0kPa (for example, 0kPa, 0.1kPa, 1kPa, 2kPa, 4kPa, 6kPa, 8kPa, 10kPa, 12kPa, 14kPa, 18kPa, 20kPa, etc.), the gasifying agent pressure at the gas inlet is 0 to 20kPa, and the pressure is a gauge pressure measured by a pressure gauge. Therefore, the positive pressure state is maintained in the control furnace, potential safety hazards in the negative pressure operation process are avoided, and meanwhile, compared with the negative pressure state, the gasification reaction rate is higher and the gasifier treatment capacity is larger when the positive pressure reaction condition exists in the furnace.
Further, the gasifying agent includes at least one of water vapor, carbon dioxide, air, and oxygen-rich gas (oxygen concentration 21 v% to 100 v%).
Further, the gasifying agent is a mixed gas of water vapor and oxygen-enriched air, and the ratio of the mass of the water vapor to the volume of the oxygen in the oxygen-enriched air is 0-8.0 kg/Nm3E.g. 0, 0.1kg/Nm3、0.5kg/Nm3、1.0kg/Nm3、2.0kg/Nm3、3.0kg/Nm3、4.0kg/Nm3、5.0kg/Nm3、6.0kg/Nm3、7.0kg/Nm3、8.0kg/Nm3And the like. The inventor finds that when the mixed gas of the water vapor and the oxygen-enriched gas is adopted as the gasifying agent, the ratio of the mass of the water vapor to the volume of the oxygen in the oxygen-enriched gas is controlled to be in the range, so that the gasifying temperature of materials with different ash melting points can be maintained below the softening point temperature of ash, and the ash slag is prevented from influencing the normal operation of the gasification furnace. Preferably, the ratio of the mass of the water vapor to the volume of the oxygen in the oxygen-enriched air is set to 1.0 to 6.0kg/Nm3. If the ratio of the mass of the water vapor to the volume of the oxygen in the rich oxygen is too large, the gasification reaction temperature may be reduced, which causes the content of the effective components such as carbon monoxide and hydrogen in the coal gas to be reduced, and the heat value of the coal gas to be reduced. If the ratio of the mass of the steam to the volume of the oxygen in the rich oxygen is too small, the gasification reaction temperature may be raised to make the temperature of the oxidation layer higher than the softening point temperature of the ash, so that the ash slagging gasification furnace cannot normally operate.
Further, the gasifying agent is a mixed gas of steam and air, and the temperature of the gasifying agent is 40-70 ℃, such as 40 ℃, 50 ℃, 60 ℃, 70 ℃ and the like. The inventors have found that when a mixed gas of steam and air is used as the gasifying agent, by controlling the temperature of the gasifying agent to be in the above range, air can be introduced into the oxidation-reduction layer of the gasification furnace with a suitable amount of steam to cause a water-gas reaction of carbon and steam, thereby generating carbon monoxide and hydrogen. If the temperature of the gasifying agent is too low, the amount of water vapor possibly brought in is less, so that the temperature of an oxidation layer is too high, and if the temperature of the oxidation layer is higher than the softening point temperature of ash, serious slagging phenomenon can be caused, and the normal operation of the gasification furnace is influenced; if the temperature of the gasifying agent is too high, the amount of water vapor possibly brought in is too high, and the reaction temperature is too low, so that the quality of the coal gas is reduced.
Further, the gasifying agent is a mixed gas of carbon dioxide and oxygen-enriched air, and the ratio of the mass of the carbon dioxide to the volume of oxygen in the oxygen-enriched air is 0-19.5 kg/Nm3E.g. 0, 0.10kg/Nm3、0.5kg/Nm3、1.0kg/Nm3、2.0kg/Nm3、3.0kg/Nm3、5.0kg/Nm3、8.0kg/Nm3、10.0kg/Nm3、12.0kg/Nm3、15.0kg/Nm3、16.0kg/Nm3、18.0kg/Nm3、19.5.0kg/Nm3And the like, so that carbon dioxide and carbon are subjected to reduction reaction to generate carbon monoxide, the heat of the reaction layer is absorbed, the temperature of the reaction layer is maintained in a reasonable range, and the quality of coal gas and slag are kept from slagging. Preferably, the ratio of the mass of carbon dioxide to the volume of oxygen in the enriched oxygen is set to 1.0 to 15.0kg/Nm3. The inventors have found that if the ratio of the mass of carbon dioxide to the volume of oxygen in the enriched oxygen is too large, this may result in too large a reduction in the temperature of the reaction layer, resulting in poor gas quality.
Furthermore, the air inflow of the top gasification agent air inlet and the middle gasification agent air inlet is 30% -90% (e.g. 30%, 40%, 50%, 60%, 70%, 80%, 90%, etc.) of the total air inflow of the gasification agents, wherein the air inflow of the top gasification agent air inlet is 70% -90% (e.g. 70%, 80%, 90%, etc.) of the total air inflow of the top gasification agent air inlet and the middle gasification agent air inlet, and the air inflow of the middle gasification agent air inlet is 10% -30% (e.g. 10%, 20%, 30%, etc.) of the total air inflow of the top gasification agent air inlet and the middle gasification agent air inlet; the air inflow of the bottom gasification agent air inlet is 10-70% (such as 10%, 20%, 30%, 40%, 50%, 60%, 70% and the like) of the total air inflow of the gasification agent. Therefore, by controlling the air inflow of each air inlet of the gasification furnace within the range, the volatile matter in the upper oxidation layer, which generates tar, can be directly oxidized into coal gas by the oxygen in the gasification agent, thereby avoiding the generation of tar, and simultaneously, the carbon in the lower oxidation layer is oxidized by the oxygen in the gasification agent to generate coal gas.
Further, the temperature of the dry layer is 20 to 200 ℃ (e.g., 20 ℃, 60 ℃, 80 ℃, 100 ℃, 120 ℃, 140 ℃, 180 ℃, 200 ℃, etc.), the temperature of the dry distillation layer is 200 to 600 ℃ (e.g., 200 ℃, 250 ℃, 300 ℃, 350 ℃, 400 ℃, 450 ℃, 500 ℃, 550 ℃, 600 ℃, etc.), the temperature of the upper oxidation layer is 600 to 1200 ℃ (e.g., 600 ℃, 700 ℃, 800 ℃, 900 ℃, 1000 ℃, 1100 ℃, 1200 ℃, etc.), the temperature of the reduction layer is 600 to 1100 ℃ (e.g., 600 ℃, 700 ℃, 800 ℃, 900 ℃, 1000 ℃, 1100 ℃, etc.), the temperature of the lower oxidation layer is 600 to 1100 ℃ (e.g., 600 ℃, 700 ℃, 800 ℃, 900 ℃, 1000 ℃, 1100 ℃, etc.), and the temperature of the ash layer is 200 to 600 ℃ (e.g., 200 ℃, 250 ℃, 300 ℃, 350 ℃, 400 ℃, 450 ℃, 500 ℃, 600 ℃, etc.). Therefore, by controlling the temperature of each reaction area in the gasification furnace to be in the range, the reaction layer of the oxidation layer can maintain reasonable reaction temperature, the quality of coal gas is ensured, and meanwhile, the reaction temperature of ash is lower than the softening point, and no slagging occurs.
(3) And (3) carrying out gasification reaction on the organic solid waste to obtain combustible gas and ash, and discharging the combustible gas out of the reaction zone furnace body through a gas outlet.
(4) And discharging the ash into an ash tray, crushing the ash through extrusion of a grate support and a slag crushing ring and rotation of the grate support, and discharging the crushed ash out of the ash tray along the direction of a first ash knife.
Therefore, the organic solid waste gasification method can be applied to gasification treatment of carbon-containing organic solids such as household garbage, medical waste, organic hazardous waste, industrial organic solid waste, biomass, coal and the like, solves the problems of high tar content and coal leakage at a feed inlet of a counter-flow gasification device with coal gas moving in the opposite direction of a material layer, and solves the problem of high carbon content in solid-phase ash slag of a co-flow gasification device with coal gas moving in the same direction of the material layer.
The invention will now be described with reference to specific examples, which are intended to be illustrative only and not to be limiting in any way.
Example 1
The structure of the organic solid waste double-layer furnace body wet ash discharge fixed bed gasification furnace is shown in figures 1-3, wherein in figures 1-3: 1-feeding hole, 2-feeding buffer bin upper valve, 3-feeding buffer bin, 4-feeding buffer bin lower valve, 5-feeding buffer bin pressure charging and releasing hole, 6-furnace top gasifying agent air inlet, 7-distributing device, 8-upper furnace body, 9-lower furnace body, 10-gas air outlet, 11-membrane water-cooled wall, 12-grate, 13-ash tray, 14-furnace bottom gasifying agent air inlet, 15-middle section gasifying agent air inlet, 16-inert gas purging air inlet, 17-grate gasifying agent distribution regulator, 18-slag crushing ring, 19-first ash knife, 20-grate supporting piece, 21-second ash knife and 22-slag crushing block.
(1) Feeding of the feedstock
The organic solid waste gasification furnace of the embodiment is composed of a feeding device, a gasification device and a slag discharging device. The feeding device is composed of a feeding hole 1, an upper feeding buffer bin valve 2, a feeding buffer bin 3, a lower feeding buffer bin valve 4, a pressure charging and releasing port 5 of the feeding buffer bin and an inert gas purging air inlet 16. The feed inlet 1 is positioned at the topmost end of the gasification furnace, is provided with a feed buffer bin upper valve 2 between the feed inlet 1 and the feed buffer bin 3, and is connected with the feed buffer bin upper valve through a flange. Install feeding surge bin lower valve 4 between feeding surge bin 3 and the upper segment furnace body 8 to through flange joint, feeding surge bin 3 side is equipped with the feeding surge bin pressure release mouth 5 that the level was arranged. The material gets into the gasifier from feed inlet 1, there is certain pressure in the stove this moment, feeding surge bin lower valve 4 keeps the encapsulated state, open feeding surge bin upper valve 2 and make the material in the feed inlet enter into feeding surge bin 3, feeding surge bin 3 is in the ordinary pressure state, close feeding surge bin upper valve 2 after adding the material in feeding surge bin 3, realize the sealing of feeding surge bin 3, fill pressure vent 5 through feeding surge bin and pressurize this moment, make pressure in feeding surge bin 3 unanimous with the internal pressure of reacting furnace, sweep air inlet 16 through feeding surge bin lower valve 4 lower part inert gas and let in nitrogen gas or carbon dioxide, make feeding surge bin lower valve 4 lower part atmosphere of valve be incombustible gas, open feeding surge bin lower valve 4, make the material in feeding surge bin 3 get into upper segment furnace body 8 under the effect of gravity and gasify. The material closes feeding surge bin lower valve 4 after getting into upper segment furnace body 8 completely in the feeding surge bin 3, fills pressure release mouth 5 through the feeding surge bin and carries out the pressure release, reaches the ordinary pressure state, opens feeding surge bin upper valve 2 and opens new round of feeding.
(2) Gasification of
Be equipped with three gasification agent air inlets in the furnace body, firstly furnace roof gasification agent air inlet 6 is located inert gas and sweeps 16 tops and the upper segment furnace body 8 intercommunication of upper segment furnace body below air inlet, runs through the annular cavity furnace roof gasification agent air inlet that upper segment furnace body 8 and hypomere furnace body 9 formed and is provided with a plurality of air inlets along circumference symmetry, realizes the even cloth wind in top through symmetrical arrangement. And the middle section gasification agent air inlet 15 is positioned at the middle section of the upper section furnace body 8, is horizontally arranged along the circumferential direction and is communicated with the upper section furnace body 8. And the third is a bottom gasifying agent inlet 14 which is communicated with the bottom grate 12, the bottom uniform air distribution is realized through the air distribution port of the grate 12, and a grate gasifying agent distribution regulator 17 is arranged in the grate 12. The even cloth wind of the edge of circumference air inlet 6 and grate 12 that 8 top sides of upper segment furnace bodies were evenly arranged can ensure that the material forms even stable reaction layer in gasification reaction zone, avoids appearing the phenomenon of inhomogeneous reaction. The middle section gasification agent air inlet 15 is used for controlling the position of the upper oxidation layer, the problem that the upper oxidation layer is too high or too low is avoided, when the gasification raw material is low in calorific value or the content of fixed carbon is low, the gasification agent supply quantity demand of the furnace bottom gasification agent air inlet 14 is less, and the small-flow uniform gas distribution is realized by reducing the height of the regulating grate gasification agent distribution regulator 17. The gasification agents introduced into the three gasification agent air inlets are air and water vapor.
(3) Gasification process
The gasification reaction zone of the organic solid waste gasification furnace is mainly positioned in the upper-section furnace body 8 and the lower-section furnace body 9 and can be divided into a drying layer, a dry distillation layer, an upper oxidation layer, a reduction layer, a lower oxidation layer and an ash layer from top to bottom. The drying layer, the dry distillation layer and the upper oxidation layer are positioned in the upper section furnace body 8, the lower oxidation layer and the ash layer are positioned in the lower section furnace body 9, and the reduction layer is positioned at the junction of the upper section furnace body 8 and the lower section furnace body 9. The material gets into upper furnace body 8 from feeding surge bin 3 in, realizes the even cloth of material on the dry layer by distributing device 7, and the dry layer temperature is in 20 ~ 200 ℃ within range, and the moisture in the material is heated the evaporation and enters into the gaseous phase, and the material through drying gets into the dry distillation layer and releases the volatile, generates tar and coke, and the temperature on dry distillation layer is in 200 ~ 600 ℃ of scope. The tar and the coke enter the upper oxidation layer, the tar and the coke are subjected to oxidation reaction with oxygen in a gasifying agent to release heat, so that the temperature of the upper oxidation layer can reach 600-1200 ℃, meanwhile, part of the tar is cracked in a high-temperature region, the coke is only partially subjected to oxidation reaction due to insufficient gas-solid contact, the coke enters the reduction layer under the action of gravity of a material mainly comprising the coke, and carbon dioxide and water generated by oxidation of the upper oxidation layer and the coke of the reduction layer are subjected to gasification reaction, so that the quality of produced gas is improved. The coke which is not reacted in the reduction layer enters the lower oxidation layer and is further oxidized by the gasification agent introduced into the gasification agent inlet 14 at the bottom of the furnace to release heat. The heat of the reduction layer comes from the heat radiation of the upper oxidation layer and the lower oxidation layer, the temperature range is 600-1100 ℃, and the temperature range of the lower oxidation layer is 600-1100 ℃. The coke is completely oxidized in the lower oxidation layer and then is changed into slag to enter an ash layer above the grate 12, and the temperature of the ash layer is within 200-600 ℃. The gasification agent introduced into the air inlet of the furnace bottom gasification agent enters the ash layer through the grate air supply hole to exchange heat with the ash so as to realize the heating of the gasification agent and the cooling of the ash.
(4) Slag discharge
The fire grate 12 is located ash tray 13 top and fixes, can drive rotatoryly through the motor, and ash tray 13 constitutes ash tray water seal jointly with the disintegrating slag circle, because there is certain pressure in the stove, extrudees the water in ash tray 13 take the altitude to realize pressing the liquid seal, thereby gas can burst out from the aquatic safety pressure release when the stove internal pressure is too big, avoids the too big potential safety hazard that produces the explosion of stove internal pressure. The fixed knife is welded on the side wall of the ash tray, the lower end of the fixed knife is inserted into the water of the ash tray, the ash in the ash tray 13 is crushed along with the rotation of the grate support 20 under the extrusion action of the slag crushing ring 18 and the grate support 20, and the crushed ash is discharged out of the ash tray along the direction of the knife.
(5) Gas outlet
The reaction zone furnace body comprises a cylindrical upper section furnace body 8 with a short diameter and a cylindrical lower section furnace body 9 with a large diameter, the upper section furnace body 8 extends into the lower section furnace body 9 to form an annular cavity, a coal gas outlet 10 is arranged at the upper part of the annular cavity and communicated with the annular cavity area, the upper section furnace body is positioned at the top of the lower section furnace body 9 and is horizontally arranged, and the cavity area can realize uniform gas outlet. The outer membrane water wall 11 that is of upper segment furnace body 8 and hypomere furnace body 9 reduces the furnace body through membrane water wall 11 and outwards radiates the heat and effectively avoids the slagging scorification phenomenon because high temperature produces in the stove simultaneously, can also make coal gas outlet gas temperature reduce, and the mode that adopts the water jacket than the tradition simultaneously can effectively avoid the bulge problem.
The following concrete examples of the operation of the gasification furnace are as follows:
the inner diameter of the gasification furnace is 3.2m, the treated materials are domestic garbage, and the treatment capacity is 2.9 t/h. The main operating conditions and gasification results were as follows:
(1) industrial analysis of materials is shown in the following Table
(2) The operating conditions are as follows:
gasification pressure: 2000 Pa;
gasifying agent: air + water vapor;
air quantity: 3100Nm3/h；
Amount of water vapor: 260 kg/h.
(3) And (3) gasification result:
gas production: 4300Nm3/h；
The fuel gas comprises the following components: h2：12.54％，CO：17.20％，CH4：2.65％，CO2：10.05％，N2：57.2％，O2：0.27％，CnHm：0.09％；
Gasification efficiency: 68 percent;
carbon content of ash: 3.3 percent;
the tar content of the fuel gas is as follows:<1g/Nm3。
in the description herein, references to the description of the term "one embodiment," "some embodiments," "an example," "a specific example," or "some examples," etc., mean that a particular feature, structure, material, or characteristic described in connection with the embodiment or example is included in at least one embodiment or example of the invention. In this specification, the schematic representations of the terms used above are not necessarily intended to refer to the same embodiment or example. Furthermore, the particular features, structures, materials, or characteristics described may be combined in any suitable manner in any one or more embodiments or examples. Furthermore, various embodiments or examples and features of different embodiments or examples described in this specification can be combined and combined by one skilled in the art without contradiction.
Although embodiments of the present invention have been shown and described above, it is understood that the above embodiments are exemplary and should not be construed as limiting the present invention, and that variations, modifications, substitutions and alterations can be made to the above embodiments by those of ordinary skill in the art within the scope of the present invention.
Claims (10)
1. The utility model provides an organic solid useless double-deck furnace body wet-type ash discharge fixed bed gasifier which characterized in that includes:
a feeding device;
the reaction zone furnace body is arranged below the feeding device and comprises an upper section furnace body and a lower section furnace body, the diameter of the upper section furnace body is smaller than that of the lower section furnace body, the upper section furnace body is sleeved in the lower section furnace body, an annular cavity is formed between the upper section furnace body and the lower section furnace body, and a sealing piece is arranged at the top of the annular cavity; a grate is arranged at the bottom in the lower section furnace body;
the furnace top gasifying agent air inlet is arranged on the side wall of the lower section furnace body corresponding to the top of the annular cavity, penetrates through the annular cavity and extends into the upper section furnace body;
the middle-section gasification agent air inlet is arranged below the furnace top gasification agent air inlet, is arranged on the side wall of the lower-section furnace body corresponding to the annular cavity, penetrates through the annular cavity and extends into the upper-section furnace body;
the furnace bottom gasification agent inlet is communicated with the lower part of the grate;
the gas outlet is arranged on the side wall of the lower-section furnace body corresponding to the annular cavity and positioned between the furnace top gasifying agent inlet and the middle-section gasifying agent inlet, and the gas outlet is communicated with the annular cavity;
arrange the sediment device, arrange the sediment device setting in aqueous and be located the below of hypomere furnace body, it includes ash tray, disintegrating slag circle, grate support piece and first grey sword to arrange the sediment device, the ash tray sets up the below of grate, the disintegrating slag circle is cyclic annular and overlaps and establish in the ash tray, grate support piece sets up the below of grate just is located in the disintegrating slag circle, first grey sword sets up on the inside wall of ash tray.
2. The organic solid waste double-layer furnace body wet type ash discharge fixed bed gasification furnace according to claim 1, further comprising a gasification agent distribution regulator, wherein the gasification agent distribution regulator is arranged at the outlet end of the furnace bottom gasification agent gas inlet in a manner of moving up and down and is positioned in the grate;
optionally, the furnace also comprises a material distribution device, wherein the material distribution device is arranged above the upper section of the furnace body;
optionally, the slag discharge device further comprises a second ash knife and a slag breaking block, the second ash knife is arranged at the bottom of the grate support, and the slag breaking block is arranged on the side wall of the grate support.
3. The organic solid waste double-layer furnace body wet type ash discharge fixed bed gasification furnace according to claim 1, wherein the outer sides of the upper section furnace body and the lower section furnace body are membrane water-cooled walls or jacket water-cooled walls;
optionally, the membrane water wall is a shell and tube membrane water wall or a coiled tube membrane water wall.
4. The organic solid waste double-layer furnace body wet type ash discharge fixed bed gasification furnace according to claim 1, wherein a plurality of the furnace top gasification agent air inlets are symmetrically arranged along the circumferential direction;
optionally, a plurality of middle-section gasifying agent air inlets are arranged symmetrically along the circumferential direction;
optionally, the number of the gas outlets is multiple, and the multiple gas outlets are symmetrically arranged along the circumferential direction.
5. The organic solid waste double-layer furnace body wet type ash discharge fixed bed gasification furnace according to claim 1, wherein the feeding device comprises a feeding hole, an upper valve of a feeding buffer bin, the feeding buffer bin, a lower valve of the feeding buffer bin and an inert gas purging air inlet which are sequentially arranged from top to bottom, and a charging pressure relief opening of the feeding buffer bin is arranged on the side part of the feeding buffer bin.
6. The organic solid waste double-layer furnace body wet type ash discharge fixed bed gasification furnace according to any one of claims 1 to 5, wherein the inner diameter of the upper section furnace body is 0.3 to 8.0m, and the inner diameter of the lower section furnace body is 0.4 to 8.0 m;
optionally, the height of the upper furnace body is 40-80% of the total height of the reaction zone furnace body;
optionally, the height from the upper furnace body to the grate is 20-60% of the total height of the furnace body of the reaction zone;
optionally, the ratio of the thickness of the annular cavity to the inner diameter of the furnace body of the reaction zone is (0.1-0.3): 1.
7. The method for gasification by adopting the organic solid waste double-layer furnace body wet ash discharge fixed bed gasification furnace as claimed in any one of claims 1 to 6, is characterized by comprising the following steps:
(1) organic solid waste is supplied to the furnace body of the reaction zone through the feeding device, and inert protective gas is blown to the lower part of the feeding device through the inert gas blowing inlet;
(2) supplying a gasification agent to the reaction zone furnace body through a furnace top gasification agent air inlet, a middle section gasification agent air inlet and a furnace bottom gasification agent air inlet, wherein the reaction zone furnace body comprises a drying layer, a dry distillation layer, an upper oxidation layer, a reduction layer, a lower oxidation layer and an ash residue layer which are sequentially arranged from top to bottom;
(3) gasifying the organic solid waste to obtain combustible gas and ash, and discharging the combustible gas out of the reaction zone furnace body through a gas outlet;
(4) and discharging the ash into an ash tray, crushing the ash through extrusion of a grate support and a slag crushing ring and rotation of the grate support, and discharging the crushed ash out of the ash tray along the direction of a first ash knife.
8. The method of claim 7, wherein the pressure in the reaction zone furnace is 0 to 20.0 kPa;
optionally, the gasification agent comprises at least one of water vapor, carbon dioxide, air, oxygen enrichment;
optionally, the gasifying agent is a mixed gas of water vapor and oxygen-enriched air, and the ratio of the mass of the water vapor to the volume of the oxygen in the oxygen-enriched air is 0-8.0 kg/Nm3；
Optionally, the gasifying agent is a mixed gas of water vapor and air, and the temperature of the gasifying agent is 40-70 ℃;
optionally, the gasification agent is a mixed gas of carbon dioxide and oxygen-enriched air, and the ratio of the mass of the carbon dioxide to the volume of oxygen in the oxygen-enriched air is 0-19.5 kg/Nm3。
9. The method according to claim 7, wherein the air inflow of the top gasification agent air inlet and the middle gasification agent air inlet is 30-90% of the total air inflow of the gasification agents, wherein the air inflow of the top gasification agent air inlet is 70-90% of the total air inflow of the top gasification agent air inlet and the middle gasification agent air inlet, and the air inflow of the middle gasification agent air inlet is 10-30% of the total air inflow of the top gasification agent air inlet and the middle gasification agent air inlet; the air inflow of the furnace bottom gasification agent air inlet is 10% -70% of the total air inflow of the gasification agent.
10. The method according to claim 7, wherein the temperature of the drying layer is 20 to 200 ℃, the temperature of the retort layer is 200 to 600 ℃, the temperature of the upper oxidation layer is 600 to 1200 ℃, the temperature of the reduction layer is 600 to 1100 ℃, the temperature of the lower oxidation layer is 600 to 1100 ℃, and the temperature of the ash layer is 200 to 600 ℃.
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| CN (1) | CN112694915A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113265271A (en) * | 2021-05-21 | 2021-08-17 | 东莞蓝橙能源热电设备科技有限公司 | High-temperature rotating bed biomass full-gasification furnace |
| CN113333439A (en) * | 2021-05-31 | 2021-09-03 | 陕西久普环保科技有限公司 | Top-end moving blanking system and method of garbage pyrolysis gasification furnace |
-
2020
- 2020-12-31 CN CN202011616418.7A patent/CN112694915A/en active Pending
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113265271A (en) * | 2021-05-21 | 2021-08-17 | 东莞蓝橙能源热电设备科技有限公司 | High-temperature rotating bed biomass full-gasification furnace |
| CN113333439A (en) * | 2021-05-31 | 2021-09-03 | 陕西久普环保科技有限公司 | Top-end moving blanking system and method of garbage pyrolysis gasification furnace |
| CN113333439B (en) * | 2021-05-31 | 2023-06-23 | 陕西久普环保科技有限公司 | Top end moving blanking system and method of garbage pyrolysis gasification furnace |
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