CN210176799U - Modularized fire-resistant garbage gasification treatment device - Google Patents
Modularized fire-resistant garbage gasification treatment device Download PDFInfo
- Publication number
- CN210176799U CN210176799U CN201921193725.1U CN201921193725U CN210176799U CN 210176799 U CN210176799 U CN 210176799U CN 201921193725 U CN201921193725 U CN 201921193725U CN 210176799 U CN210176799 U CN 210176799U
- Authority
- CN
- China
- Prior art keywords
- tank body
- brick
- refractory
- fire prevention
- temperature
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
Images
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
The utility model discloses a modularized fire-resistant garbage gasification treatment device, which is used for gasifying screened organic garbage to obtain water gas, and comprises a tank body and an annular fireproof brick wall arranged in the tank body, wherein the top of the tank body is provided with a feed inlet, and the bottom of the tank body is provided with a grate for discharging and feeding materials; the internal feeding district, reaction zone and the cooling discharge area of divideing into in proper order down of follow of jar, the fire prevention brick wall sets up at the reaction zone, the fire prevention brick wall includes that the multilayer is coaxial and the laminating is in the fire prevention ring of jar internal wall, fire prevention ring includes a plurality of fire prevention modules that set up along the central angle such as jar body axis, fire prevention module and jar body can be dismantled and be connected. The utility model discloses a design original fire resistive construction for special modular structure to be convenient for later maintenance and change.
Description
Technical Field
The utility model belongs to the technical field of gu useless the processing, concretely relates to fire-resistant rubbish gasification equipment of modularization.
Background
The garbage is solid waste generated in daily life and production of human beings, has large discharge amount, complex and various components, pollution, resource and socialization, needs harmless, resource, reduction and socialization treatment, and can pollute the environment, influence the environmental sanitation, waste resources, destroy the safety of production and life and destroy the social harmony if the garbage cannot be properly treated. The garbage disposal is to rapidly remove the garbage, perform harmless treatment and finally reasonably utilize the garbage. The garbage disposal methods widely used today are sanitary landfills, high temperature composting and incineration. The purpose of garbage treatment is harmlessness, resource utilization and reduction.
And the waste incineration can achieve the effect of resource recycling, and steam generated by the heat generated by the incineration of the waste can drive a turbine generator to generate electricity. However, while there is concern about energy safety and climate change, the cost of disposing of waste is increasing worldwide, and these factors have increased the possibility of disposing of household waste in energy-intensive ways that have been used only for disposing of dangerous materials such as medical waste and asbestos. Therefore, the process of pyrolysis and gasification of garbage is developed by combining the current technical conditions to avoid secondary pollution. The garbage pyrolysis gasification is that the garbage is heated at high temperature in a closed chamber and is converted into synthesis gas, and the components of the synthesis gas are carbon monoxide and hydrogen. After filtration and chemical "cleaning" to remove toxic particles and gases, the fuel is burned to produce energy or converted to fuels such as methane, ethanol or synthetic diesel. Garbage vaporization can be used for quickly converting household garbage into energy, the garbage can be changed into assets from liabilities, and a clean energy source capable of being used on the spot is provided.
That is, the energy substances in the organic waste can be converted into synthesis gas which can be efficiently utilized as much as possible through the waste pyrolysis vaporization process, and meanwhile, the residual substances also have certain use value, so that the waste originally discarded is changed into available resources. The existing garbage gasification process usually adopts a vertical gasification furnace structure as a main reactor, a series of reactions are achieved in the furnace through different reaction zones, finally, the discharged gas is treated to obtain synthesis gas, and the slag is also treated to be used as building filler. The inside in order to insulate against heat of present reactor, all be equipped with the fire prevention brick structure, because of the inside temperature of reaction zone can reach 1200 ℃, if direct transfer heat, can lead to jar body material to produce irreversible change because of the temperature is higher to influence the structural strength of whole jar body. Therefore, the heat is effectively isolated by arranging the fireproof brick wall structure. The existing fireproof brick is only directly attached to the inside of the tank body, namely a disposable structure is fixed, but now in practical use, the pressure of a reaction zone is about 2.7-8.5MPa, and the operating temperature can be suddenly increased to 1700 ℃. Under high temperature and high pressure, the refractory material in the combustion chamber can generate a corrosion phenomenon, and the refractory brick is continuously thinned by the scouring of heated gas and molten slag. The existing firewall structure is an integrated structure, if the existing firewall structure needs to be repaired, the wall body of the whole area needs to be dismantled, and the firewall is rebuilt after the existing firewall structure is cleaned up, so that the cost is high and the efficiency is low.
SUMMERY OF THE UTILITY MODEL
In order to solve the problems existing in the prior art, the utility model provides a modularized fire-resistant garbage gasification treatment device.
The utility model discloses the technical scheme who adopts does: the modularized fire-resistant garbage gasification treatment device is used for carrying out gasification treatment on screened organic garbage to obtain water gas and comprises a tank body and an annular fireproof brick wall arranged in the tank body, wherein the top of the tank body is provided with a feed inlet, and the bottom of the tank body is provided with a grate for discharging and feeding air;
the internal feeding district, reaction zone and the cooling discharge area of divideing into in proper order down of follow of jar, the fire prevention brick wall sets up at the reaction zone, the fire prevention brick wall includes that the multilayer is coaxial and the laminating is in the fire prevention ring of jar internal wall, fire prevention ring includes a plurality of fire prevention modules that set up along the central angle such as jar body axis, fire prevention module and jar body can be dismantled and be connected.
Firstly, the utility model relates to a reactor structure among organic garbage's dry distillation gasification technology, dry distillation gasification technology refer to after screening crushing drying process with organic garbage, send into the process that the reaction takes place to react at the certain temperature and produce the water gas in the reaction tower quantitatively. The reaction tower is generally of a vertical structure and comprises a plurality of layers from top to bottom, and the reaction tower is divided into areas according to internal temperature. The material enters the tank body from the top and then reacts differently with the change of temperature.
The uppermost part is a dry layer, the temperature of which is at 100-300 ℃, the temperature of the layer is increased in a gradient way, and the temperature is higher closer to the lower part. The layer generally dries the crushed garbage which just enters the tank body, and has large space, and occupies 10-20% of the whole tank body. But will generally be provided with means for pressing the material downwards in the feed, thereby providing a continuous pushing force downwards. The garbage entering the drying area is firstly contacted with the pyrolyzed fuel gas in the upper area and dehydrated within 2-4 hours, the exhaust port is communicated with the inside of the tank body in the area, and at the moment, the fuel gas mixed steam is exhausted from the exhaust port.
The lower part of the drying layer is a dry distillation layer, namely a cracking layer, the temperature of the drying layer is 300-600 ℃, the garbage dried by the upper layer gradually falls into the cracking layer, and is heated at the same time, so that a pyrolysis reaction is carried out, most of volatile components in the garbage are separated from solids, and when the temperature is close to the edge of 600 ℃, only ash residues are basically left in the garbage. In the dry distillation layer, a plurality of organic wastes generate alkanes, carbon monoxide, tar and water vapor, and meanwhile, some sulfur-containing and chlorine-containing substances generate a small amount of hydrogen chloride and hydrogen sulfide gas, and the hydrogen chloride and the hydrogen sulfide gas are discharged along with the water vapor and are treated by a subsequent desulfurization tower.
The lower part of the dry distillation layer is an oxidation layer, the temperature of the oxidation layer is about 600-1200 ℃, and most of heat is released by violent reaction of residual ash and air. However, because the amount of oxygen supplied is controlled so that the amount of oxygen is insufficient for complete reaction during the reaction, incomplete combustion occurs to produce carbon monoxide while heat is also released, and the maximum temperature of the oxidation zone may reach 1200 ℃.
The lower part of the oxidation zone is a reduction zone, oxygen does not exist in the reduction zone, carbon dioxide generated in the oxidation reaction is subjected to reduction reaction with carbon and water vapor to generate carbon monoxide (CO) and hydrogen (H)2). Since the reduction reaction is endothermic, the temperature in the reduction zone is correspondingly reduced to about 600-800 ℃. Main production of reduction zoneThe substances are carbon monoxide (CO) and carbon dioxide (CO)2) And hydrogen (H)2). Gasification is virtually always combined with a dry cracking process of the fuel. In actual operation, the four regions have no definite boundaries, and are interpenetrating and interlaced. Therefore, at the outlet of the gasification furnace, the components of the produced gas are mainly carbon monoxide (CO) and carbon dioxide (CO)2) Hydrogen (H)2) Methane (CH)4) Tar and small amounts of other hydrocarbons, as well as steam and small amounts of ash.
The reaction in the reduction zone is mainly as follows:
C+H2O–CO+H2
CO+H2O–CO2+H2
C+CO2–2CO
C+2H2–CH4
CO2+H2–2CO+H2O
and the lower part of the final reduction area is a cooling area, the space occupation ratio of the cooling area is approximately the same as that of the feeding area, and residual slag in the cooling area can be discharged by a discharging mechanism. Meanwhile, in order to supplement the water vapor, the water vapor is injected into the bottom part at the same time, so that the conversion rate is improved.
The inside in order to insulate against heat of present reactor, all be equipped with the fire prevention brick structure, because of the inside temperature of reaction zone can reach 1200 ℃, if direct transfer heat, can lead to jar body material to produce irreversible change because of the temperature is higher to influence the structural strength of whole jar body. Therefore, the heat is effectively isolated by arranging the fireproof brick wall structure.
The existing fireproof brick is only directly attached to the inside of the tank body, namely a disposable structure is fixed, but now in practical use, the pressure of a reaction zone is about 2.7-8.5MPa, and the operating temperature can be suddenly increased to 1700 ℃. Under high temperature and high pressure, the refractory material in the combustion chamber can generate a corrosion phenomenon, and the refractory brick is continuously thinned by the scouring of heated gas and molten slag. The thinned part is generally concentrated on the upper part of the highest temperature layer of the reaction zone, in some cases, the firebrick can fall off due to the defect of bricking, the surface temperature of the wall of the gasifier tank rises when the incandescent gas invades the outside through a brick joint, the structural strength is reduced, and the deformation is generated due to stress, so that the possibility is high.
Therefore, the tank body needs to be checked in real time, and if the tank body falls off or becomes thin, the tank body needs to be maintained in time, so that major production safety accidents are avoided. And the utility model discloses a modularization mounting structure optimizes to the fire prevention module with single fire prevention brick, fixes through frame construction to improve the installation, dismantle and change efficiency.
Furthermore, the fireproof module comprises a fixed frame fixed on the inner wall of the tank body and a fireproof brick clamped on the fixed frame;
the fixed frame comprises two fixed strips which are parallel to the axis of the tank body, at least two groups of clamping grooves are formed in the inner sides of the fixed strips, and clamps matched and clamped with the clamping grooves are arranged on the refractory bricks.
Furthermore, the firebrick is arc-shaped brick body structure, and its outer protruding one side is equipped with the boss, the checkpost is inserted and is established around the boss.
Furthermore, the checkpost is forked tail strip structure, and it inserts one section tip of resistant firebrick is equipped with the expansion end, resistant firebrick realizes fixing with its expansion end parcel.
The firebrick is an integrated structure formed by sintering refractory materials and is used as a main fireproof material. The fixing strip is fixed on the inner wall of the tank body and used for fixing refractory bricks, a special clamping groove is formed in the fixing strip, and a clamp matched with the clamping groove is arranged on the refractory bricks and is of a cuboid-like structure.
The clip is a separate component, one end of the clip is inserted into the refractory brick and is fixedly connected with the refractory brick, and once the refractory brick is crushed, the clip can be directly taken down for recycling. That is to say, if need change some resistant firebricks, can directly break up the resistant firebrick that corresponds the position, then take off the checkpost to correspond new resistant firebrick and put into, pour into inorganic high temperature glue into around it again and seal, thereby accomplish the change work.
Through the arrangement of the fixing strip structure, a certain space can be reserved between the fireproof module and the inner wall of the tank body, after actual detection, the temperature in the space is 150-.
It is worth explaining that the firebrick is an arc-shaped block structure, four sides about from top to bottom, and during the installation, the terminal surface of two piece adjacent firebricks from top to bottom bonds through inorganic high temperature glue, and control two and have certain clearance between the firebrick that belongs to a ring fireproof wall, because of the firebrick is the arc structure during the installation, then and the outer lane diameter is greater than the inner circle diameter, outside promotion was installed from inside during the installation, so reserve certain clearance, avoid causing the installation and block. And a high-viscosity inorganic high-temperature adhesive is coated between the gaps for sealing. The inorganic high-temperature adhesive is a material special for bonding refractory materials and can keep a stable state at the working temperature of 0-2000 ℃.
Furthermore, when the refractory brick is installed on the fixed frame, a high-temperature adhesive is arranged between the clamp and the clamping groove.
Furthermore, glue overflow grooves are formed in the upper end face and the lower end face of each refractory brick during installation of the refractory bricks, the end faces of the glue overflow grooves in the two adjacent refractory bricks are attached to each other, the glue overflow grooves in the two sides are aligned to form a complete tubular structure, and the tubular structure is filled with a high-temperature adhesive.
Furthermore, glue injection openings communicated with the glue overflow grooves on the corresponding side are respectively arranged on the two sides of the glue overflow grooves close to the two sides on the inner concave surface of the refractory brick.
Because two adjacent resistant firebricks from top to bottom can be terminal surface laminating about the installation, the injecting glue is difficult when the installation, then is provided with excessive gluey groove structure to be equipped with the injecting glue mouth rather than the intercommunication at the surface, so that when installing and sealing up after the position, inject into inorganic high temperature through the high pressure and glue and seal, then improve the installation effectiveness, improve simultaneously sealed effect, compare in current from last to the mode of building a wall down, through the utility model discloses a mode can improve installation and dismantlement efficiency is built to the modularization.
Furthermore, the middle part of the outer convex surface of the refractory brick is inwards sunken to form a sink groove structure, a high-temperature sensor for detecting the internal temperature of the refractory brick is inserted into the sink groove structure, and the high-temperature sensor is connected with external monitoring equipment.
Furthermore, the high-temperature sensor is fixed outside the tank body, and a section of the detection head of the high-temperature sensor penetrates through the tank body and is inserted into the corresponding refractory brick; an annular cover used for shielding is arranged outside the tank body aiming at all the high-temperature sensors on the single-layer fireproof ring.
Because the position that local resistant firebrick drops is random, the event needs to carry out temperature monitoring to every fire prevention module to the resistant firebrick structure change in the strict control ware inside prevents because of the gas leakage that the abrupt change leads to, thereby causes great potential safety hazard. The high temperature sensor is an S-shaped thermocouple with the detection range of 0-1800 ℃, and the detection point of the S-shaped thermocouple is inserted into the refractory brick.
When the outer side of the refractory brick falls off and the thickness is reduced to be less than 40% of the original thickness, the whole block easily falls off, so that the insertion depth of the detection end part of the S-shaped thermocouple is about 20-40%. The detection temperature is in the range of 400-800 ℃ at ordinary times, and the alarm is given out once the temperature exceeds 850 ℃ for more than 20min, or the alarm is directly given out when the temperature exceeds 950 ℃ within 20min after the temperature is recorded to exceed 850 ℃ for the first time. The monitoring system can warn in various ways, including but not limited to sound and light, and if the manager is not nearby and no person is on duty, the monitoring system can be set to send remote information to the terminal equipment for warning.
Furthermore, the fireproof rings at the top and the bottom of the fireproof brick wall are connected with fireproof rings for arc transition, and each fireproof ring comprises a plurality of flow guide blocks connected with the end face of one side of the fireproof brick wall provided with the glue overflow groove.
The utility model has the advantages that:
the utility model discloses a set up the fixed strip structure, can remain certain space between fire prevention module and the internal wall of jar, through actual detection, in the position on the highest temperature layer of reaction zone, the temperature in this space is 150 supple with food 200 ℃ under the state of not ventilating, and during the in-service use, set up the hole of two sets of cyclic annular arrangements on the jar body, wherein a set of setting on jar body upper portion and with annular firebrick wall headspace intercommunication, and another group set up in jar body lower part and with annular firebrick wall bottom space intercommunication, higher because of inside temperature this moment, and outside temperature is lower, then air convection phenomenon appears to form the wind channel and reach the cooling effect.
Drawings
FIG. 1 is a front view of the overall structure of the present application;
FIG. 2 is an isometric view of the overall structure of the present application;
FIG. 3 is an isometric view of the present application in an oblique orientation, from a bottom-up perspective;
FIG. 4 is an exploded isometric view of a portion of the overall structure of the subject application, wherein a single-wall firebrick wall is disassembled for better viewing of its structure and arrangement;
FIG. 5 is a schematic view of the partially exploded assembly of the tilted integral structure of the present application, according to the same principle as FIG. 4;
FIG. 6 is an isometric view of the assembly of the monolithic refractory brick and the fixed frame of the present application, taken from a rear perspective;
FIG. 7 is an isometric view of the assembly of the monolithic refractory brick and the fixed frame of the present application, taken from the front view;
FIG. 8 is a schematic view of the present application showing the disassembled structure of the refractory bricks and the fixed frame, wherein the view from the back is taken mainly;
FIG. 9 is a schematic view b of the present application in a disassembled configuration, with a bottom view taken primarily;
FIG. 10 is a schematic view of the assembly of the refractory brick, the fixed frame and the deflector block at the bottom of the refractory brick of the present application, mainly from a back view;
FIG. 11 is a schematic view of the assembly of the refractory brick, the fixed frame and the deflector block at the bottom of the refractory brick of the present application, mainly from a side view;
FIG. 12 is a front view of the present application without the power mechanism;
FIG. 13 is a cross-sectional view taken along section line A of FIG. 12 of the present application;
FIG. 14 is a cross-sectional view taken along section line B of FIG. 12 of the present application;
FIG. 15 is a cross-sectional view taken along section line C of FIG. 12 of the present application;
fig. 16 is an isometric view of the auger of the present application;
fig. 17 is a side view of the auger of the present application;
fig. 18 is a schematic structural view of the present invention in which the auger is disposed obliquely.
Icon: 1-tank body, 2-feed inlet, 3-speed reducer, 4-base, 5-support leg, 6-annular cover, 7-spiral distributor, 71-spiral body, 72-concave-convex belt, 73-rotating shaft, 74-guide plate, 75-fixing seat, 8-fireproof brick wall, 81-fireproof module, 811-fireproof brick, 812-fixing frame, 813-glue overflow groove, 814-positioning plate, 815-glue injection opening, 816-clamp, 817-clamping groove, 9-grate, 10-pressure roller, 11-high temperature sensor, 12-flow guide block and 121-hollow groove.
Detailed Description
The present invention will be further explained with reference to the drawings and the embodiments.
In order to make the objects, technical solutions and advantages of the embodiments of the present application clearer, the technical solutions in the embodiments of the present application will be clearly and completely described below with reference to the drawings in the embodiments of the present application, and it is obvious that the described embodiments are some embodiments of the present application, but not all embodiments. The components of the embodiments of the present application, generally described and illustrated in the figures herein, can be arranged and designed in a wide variety of different configurations.
Thus, the following detailed description of the embodiments of the present application, presented in the accompanying drawings, is not intended to limit the scope of the claimed application, but is merely representative of selected embodiments of the application. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present application.
It should be noted that: like reference numbers and letters refer to like items in the following figures, and thus, once an item is defined in one figure, it need not be further defined and explained in subsequent figures.
In the description of the present application, it should be noted that if the terms "center", "upper", "lower", "left", "right", "vertical", "horizontal", "inner", "outer", etc. are used for indicating the orientation or positional relationship based on the orientation or positional relationship shown in the drawings or the orientation or positional relationship which is usually placed when the product of the application is used, the description is only for convenience and simplicity, and the indication or suggestion that the referred device or element must have a specific orientation, be constructed in a specific orientation and be operated, and thus, should not be construed as limiting the present application. Furthermore, the appearances of the terms "first," "second," and the like in the description herein are only used for distinguishing between similar elements and are not intended to be construed as indicating or implying relative importance.
Furthermore, the terms "horizontal", "vertical" and the like when used in the description of the present application do not require that the components be absolutely horizontal or overhanging, but may be slightly inclined. For example, "horizontal" merely means that the direction is more horizontal than "vertical" and does not mean that the structure must be perfectly horizontal, but may be slightly inclined.
In the description of the present application, it should also be noted that, unless otherwise explicitly stated or limited, the terms "disposed," "mounted," "connected," and "connected" should be interpreted broadly, e.g., as being fixedly connected, detachably connected, or integrally connected; can be mechanically or electrically connected; they may be connected directly or indirectly through intervening media, or they may be interconnected between two elements. The specific meaning of the above terms in the present application can be understood in a specific case by those of ordinary skill in the art.
Example 1:
firstly, the embodiment is a reactor structure in a dry distillation gasification process of organic garbage, and the dry distillation gasification process refers to a process of screening, crushing and drying the organic garbage, then quantitatively feeding the organic garbage into a reaction tower, and reacting at a certain temperature to generate water gas. The reaction tower is generally of a vertical structure and comprises a plurality of layers from top to bottom, and the reaction tower is divided into areas according to internal temperature. The material enters the tank 1 from the top and then reacts differently with temperature changes.
The upper part is a dry layer, the temperature of which is at 100-300 ℃, the temperature of the layer is increased in a gradient way, and the temperature is higher when the layer is closer to the lower part. This layer generally dries the crushed waste that has just entered the tank 1 and is large in space, occupying 110-20% of the total tank volume. But will generally be provided with means for pressing the material downwards in the feed, thereby providing a continuous pushing force downwards. The garbage entering the drying area is firstly contacted with the pyrolyzed fuel gas in the upper area and dehydrated within 2-4 hours, the exhaust port is communicated with the inside of the tank body 1 in the area, and the fuel gas mixed steam is exhausted from the exhaust port.
The lower part of the drying layer is a dry distillation layer, namely a cracking layer, the temperature of the drying layer is 300-600 ℃, the garbage dried by the upper layer gradually falls into the cracking layer, and is heated at the same time, so that a pyrolysis reaction is carried out, most of volatile components in the garbage are separated from solids, and when the temperature is close to the edge of 600 ℃, only ash residues are basically left in the garbage. In the dry distillation layer, a plurality of organic wastes generate alkanes, carbon monoxide, tar and water vapor, and meanwhile, some sulfur-containing and chlorine-containing substances generate a small amount of hydrogen chloride and hydrogen sulfide gas, and the hydrogen chloride and the hydrogen sulfide gas are discharged along with the water vapor and are treated by a subsequent desulfurization tower. The lower part of the dry distillation layer is an oxidation layer, the temperature of the oxidation layer is about 600-1200 ℃, and most of heat is released by violent reaction of residual ash and air. However, because the amount of oxygen supplied is controlled so that the amount of oxygen is insufficient for complete reaction during the reaction, incomplete combustion occurs to produce carbon monoxide while heat is also released, and the maximum temperature of the oxidation zone may reach 1200 ℃.
In the oxidationThe lower part of the zone is a reduction zone in which no oxygen exists, and carbon dioxide generated in the oxidation reaction is subjected to reduction reaction with carbon and water vapor to generate carbon monoxide (CO) and hydrogen (H)2). Since the reduction reaction is endothermic, the temperature in the reduction zone is correspondingly reduced to about 600-800 ℃. The main products of the reduction zone are carbon monoxide (CO) and carbon dioxide (CO)2) And hydrogen (H)2). Gasification is virtually always combined with a dry cracking process of the fuel. In actual operation, the four regions have no definite boundaries, and are interpenetrating and interlaced. Therefore, at the outlet of the gasification furnace, the components of the produced gas are mainly carbon monoxide (CO) and carbon dioxide (CO)2) Hydrogen (H)2) Methane (CH)4) Tar and small amounts of other hydrocarbons, as well as steam and small amounts of ash. And the lower part of the final reduction area is a cooling area, the space occupation ratio of the cooling area is approximately the same as that of the feeding area, and residual slag in the cooling area can be discharged by a discharging mechanism. Meanwhile, in order to supplement the water vapor, the water vapor is injected into the bottom part at the same time, so that the conversion rate is improved.
The embodiment is specifically a modularized fire-resistant garbage gasification treatment device, and the organic garbage after being screened is gasified by a dry distillation gasification process to obtain water gas, as shown in fig. 1-3, the modularized fire-resistant garbage gasification treatment device comprises a vertical tank body 1, wherein a feed inlet 2 communicated with the inside of the tank body 1 is arranged on the side wall of the tank body 1 close to the top; the bottom of the tank body 1 is provided with a plurality of support legs 5 for fixing the whole tank body 1.
The tank body 1 is internally provided with a feeding area, a reaction area and a cooling discharging area from top to bottom, and the bottom of the tank body 1 is provided with a grate 9 for discharging.
As shown in FIGS. 4 and 5, it can be seen that the fireproof brick wall 8 is arranged on the inner wall of the reaction zone of the tank body 1, the fireproof brick wall 8 comprises a plurality of vertical annular fireproof walls which are arranged at equal intervals, each annular fireproof wall comprises a plurality of fireproof modules 81 which are positioned on the same plane and are arranged at the same central angle of the axis of the tank body 1, and all the fireproof modules 81 are detachably connected with the inner wall of the tank body 1. The inside in order to insulate against heat of present reactor, all be equipped with the fire prevention brick structure, because of the inside temperature of reaction zone can reach 1200 ℃, if direct transfer heat, can lead to jar body 1 material to produce irreversible change because of the temperature is higher to influence the structural strength of whole jar body 1. Therefore, the heat is effectively isolated by arranging the fireproof brick wall 8 structure. The existing fireproof brick is only directly attached to the inside of the tank body 1, namely a disposable structure is fixed, but now in practical use, the pressure of a reaction zone is about 2.7-8.5MPa, and the operating temperature can be suddenly increased to 1700 ℃.
Under high temperature and high pressure, the refractory material in the combustion chamber is eroded, and the refractory brick 811 becomes thinner continuously by the erosion of the heated gas and the molten slag. The thinned part is generally concentrated on the upper part of the highest temperature layer of the reaction zone, in some cases, the firebrick 811 can fall off due to the defect of bricking, the surface temperature of the wall of the gasifier tank 1 is increased when the incandescent gas invades the outside through the brickwork joint, the structural strength is reduced, and the deformation is generated due to stress. Therefore, the tank body 1 needs to be checked in real time, and if the tank body is found to fall off or become thin, the tank body 1 needs to be maintained in time, so that major production safety accidents are avoided. And this embodiment adopts modularization mounting structure, optimizes single fire prevention brick for fire prevention module 81, fixes through frame construction to improve installation, dismantlement and change efficiency.
As shown in fig. 6 to 11, the fire prevention module 81 includes a firebrick 811 and a fixing frame 812 provided on the inner wall of the vessel 1 for fixing the firebrick 811; the fixing frame 812 comprises at least two fixing strips which are identical and parallel to the axis of the tank body 1 in the length direction, at least two groups of clamping grooves 817 are correspondingly arranged on the adjacent fixing strips, one side of the refractory brick 811 is provided with a clamp 816 matched and clamped with the clamping grooves 817, and the refractory brick 811 is fixed by inserting the clamp 816 with the surface coated with inorganic high-temperature glue into the corresponding clamping groove 817; the fixing frame 812 is fixed on the inner wall of the tank 1 by arranging a positioning plate 814.
The firebrick 811 has an integral structure formed by sintering a refractory material, and is a main fireproof material. The fixing strip is fixed on the inner wall of the tank body 1 and used for fixing a refractory brick 811, a special clamping groove 817 is arranged on the fixing strip, a clamp 816 matched with the clamping groove 817 is arranged on the refractory brick 811, and the refractory brick 811 is of a cuboid-like structure.
The clip 816 is a separate member, and one end thereof is inserted into the firebrick 811 and is fixedly connected to the firebrick 811, but the clip 816 can be directly removed and recycled after the firebrick 811 is crushed. That is, if a part of the firebricks 811 needs to be replaced, the firebricks 811 at the corresponding position can be directly broken, then the clips 816 are taken down, new firebricks 811 are correspondingly placed, and inorganic high temperature glue is injected around the clips for sealing, so that the maintenance is completed. Through the arrangement of the fixing strip structure, a certain space can be reserved between the fireproof module 81 and the inner wall of the tank body 1, after actual detection, the temperature in the space is 150-.
When the refractory brick 811 is installed, the middle part of one side close to the tank body 1 is inwards sunken to form a sinking groove structure, a high-temperature sensor 11 inserted into the refractory brick 811 is arranged in the sinking groove structure, and when the outer surface of the refractory brick 811 drops and becomes thin, the temperature of a detection point of the high-temperature sensor 11 rises and data is sent to a monitoring system to give an alarm. Since the positions where the local firebricks 811 fall off are random, temperature monitoring needs to be performed on each fireproof module 81, so that the firebricks 811 inside the controller are strictly controlled to change in structure, and air leakage caused by sudden changes is prevented, thereby causing serious potential safety hazards. The high temperature sensor 11 is an S-type thermocouple with a detection range of 0-1800 deg.C, and its detection point is inserted into the firebrick 811. When the outer side of the firebrick 811 is dropped, the entire firebrick is likely to drop when the thickness is reduced to 40% or less of the original thickness,
therefore, the insertion depth of the detection end part of the S-shaped thermocouple is about 20-40%. The detection temperature is in the range of 400-800 ℃ at ordinary times, and the alarm is given once the temperature exceeds 850 ℃ for 20min, or the alarm is directly given when the temperature exceeds 950 ℃ within 20min after the temperature exceeds 850 ℃ for the first time. The monitoring system can warn in various ways, including but not limited to sound and light, and if the manager is not nearby and no person is on duty, the monitoring system can be set to send remote information to the terminal equipment for warning.
Because terminal surface laminating about two adjacent resistant firebricks 811 can be when the installation, the injecting glue is difficult when the installation, then be provided with excessive gluey groove 813 structure, and be equipped with the injecting glue mouth 815 rather than the intercommunication at the surface, so that when installing and sealing up after the position, inject into inorganic high temperature through the high pressure and glue and seal, then improve the installation effectiveness, improve simultaneously sealed effect, compare in current from last to the mode of building a wall down, can improve installation and dismantlement efficiency through the modularization mode of building up of this embodiment.
As shown in fig. 10, fire-proof rings at the top and bottom of the fire-proof brick wall 8 are connected with fire-proof rings for arc transition, and the fire-proof rings comprise a plurality of flow guide blocks 12 connected with the end surface of one side of the fire-proof brick 811 provided with the glue overflow groove 813. And a hollow groove 121 for reducing the mass is arranged in the flow guide block 12.
The middle part of the outer convex surface of the refractory brick 811 is inwards sunken to form a sinking groove structure, a high-temperature sensor 11 for detecting the internal temperature of the refractory brick 811 is inserted in the sinking groove structure, and the high-temperature sensor 11 is connected with external monitoring equipment. The high-temperature sensor 11 is fixed outside the tank body 1, and a detection head section of the high-temperature sensor 11 penetrates through the tank body 1 and is inserted into the corresponding refractory brick 811; an annular shield 6 for shielding is arranged outside the tank 1 for all the high-temperature sensors 11 on the single-layer fireproof ring.
Example 2:
the modularized fire-resistant garbage gasification treatment device of the embodiment, as shown in fig. 1-5 and 12-18, gasifies screened organic garbage through a dry distillation gasification process to obtain water gas, and comprises a vertical tank body 1, wherein a feed inlet 2 communicated with the interior of the tank body 1 is arranged on the side wall of the tank body 1 close to the top; the top of the tank body 1 is provided with a spiral distributing device 7, the top of the tank body 1 is provided with a power mechanism in transmission connection with the spiral distributing device 7, and the spiral distributing device 7 is driven by the power mechanism to quantitatively press the crushed organic garbage entering from the feeding hole 2 into a reaction area in the tank body 1 for reaction.
The feeding area, the reaction area and the cooling discharging area are sequentially arranged in the tank body 1 from top to bottom, the spiral distributor 7 is arranged in the feeding area, the bottom of the spiral distributor is in contact with the top surface of the reaction area, and materials which just enter the reaction area are compacted through a pressure roller 10 arranged on the spiral distributor 7. The spiral distributing device 7 comprises a spiral main body in transmission connection with a power mechanism and a spiral disc arranged on the curved surface of the spiral main body, and the section of the spiral disc is always parallel to the normal vector of the curved surface of the spiral main body at the point; the nip roll 10 is arranged at the bottom of the spiral disk, and the axis of the nip roll 10 is vertical to the axis of the spiral main body.
The ear seat is connected for dismantling with fixing base 75, fixes spacingly through bolt or draw-in groove 817, can set up a plurality of fixed positions simultaneously to the high position of nip roll 10 is adjusted through the fixed position of adjusting the ear seat. The bottom end of the spiral disk is connected with a guide plate 74 for guiding the material to fall out of the spiral distributor 7, and the fixed seat 75 is arranged on the bottom surface of the spiral disk and close to the guide plate 74. The spiral surface of the spiral distributor 7 facing the top of the tank body 1 is provided with a plurality of concave-convex belts spirally extending along the spiral surface.
In order to reduce the contact area between the surface of the whole spiral distributing device 7 and the garbage and reduce the adhesive force of the garbage, a plurality of concave-convex belt structures are arranged, the concave-convex belts are also in a spiral shape and extend around the spiral main body of the spiral distributing device 7, so that the concave-convex structures are formed on the surface of the spiral disc.
The present invention is not limited to the above-mentioned alternative embodiments, and various other products can be obtained by anyone under the teaching of the present invention. The above detailed description should not be taken as limiting the scope of the invention, which is defined in the following claims, and which can be used to interpret the claims.
Claims (10)
1. Modularization fire-resistant rubbish gasification treatment device for carry out gasification treatment with the organic rubbish after the screening and obtain water gas, its characterized in that: the fire-proof brick tank comprises a tank body (1) and an annular fire-proof brick wall (8) arranged in the tank body (1), wherein the top of the tank body (1) is provided with a feed inlet (2), and the bottom of the tank body is provided with a grate (9) for discharging and feeding air;
divide into feeding district, reaction zone and cooling discharge area from last to down in proper order in jar body (1), fire prevention brick wall (8) set up in the reaction zone, fire prevention brick wall (8) are in including the multilayer is coaxial and laminating the fire prevention ring of jar body (1) inner wall, fire prevention ring includes a plurality of fire prevention modules (81) that set up along the central angle such as jar body (1) axis, fire prevention module (81) can be dismantled with jar body (1) and be connected.
2. The modular refractory refuse gasification treatment installation according to claim 1, wherein: the fireproof module (81) comprises a fixed frame (812) fixed on the inner wall of the tank body (1) and a fireproof brick (811) clamped on the fixed frame (812);
the fixed frame (812) includes two all with jar body (1) axis parallel's fixed strip, the fixed strip inboard is equipped with at least two sets of draw-in grooves (817), be equipped with on resistant firebrick (811) with checkpost (816) of draw-in groove (817) cooperation joint.
3. The modular refractory refuse gasification treatment installation according to claim 2, wherein: the firebrick (811) is an arc-shaped brick body structure, a boss is arranged on one convex side of the firebrick, and the clips (816) are inserted around the boss.
4. The modular refractory refuse gasification treatment installation according to claim 3, wherein: the clip (816) is of a dovetail strip structure, an expansion end is arranged at one end part of the inserted refractory brick (811), and the expansion end is wrapped by the refractory brick (811) to realize fixation.
5. The modular refractory refuse gasification treatment installation according to claim 3, wherein: when the refractory brick (811) is installed on the fixed frame (812), a high-temperature adhesive is arranged between the clamp (816) and the clamping groove (817).
6. The modular refractory refuse gasification treatment installation according to claim 3, wherein: glue overflow grooves (813) are formed in the upper end face and the lower end face of each firebrick (811) when the firebricks (811) are installed, the end faces of the glue overflow grooves (813) in the two adjacent firebricks (811) are attached to each other, the glue overflow grooves (813) in the two sides are aligned to form a complete tubular structure, and high-temperature adhesive is filled in the tubular structure.
7. The modular refractory refuse gasification treatment installation according to claim 6, wherein: glue injection openings (815) communicated with the glue overflow grooves (813) on the corresponding side are respectively arranged on two sides of the glue overflow grooves (813) close to the two sides on the inner concave surface of the refractory brick (811).
8. The modular refractory refuse gasification treatment installation according to claim 3, wherein: the middle of the outer convex surface of the refractory brick (811) is inwards recessed to form a sinking groove structure, a high-temperature sensor (11) used for detecting the internal temperature of the refractory brick (811) is inserted into the sinking groove structure, and the high-temperature sensor (11) is connected with external monitoring equipment.
9. The modular refractory refuse gasification treatment installation according to claim 8, wherein: the high-temperature sensor (11) is fixed outside the tank body (1), and a detection head section of the high-temperature sensor (11) penetrates through the tank body (1) and is inserted into the corresponding refractory brick (811); an annular cover (6) used for shielding is arranged outside the tank body (1) aiming at all the high-temperature sensors (11) on the single-layer fireproof ring.
10. The modular refractory refuse gasification treatment installation according to claim 8, wherein: the fireproof ring at the top and the bottom of the fireproof brick wall (8) is connected with a fireproof ring for arc transition, and the fireproof ring comprises a plurality of flow guide blocks (12) which are connected with the end surface of one side of a fireproof brick (811) provided with an overflow glue groove (813).
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201921193725.1U CN210176799U (en) | 2019-07-26 | 2019-07-26 | Modularized fire-resistant garbage gasification treatment device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201921193725.1U CN210176799U (en) | 2019-07-26 | 2019-07-26 | Modularized fire-resistant garbage gasification treatment device |
Publications (1)
Publication Number | Publication Date |
---|---|
CN210176799U true CN210176799U (en) | 2020-03-24 |
Family
ID=69841683
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201921193725.1U Active CN210176799U (en) | 2019-07-26 | 2019-07-26 | Modularized fire-resistant garbage gasification treatment device |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN210176799U (en) |
-
2019
- 2019-07-26 CN CN201921193725.1U patent/CN210176799U/en active Active
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP6130837B2 (en) | Efficient and clean combustion method and apparatus for polymer materials | |
CN109780548B (en) | Pyrolysis gasifier | |
CN102329652A (en) | Downdraft plasma garbage gasification reaction chamber and gasification process | |
CN107477585A (en) | A kind of solid waste incinerator for thermal decomposition | |
CN105202545A (en) | Garbage pyrolysis gasification incineration treatment device | |
CN105062566B (en) | A kind of plasma gasification reactor for domestic waste | |
CN107676789A (en) | A kind of refuse pyrolysis method and device | |
ES2388959A1 (en) | Method and device for the thermolysis of waste polymers | |
CN102358851A (en) | Horizontal plasma garbage gasification reaction chamber and gasification technology thereof | |
CN110387249B (en) | Spiral feeding garbage gasification reaction system | |
CN102504881A (en) | Novel garbage carbonization-gasification furnace for garbage disposal | |
CN210176799U (en) | Modularized fire-resistant garbage gasification treatment device | |
JP6642924B2 (en) | Hydrogen station system | |
CN104976621A (en) | Household garbage pyrolysis gasifier | |
CN109340802B (en) | Cyclone separator | |
CN216303716U (en) | Device for resource, coal-saving and disposal of solid waste by utilizing dry distillation and gasification in cooperation with cement kiln | |
CN102925239A (en) | Refuse derived fuel production system | |
CN202829986U (en) | System for manufacturing refuse derived fuel | |
CN105602630A (en) | Technology for catalysis and quality improvement by using waste gasified gases | |
CN101845327A (en) | Waste gasification purification reacting furnace | |
CN214108261U (en) | Low-temperature anaerobic cracking treatment device for household garbage | |
CN109355068B (en) | Pyrolysis furnace | |
CN210345487U (en) | Smokeless incineration device | |
WO2013140418A1 (en) | Multi-condition thermochemical gas reactor | |
CN209508147U (en) | The pyrolysis plant of solid waste containing organic matter |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
GR01 | Patent grant | ||
GR01 | Patent grant |