WO2021221163A1 - Biomass gasification device - Google Patents
Biomass gasification device Download PDFInfo
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- WO2021221163A1 WO2021221163A1 PCT/JP2021/017234 JP2021017234W WO2021221163A1 WO 2021221163 A1 WO2021221163 A1 WO 2021221163A1 JP 2021017234 W JP2021017234 W JP 2021017234W WO 2021221163 A1 WO2021221163 A1 WO 2021221163A1
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- heat
- pyrolyzer
- opening
- valve
- biomass
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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
- C10J3/06—Continuous processes
- C10J3/12—Continuous processes using solid heat-carriers
Definitions
- the present invention relates to a biomass gasifier having a preheater, a pyrolyzer and a pyrolyzed gas reformer.
- sewage sludge having an ash content of 20% by weight is dried and then pyrolyzed in an air-blown fluidized layer pyrolysis furnace at 500 to 800 ° C. to pyrolyze the pyrolysis gas.
- a method of generating turbine power by burning with air at a high temperature of 1000 to 1,250 ° C and generating steam with the heat Japanese Patent Laid-Open No. 2002-322902
- high ash biomass as a raw material is circulated by air blowing.
- Pyrolysis is carried out in a flow heating furnace at a temperature of 450 to 850 ° C., and char, which is a thermal decomposition residue, is recovered by a cyclone, while pyrolysis gas containing tar is reformed at 1000 to 1200 ° C. in the presence of oxygen.
- Method Japanese Unexamined Patent Publication No. 2004-517405
- the char is pyrolyzed by the same method to separate the char, and then the char is granulated and supplied into the circulating flow reforming furnace.
- a method of producing a granulated sintered body by sintering at a temperature of 900 to 1000 ° C. (Japanese Patent No. 4155507) or the like is disclosed.
- a heat-carrying medium for carrying heat a preheater for heating the heat-carrying medium, a reformer for steam reforming of the heat-decomposed gas, and a heat-decomposing wood biomass raw material.
- the preheater, the reformer, and the heat decomposer 20 are provided with a heat decomposer, a separator for separating the heat-bearing medium and the char, and a hot air furnace that burns the char to generate hot air.
- Devices arranged vertically in order from the top are known (Japanese Patent Laid-Open No. 2011-144329).
- the heat-decomposed coke obtained by separating the mixture consisting of the heat-decomposed coke and the heat-bearing medium is burned in a combustion device, and the heat-bearing medium is heated in the heating zone by utilizing the apparent heat generated thereby.
- An embodiment of producing a product gas having a high calorific value from an organic substance and a substance mixture Japanese Patent No. 4264525) is known.
- a pyrolysis gas introduction tube for introducing the pyrolysis gas from the pyrolysis device to the pyrolysis gas reformer is formed on the pyrolysis device side on the upper surface of the preheated heat-bearing medium layer formed in the pyrolysis device.
- a gasification method Japanese Patent Laid-Open No. 2019-65160 installed on the side surface of a lower pyrolyzer is known.
- the heat-supporting heat is carried by hot air in the preheater.
- the medium is dropped into a pyrolyzer and mixed with biomass such as wood chips to generate biogas.
- Japanese Patent Application Laid-Open No. 2019-65160 uses a so-called two-stage valve system in which a total of two valves are provided, one on the top and one on the bottom of the pipe.
- composition and flow rate of the gas are not stable when gasification progresses and when it does not progress, and gas of constant quality is not generated, which hinders the separation performance of the device that separates the components in the gas installed in the subsequent stage. There can also be a problem of becoming a factor.
- the biomass gasifier according to the present invention A preheater that preheats the heat-supporting medium and A thermal decomposer that receives a supply of a heat-bearing medium preheated by the preheater and executes thermal decomposition of biomass by the heat of the heat-bearing medium.
- a pyrolysis gas reformer that at least partially burns the pyrolysis gas generated by pyrolysis with air or oxygen.
- a supply mechanism provided between the preheater and the pyrolyzer for supplying the heat-carrying medium from the preheater to the pyrolyzer, and With The supply mechanism An opening / closing part for temporarily storing the heat-carrying medium and An adjusting unit provided below the opening / closing unit and supplying the heat-carrying medium supplied from the opening / closing unit to the pyrolyzer by swinging or rotating. May have.
- the opening / closing portion has a first opening / closing portion and a second opening / closing portion provided below the first opening / closing portion.
- a control device may be provided which opens the first opening / closing portion while the second opening / closing portion is closed and opens the second opening / closing portion while the first opening / closing portion is closed.
- Each of the first opening / closing part and the second opening / closing part may be a damper valve.
- the biomass gasifier according to the present invention A hopper provided between the preheater and the pyrolyzer, A control device that controls the supply of the heat-supporting medium from the preheater to the pyrolyzer based on the weight or top surface position of the heat-supporting medium in the hopper. May be provided.
- the adjusting portion may be a swing valve or a rotary valve.
- a steam atomizer that sprays steam between the preheater and the pyrolyzer when the opening / closing portion is in the open state may be provided.
- the adjusting part is composed of a swinging part.
- a control device for controlling the supply amount of the heat-carrying medium to the pyrolyzer may be provided by changing the swing cycle time or the swing distance of the swing portion.
- the adjusting part is composed of a rotating part.
- the control device may control the supply amount of the heat-carrying medium to the pyrolyzer by changing the rotation speed of the rotating portion.
- a third valve provided below the pyrolyzer and A steam atomizer that sprays steam when the third valve is in the open state may be provided.
- the supply mechanism is provided at the opening / closing part for temporarily storing the heat-carrying medium and below the opening / closing part, and the heat-carrying medium supplied from the opening / closing part is thermally decomposed by swinging or rotating.
- gasification can be performed in a stable amount.
- FIG. 1 is a schematic view showing an embodiment of a biomass gasification device.
- FIG. 2 is a diagram showing a method of supplying a heat-carrying medium from a preheater to a pyrolyzer in a biomass gasifier.
- FIG. 3A is a diagram for explaining the supply of the heat-carrying medium from the preheater through the pyrolyzer in the biomass gasifier.
- FIG. 3B is a diagram in which the state is advanced from FIG. 3A.
- FIG. 3C is a diagram in which the state is advanced from FIG. 3B.
- FIG. 3D is a diagram in which the state is advanced from FIG. 3C.
- FIG. 4 is a schematic view showing one embodiment of the supply control method in the biomass gasification device of the present embodiment.
- FIG. 4 is a schematic view showing one embodiment of the supply control method in the biomass gasification device of the present embodiment.
- FIG. 5 is a schematic view showing one embodiment of the supply control method in the biomass gasification device of the present embodiment.
- FIG. 6 is a schematic view showing one embodiment of the supply control method in the biomass gasification device of the present embodiment.
- FIG. 7 is a schematic view showing one embodiment of the supply control method in the biomass gasification device of the present embodiment.
- FIG. 8 is a schematic view showing an embodiment of a control device in the biomass gasification device of the present embodiment.
- FIG. 9 is a side view of the rotary valve used in this embodiment.
- FIG. 10 is a schematic view for explaining a control mode of the heat-carrying medium in the hopper.
- the biomass gasifier of the present embodiment receives heat from the preheater 10 that preheats the heat-bearing medium 30 and the heat-supporting medium 30 that has been preheated by the preheater 10.
- a thermal decomposition device (biomass thermal decomposition device) 20 that executes thermal decomposition of biomass by the heat of the supporting medium 30 and a thermal decomposition gas generated by the thermal decomposition are partially burned by air or oxygen to execute steam reforming. It has a thermal decomposition gas reformer 40 and a supply mechanism provided between the preheater 10 and the thermal cracker 20 for supplying the heat-bearing medium 30 from the preheater 10 to the thermal cracker. There is.
- the heat-supporting medium 30 (also referred to as "heat carrier”) is a plurality of granules and / or lumps, preferably made of one or more materials selected from the group consisting of metals and ceramics.
- the metal is preferably selected from the group consisting of iron, stainless steel, nickel alloy steel, and titanium alloy steel, and more preferably stainless steel.
- the ceramic is selected from the group consisting of alumina, silica, silicon carbide, tungsten carbide, zirconia and silicon nitride, and more preferably alumina.
- the shape of the heat-supporting medium 30 is preferably spherical (ball), but it does not necessarily have to be a true sphere, and it may be a spherical object having an elliptical or oval cross-sectional shape.
- the diameter (maximum diameter) of the spherical object is preferably 3 to 25 mm, more preferably 8 to 15 mm. Exceeding the above upper limit (25 mm) may impair the fluidity inside the pyrolyzer 20, that is, the free fall property, which causes the spherical object to stand still inside the pyrolyzer 20 and cause blockage. May become.
- the spheroids themselves may stick to the spheroids due to tar and soot and dust adhering to the spheroids in the pyrolyzer 20, which may cause blockage.
- the diameter of the spherical object is less than 3 mm, the spherical object adheres to the inner wall of the pyrolyzer 20 and grows due to the influence of tar and dust adhering to the spherical object, and in the worst case, the pyrolyzer There is a concern that 20 will be blocked.
- the spherical object to which tar is attached is extracted from the valve at the bottom of the pyrolyzer 20
- the spherical object having a thickness of less than 3 mm is light, and since the tar is attached, it does not fall naturally and sticks to the inside of the valve. May promote obstruction.
- the biomass of this embodiment means a so-called biomass resource.
- the biomass resource refers to plant-based biomass, for example, agricultural products such as thinned wood, sludge waste, pruned branches, forest land residue, unused trees, etc., which are discarded from agriculture, and vegetable residues and fruit tree residues, which are discarded from agriculture.
- plant-based biomass for example, agricultural products such as thinned wood, sludge waste, pruned branches, forest land residue, unused trees, etc., which are discarded from agriculture, and vegetable residues and fruit tree residues, which are discarded from agriculture.
- biological biomass for example, biological waste such as livestock excrement and sewage sludge
- the apparatus of this embodiment is preferably suitable for gasification of plant-based biomass and biological-based biomass.
- high ash biomass having an ash content of preferably 5.0% by mass or more, more preferably 10.0 to 30.0% by mass, and further preferably 15.0 to 20.0% by mass on a drying basis.
- high ash biomass having an ash content of preferably 5.0% by mass or more, more preferably 10.0 to 30.0% by mass, and further preferably 15.0 to 20.0% by mass on a drying basis.
- it is suitable for gasification of sewage sludge and livestock excrement.
- the heat-supporting medium 30 preheated by the preheater 10 is supplied from the preheater 10 to the pyrolyzer 20 via a valve described later by free fall.
- the heat-supporting medium 30 causes thermal decomposition of the biomass supplied into the pyrolyzer 20 by its own heat.
- the heat-supporting medium 30 in the pyrolyzer 20 is discharged from the pyrolyzer 20 by free fall via a valve, and is preferably recirculated to the preheater 10.
- a first valve 50, a hopper 60, and a second valve 70 are provided between the preheater 10 and the pyrolyzer 20 downward from the preheater 10.
- the supply mechanism is openable and closable, and has an opening / closing part for temporarily storing the heat-carrying medium and a heat-bearing medium provided below the opening / closing part, which is shaken or rotated to thermally decompose the heat-carrying medium supplied from the opening / closing part. It has a second adjusting unit that supplies the vessel. When the opening / closing portion is in the closed state, the heat-carrying medium is placed above the opening / closing portion and is temporarily stored. In the configuration shown in FIG.
- the opening / closing part is composed of the first opening / closing part and the second opening / closing part (the first damper valve 51a and the second damper valve 51b described later) of the first valve 50, and the second adjusting part is from the second valve 70. It has become.
- a control device 100 that controls the supply of the heat-carrying medium 30 may be provided.
- a control device 100 it enables stable continuous supply of the heat-bearing medium 30 in the gasification device, stabilization of the pressure fluctuation of the pyrolyzer 20, and improvement of the separation ability in gas separation. Further, it is possible to provide a gas having stable quality.
- the first valve 50 may have a first adjusting portion, a first opening / closing portion provided below the first adjusting portion, and a second opening / closing portion provided below the first opening / closing portion. .. Then, the control device 100 controls so that the first opening / closing portion is opened while the second opening / closing portion is closed and the second opening / closing portion is opened while the first opening / closing portion is closed. Therefore, it may be possible to prevent the gas on the upper side and the gas on the lower side of the first valve 50 from being mixed.
- Each of the first opening / closing part and the second opening / closing part may be a damper valve.
- the first opening / closing portion is the first damper valve 51a and the second opening / closing portion is the second damper valve 51b will be described. Further, the embodiment in which the first adjusting portion of the first valve 50 is the swing valve 52 will be described. Further, a mode in which the second adjusting portion of the second valve 70 is a swing valve 72 or a rotary valve 74 will be described.
- the swing valve 52 swings (see FIGS. 3A to 3D) in order to drop the heat-bearing medium 30 into the pyrolyzer 20.
- a method is adopted in which the heat-bearing medium 30 is dropped into the pyrolyzer 20 by a free drop in combination with the opening and closing of the damper valve 51.
- the upper and lower two first damper valves 51a and the second damper valve 51b are closed (FIG. 3A), the first damper valve 51a is opened, and the heat-supporting medium 30 is placed inside the pipe. It is dropped and the heat-supporting medium 30 is filled between the second damper valve 51b and the first damper valve 51a (FIG. 3B).
- the first damper valve 51a FIG. 3C
- the second damper valve 51b the heat-carrying medium 30 filled between the first damper valve 51a and the second damper valve 51b is introduced into the pyrolyzer 20. , Or discharged from the pyrolyzer 20 (Fig. 3D).
- the heat-supporting medium 30 is introduced into the pyrolyzer 20 and discharged from the pyrolyzer 20.
- the high-temperature gas for heating the heat-carrying medium 30 is mixed with the gas produced by biomass (mixed gas containing hydrogen, methane, carbon monoxide, etc.). ..
- the swing valve 52 is a valve suitable for stopping the flow by moving like a pendulum while the solid is flowing downward, but it does not have a gas sealing property. By providing such a swing valve 52, it is possible to prevent the heat-supporting medium 30 from being supplied all at once, and it is possible to prevent the heat-supporting medium 30 from being stuck in the tube 300.
- the pyrolyzer 20 located below the preheater 10 in the biomass gasifier is provided with an inlet for the heat carrier medium 30 above (upper), preferably at the top, and below (lower) the pyrolyzer 20. ), Preferably, the bottom is provided with a discharge port for the heat-bearing medium 30.
- a preheater 10 for preheating the heat-carrying medium 30 is provided above the pyrolyzer 20, and the heat-carrying medium 30 is heated to a predetermined temperature.
- the preheater 10 is preferably provided on the upper part of the pyrolyzer 20, where all the heat-bearing media 30 are heated to a predetermined temperature, and the heat-bearing medium 30 heated to the temperature is brought into the pyrolyzer. Can be supplied to 20.
- a third valve 90 may be provided between the pyrolyzer 20 and the waste treatment device 240.
- the third valve 90 may have a pair of damper valves 91a and 91b which are examples of the opening / closing part and a swing valve (third adjusting part) 92 which is an example of the adjusting part (FIG. 2). reference).
- the swing valve 92, the first damper valve 91a, and the second damper valve 91b may be arranged in order from the top.
- the waste treatment device 240 is provided with a filter F (see FIG.
- Steam may be sprayed by the steam atomizer 80 between the preheater 10 and the pyrolyzer 20 and / or between the pyrolyzer 20 and the waste treatment device 240 (see FIG. 5).
- the flow of gas can be blocked by water vapor, and it is possible to prevent the heating gas flowing through the preheater 10 and the gas from biomass from being mixed.
- only one damper valve may be used, and when the damper valve is in the open state, water vapor may be sprayed by the steam sprayer 80 to block the flow of gas.
- Such control may be performed by a command from the control device 100. Even when the steam sprayer 80 is provided, two or more damper valves may be provided.
- a detector 110 for detecting the weight or the upper surface position of the heat-carrying medium 30 in the hopper 60 and the pyrolyzer 20 may be provided (see FIG. 4). Then, the control device 100 issues a command based on the data from the detector 110 or a command based on the calculation using the data from the detector 110 to the first valve 50 and the second valve 70, and the third valve 90. The operation of the first valve 50, the second valve 70, the third valve 90, and the steam sprayer 80 can be controlled by transmitting the data to the steam sprayer 80.
- the control device 100 includes a detection unit 101 that receives information from the detector 110, a calculation unit 102 that calculates information from the detection unit 101 and transmits information as a command to the control unit 103, valves 50, 70, 90, and water vapor. It may have a control unit 103 that transmits a command to the atomizer 80 (see FIGS. 5 and 8).
- a switch such as the first switch 120 or the second switch 130 may be driven by a command from the control device 100 to drive the valves 50, 70, 90 and the steam atomizer 80.
- the second valve 70 can be composed of one or a plurality of swing valves 72 that swing continuously, but it is preferable that the second valve 70 is composed of one swing valve 72.
- the second valve 70 can be composed of one or a plurality of rotary valves 74 (see FIGS. 2 and 9), but it is preferably composed of one rotary valve 74.
- the rotary valve 74 is divided into a plurality of spaces, and when the rotary valve 74 rotates, the heat-carrying medium 30 accommodated in each space is sequentially dropped (see FIG. 9).
- the control device 100 may control the supply amount of the heat-carrying medium 30 to the pyrolyzer 20 by changing the swing cycle time and / or the swing distance of the swing valve 72. By changing the rotation speed of the rotary valve 74, the supply amount of the heat-carrying medium 30 to the pyrolyzer 20 may be controlled. By performing such control, the supply amount of the heat-supporting medium 30 can be appropriately adjusted.
- the hopper 60 absorbs the impact due to the drop of the heat-carrying medium 30 by receiving the heat-carrying medium 30 once.
- the heat-carrying medium 30 can be supplied to the pyrolyzer 20 while being adjusted by the second valve 70. Therefore, the heat-supporting medium 30 can be supplied in a more stable state.
- the first aspect of the control device 100 in the biomass gasification device of the present embodiment is that the first valve 50, the hopper 60, and the hopper 60 are located between the preheater 10 and the pyrolyzer 20 downward from the preheater 10.
- a second valve 70 is provided.
- the control device 100 monitors the supply of the heat-carrying medium 30 from the preheater 10 through the pyrolyzer 20 and controls the operations of the first valve 50 and the second valve 70 based on the monitoring result. There is.
- stable continuous supply of the heat-bearing medium 30 in the gasifier is realized, pressure fluctuation of the pyrolyzer 20 is suppressed, problems such as deterioration of separation ability in gas separation are solved, and quality is stable. Gas can be provided.
- the control device 100 monitors the weight or top position (hereinafter, also referred to as “level”) of the heat-carrying medium 30 supplied from the preheater 10 through the first valve 50 in the hopper 60. If the weight or level falls below a predetermined value, the first switch 120 is operated to open the first valve 50. On the other hand, if the weight or the upper surface position exceeds a predetermined value, the second switch 130 is operated to close the first valve 50.
- the heat-supporting medium 30 is continuously supplied to the second valve 70, and the amount of the heat-supporting medium 30 supplied from the hopper 60 to the pyrolyzer 20 is controlled by the opening degree of the second valve 70.
- the valve when the first valve 50 is opened, the valve is provided with a steam atomizer 80 that sprays a steam pulse and seals the valve with steam (see FIG. 5).
- the control device 100 can control the operation of the steam sprayer 80 to further improve the sealing property of the first valve 50 and prevent the backflow of gas.
- the third valve 90 When the third valve 90 is opened, the third valve 90 may be provided with a steam sprayer 80 that sprays a steam pulse and seals with steam.
- the control device 100 controls the steam sprayer 80 so as to spray the steam pulse on the third valve 90 when the third valve 90 is opened, and controls the discharge of the heat-bearing medium 30 from the pyrolyzer 20. Therefore, the sealing property of the third valve 90 can be further improved, and the backflow of gas can be prevented.
- the first valve 50 is preferably composed of one or more swing valves 52 at the upper part and one or more damper valves 51 at the lower part, and the steam pulse spray from the steam sprayer 80 is preferably linked to the opening of the damper valve 51.
- the third valve 90 is preferably composed of one or more swing valves 92 at the upper part and one or more damper valves 91 at the lower part, and the steam pulse spray from the steam sprayer 80 is preferably linked to the opening of the damper valve 91.
- the control device 100 supplies the heat-bearing medium 30 to the pyrolyzer 20 per unit time W kg / h in the hopper 60 as compared with a preset value W 0 kg / h.
- W kg / h the opening degree of the second valve 70 is reduced to decrease it
- W kg / h the opening degree of the second valve 70 is increased to increase it, and heat is carried to the pyrolyzer 20.
- the supply amount of the medium 30 may be controlled.
- the time t and the weight from the initial level H to the final level L may be measured (see FIG. 10).
- the cross-sectional area of the hopper 60 is S and the bulk density of the heat-supporting medium 30 is ⁇
- the calculation using the time t is calculated.
- the set value W 0 and the supply amount W may be calculated using the decrease rate (w / t), and the above control may be performed.
- the weight or the upper surface position of the heat-carrying medium 30 may be constantly monitored by the detector 110 in any one or more of the preheater 10, the hopper 60, and the pyrolyzer 20. (See FIGS. 4 and 6 to 8). Taking the heat-bearing medium 30 as an example, if the weight or the upper surface position falls below a certain value, a command to open / close the third valve 90 is transmitted to the third valve 90 at a speed faster than the normal speed X, and the weight or the upper surface position is changed.
- a command to open / close the third valve 90 at a speed slower than the normal speed X is transmitted to the third valve 90, and when the weight or the upper surface position is a certain amount, the third valve 90 is opened / closed at the normal speed. It is also possible to control the operation of the 3 valve 90 to control the opening and closing of the 3rd valve 90.
- control device 100 in the biomass gasification device of the present embodiment may be incorporated into the conventional biomass gasification device.
- the pyrolyzer 20 has a biomass supply port and a non-oxidizing gas supply port and / or a steam blow port.
- the pyrolysis gas reformer 40 has a steam inlet and a reformed gas outlet.
- a pyrolysis gas introduction pipe 200 provided between the pyrolysis device 20 and the pyrolysis gas reformer 40, which introduces the pyrolysis gas generated in the pyrolysis device 20 into the pyrolysis gas reformer 40.
- Each of the thermal decomposition device 20 and the thermal decomposition gas reformer 40 further includes an inlet and an outlet for a preheated heat-bearing medium, and the heat of the heat-bearing medium causes thermal decomposition of biomass and thermal decomposition of biomass.
- the pyrolysis device 20 and the pyrolysis gas reformer 40 are provided in parallel with respect to the flow of the heat-bearing medium, and the pyrolysis gas introduction pipe 200 is provided with the pyrolysis device 20 and the pyrolysis gas reformer.
- the pyrolysis gas introduction pipe 200 is provided and is provided substantially horizontally with respect to the direction of gravity.
- a first valve 50, a hopper 60, and a second valve 70 are provided between the preheater 10 and the pyrolyzer 20 downward from the preheater 10.
- the control device 100 monitors the weight or the position of the upper surface of the heat-bearing medium 30 in the hopper 60, controls the operations of the first valve 50 and the second valve 70 based on the monitoring result, and from the preheater 10 to the pyrolyzer. It is possible to provide a biomass gasification device incorporating a control device 100 that controls the supply of the heat carrying medium 30 through the 20.
- the pyrolyzer 20 has a biomass supply port and a non-oxidizing gas supply port and / or a steam blow port.
- the pyrolysis gas reformer 40 has a steam inlet and a reformed gas outlet.
- a pyrolysis gas introduction pipe 200 provided between the pyrolysis device 20 and the pyrolysis gas reformer 40 is provided, and the pyrolysis gas generated in the pyrolysis device 20 is transferred to the pyrolysis gas reformer 40.
- the pyrolyzer 20 further includes an inlet and an outlet for a heat-supporting medium that has been preheated, and uses the heat of the heat-supporting medium to carry out thermal decomposition of biomass.
- the pyrolysis gas reformer 40 executes steam reforming of the pyrolysis gas generated by the thermal decomposition of biomass.
- the pyrolysis gas reformer 40 further includes an air or oxygen inlet, and performs steam reforming by partially burning the pyrolysis gas generated by the thermal decomposition of biomass with the air or oxygen.
- the pyrolysis gas introduction pipe 200 is provided on the side surface of the pyrolyzer 20 below the upper surface of the heat-carrying medium layer formed in the pyrolyzer 20.
- a first valve 50, a hopper 60, and a second valve 70 are provided between the preheater 10 and the pyrolyzer 20 downward from the preheater 10, and the control device 100 is a heat-bearing medium in the hopper 60.
- the weight or top position of 30 is monitored, the operation of the first valve 50 and the second valve 70 is controlled based on the monitoring result, and the supply of the heat-bearing medium 30 from the preheater 10 through the pyrolyzer 20 is controlled. It is possible to provide a biomass gasification device incorporating the control device 100.
- the pyrolyzer 20 that heats the biomass in a non-oxidizing gas atmosphere or a mixed gas atmosphere of a non-oxidizing gas and steam, and the gas generated in the pyrolyzing device 20.
- a pyrolysis gas reformer 40 that reforms the heat in the presence of steam, and the preheated heat-supporting medium 30 is charged into the pyrolyzer 20 to bring the heat-supporting medium 30 into the pyrolyzer 20.
- Pyrolysis of the biomass is carried out by the heat possessed, and then the pyrolysis gas generated by the pyrolysis of the biomass is introduced into the pyrolysis gas reformer 40 to carry out steam reforming of the pyrolysis gas.
- a pyrolysis gas introduction tube provided on the side surface of the pyrolysis device 20 below the upper surface of the heat-supporting medium layer, in which the pyrolysis gas generated by the thermal decomposition of the biomass is formed in the pyrolysis device 20.
- the pyrolysis gas reformer 40 is introduced into the pyrolysis gas reformer 40, and then the introduced pyrolysis gas is partially introduced into the pyrolysis gas reformer 40 by air or oxygen separately introduced into the pyrolysis gas reformer 40.
- the method of gasifying biomass which is pyrolyzed and reformed by steam introduced at the same time as the above air or oxygen.
- a first valve 50, a hopper 60, and a second valve 70 are provided between the preheater 10 and the pyrolyzer 20 downward from the preheater 10, and heat is carried from the preheater 10 through the pyrolyzer 20.
- a method of gasifying biomass is provided that monitors and controls the supply of medium 30.
- the heat-supporting medium 30, that is, the heat carrier, is preheated in the preheater 10 before being introduced into the pyrolyzer 20.
- the heat-supporting medium 30 is preferably heated to 650 to 800 ° C, more preferably 700 to 750 ° C.
- the biomass for example, high ash biomass
- the amount of pyrolyzed gas generated decreases.
- it exceeds the above upper limit (800 ° C.) it causes volatilization of phosphorus and potassium (potassium), and causes blockage and corrosion of pipes by diphosphorus pentoxide and potassium (potassium).
- it is not expected that the effect will be significantly increased only by giving extra heat, and on the contrary, it will only lead to high cost. It also causes a decrease in the thermal efficiency of the equipment.
- the heat-supporting medium 30 heated to a predetermined temperature in the preheater 10 is then introduced into the pyrolyzer 20.
- the heat-carrying medium 30 is separately contacted with the biomass supplied to the pyrolyzer 20 from the biomass supply port 220.
- the biomass is heated and thermally decomposed to generate a thermal decomposition gas.
- the generated pyrolysis gas passes through the pyrolysis gas introduction pipe 200 and is introduced into the pyrolysis gas reformer 40. At this time, tar, soot, etc.
- the tar, soot, and the like remaining after being gasified are discharged from the bottom of the pyrolyzer 20 while still adhering to the heat-bearing medium 30.
- the pyrolysis gas generated by thermally decomposing the biomass in the pyrolysis device 20 is introduced into the pyrolysis gas reformer 40 through the pyrolysis gas introduction pipe 200.
- the pyrolysis gas introduced into the pyrolysis gas reformer 40 is partially oxidized by air or oxygen, whereby the inside of the pyrolysis gas reformer 40 is heated.
- the pyrolysis gas reacts with steam, and the pyrolysis gas can be reformed into a hydrogen-rich gas.
- the introduction of the heat-bearing medium 30 into the pyrolyzer 20 and the discharge of the heat-bearing medium 30 from the pyrolyzer 20 are carried out, for example, by providing a total of two valves, one on the top and one on the bottom of the pipe, so-called two-stage. It is carried out using the type valve method (FIGS. 2 and 3).
- the heat-bearing medium layer is formed in the pyrolyzer 20 and the thickness of the layer is formed.
- the temperature can be controlled to an appropriate value, and the temperature of the pyrolyzer 20 can be controlled to the above-mentioned predetermined temperature.
- the discharge rate of the heat-bearing medium 30 from the pyrolyzer 20 is too fast, the temperature of the pyrolyzer 20 becomes high, while if the discharge rate is too slow, the heat-supporting medium 30 dissipates heat and heat.
- the temperature of the decomposer 20 becomes low.
- the heat in the stable pyrolyzer 20 is controlled.
- the generation of decomposition gas can be controlled. Therefore, control of the supply rate of the heat-bearing medium 30 from the first valve 50, the second valve 70, and the third valve 90 results in the stable generation of pyrolysis gas in the pyrolyzer 20.
- the control device 100 in the biomass gasification device of the present embodiment controls the supply rate of the heat-carrying medium 30 of the valve to bring about the stable generation of pyrolysis gas in the pyrolyzer 20.
- the control device 100 receives information from the detector 110 provided in any one or more of the preheater 10, the hopper 60, and the thermal decomposition device 20, and the detection unit 101 receives the received information.
- the calculation unit 102 processes and transmits the information after the calculation to the control unit 103, and finally, according to the command from the control unit 103, the first switch 120, the second switch 130, the first valve 50, and the second
- the valve 70, the third valve 90, the steam atomizer 80, and the like are controlled.
- two or three or more control devices 100 may be provided, or only one control device 100 may be provided.
- biomass raw material used in the examples and the gasifier used for the thermal decomposition and gas reforming of the biomass raw material are as follows.
- sewage sludge As a biomass raw material, sewage sludge was granulated and used. The maximum size of the sewage sludge after granulation was about 6 to 15 mm. The properties of the sewage sludge are shown in Table 1. Table 2 shows the composition of the ash obtained by burning the sewage sludge.
- silicon dioxide, aluminum oxide, ferric oxide, magnesium oxide, calcium oxide, sodium oxide, potassium oxide, diphosphorus pentoxide and manganese oxide were measured in accordance with JIS M8815.
- Mercury, chromium, cadmium, copper oxide, lead oxide, zinc oxide and nickel were measured in accordance with JIS Z 7302-5: 2002.
- the gasifier basically includes a pyrolyzer 20, a pyrolyzed gas reformer 40, and a preheater 10 (see FIG. 1), and includes the pyrolyzer 20 and the pyrolyzed gas reformer 40. Is connected by a pyrolysis gas introduction pipe 200 that introduces the pyrolysis gas generated in the pyrolysis device 20 into the pyrolysis gas reformer 40.
- one preheater 10 is provided above the thermal decomposition device 20, and the preheater 10 preheats the heat-bearing medium 30 supplied to the thermal decomposition device 20, and the heated heat.
- the carrying medium 30 is supplied to the thermal decomposer 20, supplies heat necessary for thermal decomposition of biomass, is extracted from the bottom thereof, and is returned to the preheater 10 again.
- the pyrolysis gas generated in the pyrolysis device 20 is introduced into the pyrolysis gas reformer 40 through the pyrolysis gas introduction pipe 200.
- air or oxygen is separately introduced into the pyrolysis gas reformer 40 from the air or oxygen introduction pipes 261,262, whereby the pyrolysis gas is partially burned, and at the same time, steam is generated. It is introduced from the steam inlet 242, the pyrolysis gas is reformed by steam, and the reformed gas obtained thereby is taken out from the reformed gas discharge port 230. Further, instead of the above-mentioned air or oxygen introduction pipe 261 and steam injection port 242, the air or oxygen and steam are provided in the heat decomposition gas introduction pipe 200, and the air or oxygen introduction pipe 262 and the steam injection port 243 are provided. It can be introduced from, or it can be introduced from all air or oxygen introduction pipes 261,262 and steam inlets 242 and 243.
- the inner diameter of the straight body portion of the pyrolyzer 20 was about 550 mm, the height was about 1100 mm, and the internal volume was about 260 liters.
- the inner diameter of the straight body portion of the pyrolysis gas reformer 40 was about 600 mm, the height was about 1200 mm, and the internal volume was about 340 liters.
- the pyrolysis gas introduction pipe 200 is provided on the side of the pyrolyzer 20 on the side of the pyrolyzer 20 below the upper surface of the heat-bearing medium layer formed in the pyrolyzer 20. On the pyrolysis gas reformer 40 side, it is provided on the side surface near the bottom surface of the pyrolysis gas reformer 40. Further, the pyrolysis gas introduction pipe 200 is provided substantially horizontally with respect to the direction of gravity.
- a pipe having a length of about 1000 mm and an inner diameter of about 80 mm is used, the inside thereof is covered with a heat insulating material, and the protruding portion is also formed of the heat insulating material.
- a substantially spherical alumina ball having a diameter (maximum diameter) of 10 to 12 mm is used.
- the heat-supporting medium 30 is pre-filled in the pyrolyzer 20 and the preheater 10 to a height of about 70% of each container, and then the heat-supporting medium 30 is charged in the preheater 10 at a temperature of about 700 ° C. Heat to. Next, the heat-supporting medium 30 is introduced from the top of the pyrolyzer 20 at an amount of 200 kilograms / hour, and an appropriate amount is extracted from the bottom of the pyrolyzer 20 to start circulation of the heat-supporting medium 30.
- the gas phase temperature inside the pyrolyzer 20 and the temperature of the container itself gradually increased. While continuing such circulation of the heat-supporting medium 30, at the same time, the temperature of the heat-supporting medium 30 inside the preheater 10 is gradually raised to 800 ° C. After the heat-bearing medium 30 reaches the temperature, the circulation is further continued to gradually raise the gas phase temperature inside the pyrolyzer 20 from the time when the gas phase temperature of the pyrolyzer 20 exceeds 550 ° C.
- the biomass raw material, nitrogen gas and steam are introduced into the pyrolyzer 20 from the biomass supply port 220, the non-oxidizing gas supply port 250 and the steam inlet 241 respectively, and the temperature of the pyrolyzer 20 becomes 600 ° C. To control.
- the heat-supporting medium 30 is deposited in layers in the pyrolyzer 20, and the accumulated amount is about 60% by volume of the internal volume of the pyrolyzer 20.
- the amount of the heat-carrying medium 30 extracted from the pyrolyzer 20 was the same as the supply amount, and was 200 kg / hour in the pyrolyzer 20.
- the temperature of the heat-supporting medium 30 at the time of extraction is 650 ° C. However.
- the amount of the heat-carrying medium 30 extracted from the pyrolyzer 20 can be appropriately controlled according to the temperature condition.
- the amount of sewage sludge as a biomass raw material is gradually increased from the biomass supply port 220 (see FIG. 2) to the pyrolyzer 20 using a quantitative feeder, and finally about 22 kg. Introduce continuously so that it becomes / hour (drying standard).
- the temperature of the pyrolyzer 20 gradually decreases with the introduction of the biomass raw material, but at the same time, by introducing nitrogen gas and superheated steam into the pyrolyzer 20 while adjusting the supply amount thereof, the pyrolyzer 20 is introduced.
- the temperature of 20 is maintained at 600 ° C. Further, the pressure in the pyrolyzer 20 is maintained at 101.3 kPa.
- nitrogen gas is finally introduced at a fixed amount of 1000 liters / hour from the non-oxidizing gas supply port 250 provided in the upper part of the pyrolyzer 20.
- superheated steam 160 ° C., 0.6 MPa
- the residence time of the biomass raw material in the pyrolyzer 20 is about 1 hour.
- the gas generated by the thermal decomposition in the pyrolyzer 20 is obtained at 15 kilograms / hour.
- char and ash are discharged from the pyrolysis residue (char) outlet 210 at a total of 6.5 kg / hour.
- the pyrolysis gas obtained in the pyrolysis device 20 subsequently passes through the pyrolysis gas introduction pipe 200 from the lower side surface of the pyrolysis device 20 and is introduced into the pyrolysis gas reformer 40.
- the temperature inside the pyrolysis gas reformer 40 becomes unstable, but the superheated steam introduced from the steam inlet 242 provided at the bottom of the pyrolysis gas reformer 40
- the pyrolysis gas is partially combusted and the temperature inside the pyrolysis gas reformer 40 is adjusted to 1000 ° C. do.
- the pyrolysis gas reformer 40 is held at a pressure of 101.3 kPa.
- the superheated steam from the steam inlet 242 provided at the bottom of the pyrolysis gas reformer 40 was finally introduced at a fixed amount of 3.7 kg / hour.
- Oxygen from the air or oxygen inlet 261 is finally introduced at a fixed amount of 2.3 m 3-normal / hour.
- this amount of oxygen is appropriately increased or decreased depending on the degree of temperature rise inside the pyrolysis gas reformer 40.
- the pyrolyzer 20 is held at a temperature of 600 ° C. and a pressure of 101.3 kPa, and the pyrolyzed gas reformer 40 is held at a temperature of 950 ° C. and a pressure of 101.3 kPa.
- the reformed gas having a temperature of 1000 ° C. is obtained from the reformed gas outlet 230 at an amount of 31 kg / hour.
- the obtained reformed gas is collected in a rubber bag, and the gas composition is measured by gas chromatography. Table 3 shows the composition of the obtained reformed gas.
- the operation can be carried out continuously for 3 days. During the operation period, good continuous operation can be maintained without troubles, especially troubles caused by tar. Further, during the operation period, the heat-supporting medium 30 does not become blocked by tar or the like in the pyrolysis gas introduction pipe 200, and the pyrolysis gas from the pyrolysis device 20 to the pyrolysis gas reformer 40 does not occur. Smooth introduction is maintained.
- the amount of tar in the reformed gas taken out from the outlet of the pyrolysis gas reformer 40 is about 10 mg / m 3- normal.
- the reformed gas can be obtained in this way, and by realizing a stable continuous supply of the heat-carrying medium 30 in the gasifier, the pressure fluctuation of the pyrolyzer 20 is suppressed, and the separation ability in gas separation is lowered. It is possible to solve the problem and provide a gas with stable quality.
- the biomass gasifier of the present embodiment includes a preheater 10, a pyrolyzer 20, and a pyrolyzed gas reformer 40, and further supplies a heat-bearing medium 30 from the preheater 10 to the pyrolyzer 20.
- a control device that controls the discharge of the heat-bearing medium 30 from the pyrolyzer 20
- stable continuous supply of the heat-bearing medium 30 in the gasifier is realized, and the pressure fluctuation of the pyrolyzer 20 is suppressed. It is possible to solve problems such as deterioration of separation ability in gas separation and provide gas with stable quality.
- the biomass gasifier of the present embodiment can generate a reformed gas containing a large amount of valuable gas such as hydrogen from biomass, preferably biomass having a relatively high ash content, and is contained in the biomass. not only can prevent clogging and corrosion of the piping caused by the volatilization of diphosphorus pentoxide and potassium (potassium) contained in the ash, resulting suppressing the occurrence of N 2 O, and the generation amount of tar and dust It is expected that it will be widely used as a gasifier for biomass, especially biomass with a relatively high ash content, because it can be reduced.
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Abstract
Description
本発明は、予熱器、熱分解器及び熱分解ガス改質器を有するバイオマスのガス化装置に関する。 The present invention relates to a biomass gasifier having a preheater, a pyrolyzer and a pyrolyzed gas reformer.
高灰分バイオマスのガス化装置としては、例えば、灰分20重量%の下水汚泥を乾燥した後、空気吹き込み式の流動層式熱分解炉にて500~800℃で熱分解し、その熱分解ガスを空気と共に1000~1,250℃の高温で燃焼させ、その熱で水蒸気を発生させてタービン発電を行う方法(特開2002-322902号公報)、原料である高灰分バイオマスを、空気吹き込み式の循環流動加熱炉にて450~850℃の温度で熱分解し、熱分解残渣であるチャーをサイクロンで回収する一方、タールを含む熱分解ガスを、酸素の存在下に1000~1200℃で改質する方法(特開2004-51745号公報)、流動媒体の固着を防ぐために、同様の方法で熱分解してチャーを分離した後に、そのチャーを造粒して循環流動改質炉内に供給し、900~1000℃の温度で焼結することで造粒焼結体を製造する方法(特許4155507号公報)等を採用したものが開示されている。 As a gasifier for high ash biomass, for example, sewage sludge having an ash content of 20% by weight is dried and then pyrolyzed in an air-blown fluidized layer pyrolysis furnace at 500 to 800 ° C. to pyrolyze the pyrolysis gas. A method of generating turbine power by burning with air at a high temperature of 1000 to 1,250 ° C and generating steam with the heat (Japanese Patent Laid-Open No. 2002-322902), high ash biomass as a raw material is circulated by air blowing. Pyrolysis is carried out in a flow heating furnace at a temperature of 450 to 850 ° C., and char, which is a thermal decomposition residue, is recovered by a cyclone, while pyrolysis gas containing tar is reformed at 1000 to 1200 ° C. in the presence of oxygen. Method (Japanese Unexamined Patent Publication No. 2004-51745), in order to prevent sticking of the flow medium, the char is pyrolyzed by the same method to separate the char, and then the char is granulated and supplied into the circulating flow reforming furnace. A method of producing a granulated sintered body by sintering at a temperature of 900 to 1000 ° C. (Japanese Patent No. 4155507) or the like is disclosed.
また、熱を運ぶための熱担持媒体と、この熱担持媒体を加熱するための予熱器と、熱分解ガスの水蒸気改質を行うための改質器と、木質バイオマス原料を熱分解するための熱分解器と、熱担持媒体とチャーとを分離するための分離機と、チャーを燃焼して熱風を生成する熱風炉とを備えており、上記予熱器、改質器及び熱分解器20を、上から順次縦型に配置した装置が知られている(特開2011-144329号公報)。
Further, a heat-carrying medium for carrying heat, a preheater for heating the heat-carrying medium, a reformer for steam reforming of the heat-decomposed gas, and a heat-decomposing wood biomass raw material. The preheater, the reformer, and the
また、熱分解帯域における熱分解器と、反応帯域におけるガス改質器とを別個独立して備えることを基本として、それにより、直列接続型と並列接続型のいずれをも構成し得ることを特徴する装置も提案されている。熱担持媒体が、約1100℃の加熱帯域、950~1000℃の反応帯域、550~650℃の熱分解帯域および分離工程を通過し、引き続き加熱帯域に戻り、熱分解反応器を出た直後に、熱分解コークス及び熱担持媒体からなる混合物を分離して得た熱分解コークスを燃焼装置で燃焼して、これにより発生した顕熱を利用して加熱帯域内で熱担持媒体を加熱することにより、有機物質および物質混合物から高い発熱量を有する生成物ガスを製造する態様(特許4264525号公報)が知られている。 Further, it is characterized in that it is basically provided with a pyrolyzer in the pyrolysis zone and a gas reformer in the reaction zone separately and independently, so that both a series connection type and a parallel connection type can be configured. A device to do so has also been proposed. Immediately after the heat-bearing medium has passed through a heating zone of about 1100 ° C., a reaction zone of 950 to 1000 ° C., a thermal decomposition zone of 550 to 650 ° C., and a separation step, and then returns to the heating zone and exits the thermal decomposition reactor. , The heat-decomposed coke obtained by separating the mixture consisting of the heat-decomposed coke and the heat-bearing medium is burned in a combustion device, and the heat-bearing medium is heated in the heating zone by utilizing the apparent heat generated thereby. , An embodiment of producing a product gas having a high calorific value from an organic substance and a substance mixture (Japanese Patent No. 4264525) is known.
さらに、熱分解器から熱分解ガス改質器に熱分解ガスを導入する熱分解ガス導入管が、熱分解器側において、熱分解器内に形成される予め加熱された熱担持媒体層の上面より下方の熱分解器の側面に設置されるガス化方法(特開2019-65160号公報)が知られている。 Further, a pyrolysis gas introduction tube for introducing the pyrolysis gas from the pyrolysis device to the pyrolysis gas reformer is formed on the pyrolysis device side on the upper surface of the preheated heat-bearing medium layer formed in the pyrolysis device. A gasification method (Japanese Patent Laid-Open No. 2019-65160) installed on the side surface of a lower pyrolyzer is known.
上記のような、予熱器、熱分解器及びガス改質器を備え、予熱器で加熱された熱担持媒体の持つ熱を利用するガス化方法においては、予熱器内で熱風により温めた熱担持媒体を、熱分解器に落とし、木質チップ等のバイオマスと混合してバイオガスを発生させる。 In the gasification method as described above, which is provided with a preheater, a pyrolyzer and a gas reformer and utilizes the heat of the heat-bearing medium heated by the preheater, the heat-supporting heat is carried by hot air in the preheater. The medium is dropped into a pyrolyzer and mixed with biomass such as wood chips to generate biogas.
特開2019-65160号公報では、配管の上下に1個ずつ合計2個のバルブを備えた、いわゆる2段式バルブ方式が使用されている。 Japanese Patent Application Laid-Open No. 2019-65160 uses a so-called two-stage valve system in which a total of two valves are provided, one on the top and one on the bottom of the pipe.
この2段式バルブ方式を採用した場合には、複数の熱担持媒体が固まりで熱分解器に供給されることになる。また、バルブ群の開閉が一巡するのに時間がかかるため、熱担持体の供給は断続的になされることになる。例えば、熱担持媒体が熱分解器に落ちた直後はガス化が良く進むが、次の熱担持媒体が熱分解器に落ちるまではガス化があまり進まない。その結果、熱分解器の圧力が変動する。また、バルブの開閉そのものでも圧力が変動する。このため、木質チップ等の供給口から空気が入ってきたり、あるいはその逆にバイオガスが漏れたりする。また、ガス化が進むときと進まないときでガスの組成や流量等が安定せず、品質が一定のガスが発生しないため、後段に設置するガス中の成分を分離する装置の分離性能を阻害する要因となるという問題も生じ得る。 When this two-stage valve system is adopted, a plurality of heat-supporting media are supplied to the pyrolyzer in a mass. Further, since it takes time for the valve group to open and close once, the heat carrier is supplied intermittently. For example, gasification proceeds well immediately after the heat-supporting medium falls into the pyrolyzer, but gasification does not proceed much until the next heat-supporting medium falls into the pyrolyzer. As a result, the pressure of the pyrolyzer fluctuates. In addition, the pressure fluctuates even when the valve is opened and closed. For this reason, air may enter from the supply port of wood chips or the like, or vice versa, biogas may leak. In addition, the composition and flow rate of the gas are not stable when gasification progresses and when it does not progress, and gas of constant quality is not generated, which hinders the separation performance of the device that separates the components in the gas installed in the subsequent stage. There can also be a problem of becoming a factor.
本発明によるバイオマスのガス化装置は、
熱担持媒体を予め加熱する予熱器と、
前記予熱器で予め加熱された熱担持媒体の供給を受け、熱担持媒体の熱によりバイオマスの熱分解を実行する熱分解器と、
熱分解により発生した熱分解ガスを、空気又は酸素により少なくとも部分的に燃焼する熱分解ガス改質器と、
前記予熱器と前記熱分解器との間に設けられ、予熱器からの熱担持媒体を熱分解器に供給するための供給機構と、
を備え、
前記供給機構は、
熱担持媒体を一時的に貯留するための開閉部と、
前記開閉部の下方に設けられ、揺動又は回転することで前記開閉部から供給された熱担持媒体を熱分解器に供給する調整部と、
を有してもよい。
The biomass gasifier according to the present invention
A preheater that preheats the heat-supporting medium and
A thermal decomposer that receives a supply of a heat-bearing medium preheated by the preheater and executes thermal decomposition of biomass by the heat of the heat-bearing medium.
A pyrolysis gas reformer that at least partially burns the pyrolysis gas generated by pyrolysis with air or oxygen.
A supply mechanism provided between the preheater and the pyrolyzer for supplying the heat-carrying medium from the preheater to the pyrolyzer, and
With
The supply mechanism
An opening / closing part for temporarily storing the heat-carrying medium and
An adjusting unit provided below the opening / closing unit and supplying the heat-carrying medium supplied from the opening / closing unit to the pyrolyzer by swinging or rotating.
May have.
本発明によるバイオマスのガス化装置において、
前記開閉部は、第1開閉部と、前記第1開閉部の下方に設けられた第2開閉部と、を有し、
前記第2開閉部が閉状態の間に前記第1開閉部を開状態とし、前記第1開閉部が閉状態の間に前記第2開閉部を開状態とする制御装置を備えてもよい。
In the biomass gasification device according to the present invention
The opening / closing portion has a first opening / closing portion and a second opening / closing portion provided below the first opening / closing portion.
A control device may be provided which opens the first opening / closing portion while the second opening / closing portion is closed and opens the second opening / closing portion while the first opening / closing portion is closed.
本発明によるバイオマスのガス化装置において、
第1開閉部及び第2開閉部の各々がダンパバルブであってもよい。
In the biomass gasification device according to the present invention
Each of the first opening / closing part and the second opening / closing part may be a damper valve.
本発明によるバイオマスのガス化装置は、
前記予熱器と前記熱分解器との間に設けられたホッパと、
前記ホッパ内の熱担持媒体の重量又は上面位置に基づいて、前記予熱器から前記熱分解器への前記熱担持媒体の供給を制御する制御装置と、
を備えてもよい。
The biomass gasifier according to the present invention
A hopper provided between the preheater and the pyrolyzer,
A control device that controls the supply of the heat-supporting medium from the preheater to the pyrolyzer based on the weight or top surface position of the heat-supporting medium in the hopper.
May be provided.
本発明によるバイオマスのガス化装置において、
前記調整部はスイングバルブ又はロータリーバルブであってもよい。
In the biomass gasification device according to the present invention
The adjusting portion may be a swing valve or a rotary valve.
本発明によるバイオマスのガス化装置において、
前記開閉部が開状態のときに、前記予熱器と前記熱分解器との間に水蒸気を噴霧する水蒸気噴霧器を備えてもよい。
In the biomass gasification device according to the present invention
A steam atomizer that sprays steam between the preheater and the pyrolyzer when the opening / closing portion is in the open state may be provided.
本発明によるバイオマスのガス化装置において、
前記調整部が揺動部からなり、
前記揺動部の揺動周期時間又は揺動距離を変更することで、前記熱分解器への前記熱担持媒体の供給量を制御する制御装置を備えてもよい。
In the biomass gasification device according to the present invention
The adjusting part is composed of a swinging part.
A control device for controlling the supply amount of the heat-carrying medium to the pyrolyzer may be provided by changing the swing cycle time or the swing distance of the swing portion.
本発明によるバイオマスのガス化装置において、
前記調整部が回転部からなり、
前記制御装置が、前記回転部の回転数を変更することで、前記熱分解器への前記熱担持媒体の供給量を制御してもよい。
In the biomass gasification device according to the present invention
The adjusting part is composed of a rotating part.
The control device may control the supply amount of the heat-carrying medium to the pyrolyzer by changing the rotation speed of the rotating portion.
本発明によるバイオマスのガス化装置において、
前記熱分解器の下方に設けられた第3バルブと、
前記第3バルブが開状態のときに、水蒸気を噴霧する水蒸気噴霧器と、を備えてもよい。
In the biomass gasification device according to the present invention
A third valve provided below the pyrolyzer and
A steam atomizer that sprays steam when the third valve is in the open state may be provided.
本発明において、供給機構が、熱担持媒体を一時的に貯留するための開閉部と、開閉部の下方に設けられ、揺動又は回転することで開閉部から供給された熱担持媒体を熱分解器に供給する調整部と、を有する態様を採用した場合には、安定した量でガス化が可能となる。 In the present invention, the supply mechanism is provided at the opening / closing part for temporarily storing the heat-carrying medium and below the opening / closing part, and the heat-carrying medium supplied from the opening / closing part is thermally decomposed by swinging or rotating. When an embodiment having an adjusting unit for supplying to the vessel is adopted, gasification can be performed in a stable amount.
図1に示すように、本実施の形態のバイオマスのガス化装置は、熱担持媒体30を予め加熱する予熱器10と、予熱器10で予め加熱された熱担持媒体30の供給を受け、熱担持媒体30の持つ熱によりバイオマスの熱分解を実行する熱分解器(バイオマス熱分解器)20と、熱分解により発生した熱分解ガスを、空気又は酸素により部分燃焼してスチーム改質を実行する熱分解ガス改質器40と、予熱器10と熱分解器20との間に設けられ、予熱器10からの熱担持媒体30を熱分解器に供給するための供給機構と、を有している。
As shown in FIG. 1, the biomass gasifier of the present embodiment receives heat from the
熱担持媒体30(「ヒートキャリア」ともいう。)は、複数の粒状物及び/又は塊状物であり、好ましくは、金属及びセラミックより成る群から選ばれる一以上の材質からなる。金属としては、好ましくは、鉄、ステンレス鋼、ニッケル合金鋼、及び、チタン合金鋼より成る群から選ばれ、より好ましくは、ステンレス鋼が選ばれる。また、セラミックとしては、アルミナ、シリカ、シリコンカーバイド、タングステンカーバイド、ジルコニア及び窒化ケイ素より成る群から選ばれ、より好ましくは、アルミナが選ばれる。 The heat-supporting medium 30 (also referred to as "heat carrier") is a plurality of granules and / or lumps, preferably made of one or more materials selected from the group consisting of metals and ceramics. The metal is preferably selected from the group consisting of iron, stainless steel, nickel alloy steel, and titanium alloy steel, and more preferably stainless steel. The ceramic is selected from the group consisting of alumina, silica, silicon carbide, tungsten carbide, zirconia and silicon nitride, and more preferably alumina.
熱担持媒体30の形状は、好ましくは球状(ボール)であるが、必ずしも真球である必要はなく、断面形状が楕円形又は長円形である球状物であってもよい。球状物の直径(最大径)は、好ましくは3~25mm、より好ましくは8~15mmである。上記上限(25mm)を超えては、熱分解器20内部での流動性、即ち、自由落下性を損なうことがあり、これにより、球状物が熱分解器20内部で静止して閉塞の原因となることがある。一方、上記下限(3mm)未満では、熱分解器20において、球状物に付着したタール及び煤塵等により球状物自体が固着することがあり、閉塞の原因となることがある。例えば、球状物の直径が3mm未満では、球状物に付着したタール及び煤塵等の影響により、球状物が、熱分解器20の内壁に付着して成長し、最悪の場合には、熱分解器20を閉塞させてしまうことが懸念される。また、タールが付着した球状物が、熱分解器20の底部のバルブから抜き出される際、3mm未満の球状物は軽く、そのうえタールが付着しているために自然落下せずにバルブ内部に固着して閉塞を助長することがある。
The shape of the heat-supporting
本実施の形態のバイオマスとは、いわゆるバイオマス資源を言う。ここで、バイオマス資源とは、植物系バイオマス、例えば、林業から廃棄される間伐材、製材廃材、剪定枝、林地残材、未利用樹等、農業から廃棄される野菜残渣及び果樹残渣等の農作物、稲藁、麦藁及び籾殻等、その他海洋植物、建設系廃木材等;生物系バイオマス、例えば、家畜排せつ物及び下水汚泥に代表される生物系排せつ物;並びに塵芥等の生活雑排出物及び食品廃棄物等を言う。本実施の形態の装置は、好ましくは植物系バイオマス及び生物系バイオマスのガス化に適している。なかでも、灰分が、乾燥基準で、好ましくは5.0質量%以上、より好ましくは10.0~30.0質量%、更に好ましくは15.0~20.0質量%である高灰分バイオマス、とりわけ、下水汚泥及び家畜排せつ物のガス化に適している。 The biomass of this embodiment means a so-called biomass resource. Here, the biomass resource refers to plant-based biomass, for example, agricultural products such as thinned wood, sludge waste, pruned branches, forest land residue, unused trees, etc., which are discarded from agriculture, and vegetable residues and fruit tree residues, which are discarded from agriculture. , Rice straw, wheat straw, rice husks, etc., other marine plants, construction waste wood, etc .; biological biomass, for example, biological waste such as livestock excrement and sewage sludge; And so on. The apparatus of this embodiment is preferably suitable for gasification of plant-based biomass and biological-based biomass. Among them, high ash biomass having an ash content of preferably 5.0% by mass or more, more preferably 10.0 to 30.0% by mass, and further preferably 15.0 to 20.0% by mass on a drying basis. In particular, it is suitable for gasification of sewage sludge and livestock excrement.
予熱器10で予め加熱された熱担持媒体30は、予熱器10から後述するバルブを介して熱分解器20へ自由落下により供給される。熱分解器20内において、熱担持媒体30は、それ自身の熱により熱分解器20内に供給されたバイオマスの熱分解を引き起こす。熱分解器20内の熱担持媒体30は、熱分解器20からバルブを介して自由落下により排出され、好ましくは予熱器10へと再循環する。
The heat-supporting
図4に示す構成では、予熱器10と熱分解器20との間に、予熱器10から下方に向かって、第1バルブ50、ホッパ60及び第2バルブ70が設けられている。供給機構は、開閉自在となり、熱担持媒体を一時的に貯留するための開閉部と、開閉部の下方に設けられ、揺動又は回転することで開閉部から供給された熱担持媒体を熱分解器に供給する第2調整部と、を有している。開閉部が閉状態にあるときに、その上方に熱担持媒体が載置され、一時的に貯留されることになる。図4に示す構成では、開閉部が第1バルブ50の第1開閉部及び第2開閉部(後述する第1ダンパバルブ51a及び第2ダンパバルブ51b)からなり、第2調整部が第2バルブ70からなっている。
In the configuration shown in FIG. 4, a
ホッパ60内の熱担持媒体30の重量又は上面位置を監視し、監視結果に基づいて、第1バルブ50及び第2バルブ70の動作を制御して、予熱器10から熱分解器20を通した熱担持媒体30の供給を制御する制御装置100が設けられてもよい。このような制御装置100を採用する場合には、ガス化装置における熱担持媒体30の安定的な連続供給、熱分解器20の圧力変動の安定化、ガス分離における分離能の向上を可能にし、さらに品質の安定したガスを提供することができる。
The weight or top surface position of the heat-carrying
第1バルブ50は、第1調整部と、第1調整部の下方に設けられた第1開閉部と、第1開閉部の下方に設けられた第2開閉部と、を有してもよい。そして、第2開閉部が閉状態の間に第1開閉部を開状態とし、第1開閉部が閉状態の間に前記第2開閉部を開状態とするように制御装置100が制御することで、第1バルブ50の上方側の気体と下方側の気体とが混合されてしまうことを防止できるようにしてもよい。第1開閉部及び第2開閉部の各々はダンパバルブであってもよい。以下では、第1開閉部が第1ダンパバルブ51aであり、第2開閉部が第2ダンパバルブ51bである態様を用いて説明する。また、第1バルブ50の第1調整部がスイングバルブ52である態様を用いて説明する。また、第2バルブ70の第2調整部がスイングバルブ72又はロータリーバルブ74である態様を用いて説明する。
The
本実施の形態では、バイオマスのガス化装置の熱担持媒体30の供給方式は、熱担持媒体30を熱分解器20に落とすために、スイングバルブ52の揺動(図3A乃至図3D参照)、ダンパバルブ51の開閉を組み合わせて自由落下で熱担持媒体30を熱分解器20へ落とす方法が採用されている。
In the present embodiment, in the method of supplying the heat-bearing
2段式バルブ方式の操作を簡単に説明すると、上下2個の第1ダンパバルブ51a及び第2ダンパバルブ51bを閉じておき(図3A)、第1ダンパバルブ51aを開いて熱担持媒体30を配管内部に落下させ、第2ダンパバルブ51bと第1ダンパバルブ51aとの間に熱担持媒体30を充填する(図3B)。次いで、第1ダンパバルブ51aを閉じ(図3C)、第2ダンパバルブ51bを開くことによって、第1ダンパバルブ51aと第2ダンパバルブ51bの間に充填された熱担持媒体30を熱分解器20へ導入するか、又は熱分解器20から排出する(図3D)。このようなバルブ操作を繰り返すことによって、熱担持媒体30は熱分解器20に導入され、かつ、熱分解器20から排出される。このような機構を採用することで、熱担持媒体30を加熱するための高温ガスと、バイオマスによるガス(水素、メタン、一酸化炭素等を含んだ混合ガス)とが混ざってしまうことを防止できる。
To briefly explain the operation of the two-stage valve system, the upper and lower two
スイングバルブ52は、固体が下部へ流れている途中で、振り子のような動きで流れを止めるのに適したバルブであるが、ガスのシール性はない。このようなスイングバルブ52を設けることで、熱担持媒体30が一気に供給されることを防止でき、熱担持媒体30が管300の中でスタックしてしまうことを防止できる。
The
バイオマスのガス化装置における予熱器10の下部に位置する熱分解器20においては、上方(上部)、好ましくは頂部に、熱担持媒体30の導入口が備えられ、熱分解器20の下方(下部)、好ましくは底部に、熱担持媒体30の排出口が備えられる。
The
本実施の形態のガス化装置においては、熱分解器20の上部に、熱担持媒体30を予め加熱するための予熱器10が備えられ、熱担持媒体30が所定の温度に加熱される。予熱器10は、熱分解器20の上部に好ましくは1器設けて、そこで全ての熱担持媒体30を所定の温度に加熱して、当該温度に加熱された熱担持媒体30を、熱分解器20に供給することができる。
In the gasification device of the present embodiment, a
本実施の形態では、図1に示すように、熱分解器20と排出物処理装置240との間に第3バルブ90が設けられてもよい。第3バルブ90は、第1バルブ50と同様、開閉部の一例である一対のダンパバルブ91a,91b及び調整部の一例であるスイングバルブ(第3調整部)92を有してもよい(図2参照)。第3バルブ90においても、スイングバルブ92、第1ダンパバルブ91a及び第2ダンパバルブ91bが上から順番に配置されてもよい。排出物処理装置240にはフィルタFが設けられており(図1参照)、バイオマスのガスに含まれていた煤はフィルタFを介して下方に落下し、フィルタFを通過しない熱担持媒体30はエレベータ式、エスカレーター式等からなる循環部290によって循環され、予熱器10に投入されることになる。
In the present embodiment, as shown in FIG. 1, a
予熱器10と熱分解器20との間及び/又は熱分解器20と排出物処理装置240との間で、水蒸気噴霧器80によって水蒸気が噴霧されるようにしてもよい(図5参照)。このような態様を採用した場合には、水蒸気によって気体の流れを遮断でき、予熱器10を流れる加熱用の気体とバイオマスによるガスが混ざってしまうことを防止できる。このような態様を採用する場合には、ダンパバルブを1つだけ用い、当該ダンパバルブが開状態になるときに水蒸気噴霧器80によって水蒸気を噴霧することで、気体の流れを遮断するようにしてもよい。このような制御は制御装置100からの指令によって行われてもよい。なお、水蒸気噴霧器80が設けられる場合であっても、ダンパバルブは2つ以上設けられてもよい。
Steam may be sprayed by the
ホッパ60及び熱分解器20における熱担持媒体30の重量又は上面位置を検知する検知器110が設けられてもよい(図4参照)。そして、制御装置100は、検知器110からのデータに基づいた指令又は検知器110からのデータを用いた演算に基づいた指令を、第1バルブ50及び第2バルブ70に、また第3バルブ90及び水蒸気噴霧器80に伝達することで、第1バルブ50、第2バルブ70、第3バルブ90及び水蒸気噴霧器80の動作を制御することができる。制御装置100は、検知器110からの情報を受け取る検知部101と、検知部101の情報を演算して指令としての情報を制御部103に伝える演算部102と、バルブ50,70,90及び水蒸気噴霧器80に指令を伝達する制御部103と、を有してもよい(図5及び図8参照)。制御装置100からの指令によって、第1スイッチ120や第2スイッチ130等のスイッチが駆動され、バルブ50,70,90や水蒸気噴霧器80が駆動されるようにしてもよい。
A
第2バルブ70は、連続的に揺動する1又は複数のスイングバルブ72で構成することができるが、1つのスイングバルブ72で構成することが好ましい。
The
第2バルブ70が1又は複数のロータリーバルブ74(図2及び図9参照)で構成することができるが、1つのロータリーバルブ74で構成することが好ましい。ロータリーバルブ74は複数の空間に仕切られており、ロータリーバルブ74が回転することで、各空間に収容された熱担持媒体30が順次落下することになる(図9参照)。
The
制御装置100が、スイングバルブ72の揺動の周期時間及び/又は揺動距離を変更することで、熱分解器20への熱担持媒体30の供給量を制御してもよい。ロータリーバルブ74の回転数を変更することで、熱分解器20への熱担持媒体30の供給量を制御するようにしてもよい。このような制御を行うことで、熱担持媒体30の供給量を適宜調整することができる。
The
また、ホッパ60を設け、ホッパ60の下方に第2バルブ70を設けることで、ホッパ60で熱担持媒体30を一度受けることで熱担持媒体30の落下による衝撃をホッパ60で吸収しつつ、当該熱担持媒体30を第2バルブ70で調整しつつ熱分解器20へ供給することができるようになる。このため、より安定した状態で熱担持媒体30を供給することができるようになる。
Further, by providing the
[第1の態様]
本実施の形態のバイオマスのガス化装置における制御装置100の第1の態様は、予熱器10と熱分解器20との間に予熱器10から下方に向かって、第1バルブ50、ホッパ60及び第2バルブ70が設けられている。そして、制御装置100が、予熱器10から熱分解器20を通した熱担持媒体30の供給を監視して、監視結果に基づいて、第1バルブ50及び第2バルブ70の動作を制御している。このことにより、ガス化装置における熱担持媒体30の安定的な連続供給を実現し、熱分解器20の圧力変動を抑え、ガス分離における分離能の低下等問題を解決して、品質の安定したガスを提供することができる。
[First aspect]
The first aspect of the
第1の態様では、制御装置100は、ホッパ60内における予熱器10から第1バルブ50を通して供給される熱担持媒体30の重量又は上面位置(以下、「レベル」ともいう。)を監視して、重量又はレベルが所定値を下回れば第1スイッチ120を作動して第1バルブ50を開く。他方、重量又は上面位置が所定値を上回れば第2スイッチ130を作動して第1バルブ50を閉じる。熱担持媒体30を第2バルブ70に連続的に供給し、ホッパ60から熱分解器20に供給される熱担持媒体30の供給量は、第2バルブ70の開度によって制御される。
In the first aspect, the
[第2の態様]
第2の態様では、第1バルブ50が開いたときに、当該バルブに水蒸気パルスを噴霧して水蒸気でシールする水蒸気噴霧器80が設けられている(図5参照)。制御装置100は水蒸気噴霧器80の動作を制御して、第1バルブ50のシール性をより向上され、ガスの逆流を防止することもできる。
[Second aspect]
In the second aspect, when the
第3バルブ90が開いたときに当該第3バルブ90に水蒸気パルスを噴霧して水蒸気でシールする水蒸気噴霧器80が設けられてもよい。制御装置100が、第3バルブ90が開いたときに当該第3バルブ90に水蒸気パルスを噴霧するように水蒸気噴霧器80を制御して、熱分解器20からの熱担持媒体30の排出を制御して、第3バルブ90のシール性をより向上させ、ガスの逆流を防止することもできる。
When the
第1バルブ50は、上部の1又は複数のスイングバルブ52及び下部の1又は複数のダンパバルブ51で構成され、水蒸気噴霧器80からの水蒸気パルス噴霧は、ダンパバルブ51の開きに連動することが好ましい。
The
第3バルブ90は、上部の1又は複数のスイングバルブ92及び下部の1又は複数のダンパバルブ91で構成され、水蒸気噴霧器80からの水蒸気パルス噴霧は、ダンパバルブ91の開きに連動することが好ましい。
The
[第3の態様]
第3の態様では、制御装置100が、ホッパ60において、予め定まった設定値W0 kg/hと比較して、熱分解器20への熱担持媒体30の単位時間あたりの供給量W kg/hが大きいときには第2バルブ70の開度を小さくして減少させ、供給量W kg/hが小さいときには第2バルブ70の開度を大きくすることにより増大させ、熱分解器20への熱担持媒体30の供給量を制御するようにしてもよい。
[Third aspect]
In the third aspect, the
なお、初期レベルをHとし、終期レベルをLとした場合、初期レベルHから終期レベルLに至る時間tや重量を計測するようにしてもよい(図10参照)。ホッパ60の断面積をSとし、熱担持媒体30のかさ密度をρとした場合、上記時間tを用いて計算すると、
S×(H-L)×ρ=減少熱媒体重量w(kg)
w/t=減少速度(kg/h)
となる。
上記減少速度(w/t)を用いて設定値W0及び供給量Wを算出し、上記のような制御を行うようにしてもよい。
When the initial level is H and the final level is L, the time t and the weight from the initial level H to the final level L may be measured (see FIG. 10). When the cross-sectional area of the
S × (HL) × ρ = reduced heat medium weight w (kg)
w / t = decrease rate (kg / h)
Will be.
The set value W 0 and the supply amount W may be calculated using the decrease rate (w / t), and the above control may be performed.
[第4の態様]
第4の態様では、予熱器10内、ホッパ60内及び熱分解器20内のいずれか1つ以上において、熱担持媒体30の重量又は上面位置を検知器110により常時監視するようにしてもよい(図4及び図6乃至図8参照)。熱担持媒体30を例に採ると、重量又は上面位置が一定値を下回れば、通常速度Xより速い速度で第3バルブ90を開閉する指令を第3バルブ90に伝達し、重量又は上面位置が一定値を上回れば、通常速度Xより遅い速度で第3バルブ90を開閉する指令を第3バルブ90に伝達し、重量又は上面位置が一定量のときは、通常速度で開閉するように、第3バルブ90の動作を制御して、第3バルブ90の開閉を制御することもできる。
[Fourth aspect]
In the fourth aspect, the weight or the upper surface position of the heat-carrying
[その他の変形例]
本実施の形態のバイオマスのガス化装置における制御装置100の態様を、従来のバイオマスのガス化装置に組み込んでもよい。
[Other variants]
The aspect of the
熱分解器20が、バイオマス供給口、並びに、非酸化性ガス供給口及び/又はスチーム吹込み口を有し、
熱分解ガス改質器40が、スチーム吹込み口及び改質ガス排出口を有し、
熱分解器20において発生した熱分解ガスを熱分解ガス改質器40へと導入する、熱分解器20と上記熱分解ガス改質器40との間に備えられた、熱分解ガス導入管200を含み、
熱分解器20及び熱分解ガス改質器40が、夫々更に、予め加熱された熱担持媒体の導入口及び排出口を備え、熱担持媒体の持つ熱により、バイオマスの熱分解及びバイオマスの熱分解により発生した熱分解ガスの改質を実行し、
熱分解器20と熱分解ガス改質器40とが、熱担持媒体の流れに対して並列に備えられており、かつ、熱分解ガス導入管200が、熱分解器20及び熱分解ガス改質器40の両側において、熱分解器20及び熱分解ガス改質器40内に夫々形成される、熱担持媒体層の上面より下方の上記熱分解器20及び熱分解ガス改質器40の側面に備えられており、かつ、熱分解ガス導入管200が、重力方向に対して略水平に備え、
予熱器10と熱分解器20との間に予熱器10から下方に向かって、第1バルブ50、ホッパ60及び第2バルブ70が設けられ、
制御装置100が、ホッパ60内の熱担持媒体30の重量又は上面位置を監視し、監視結果に基づいて第1バルブ50及び第2バルブ70の動作を制御して、予熱器10から熱分解器20を通した熱担持媒体30の供給を制御する制御装置100を組み込むバイオマスのガス化装置を提供することができる。
The
The
A pyrolysis
Each of the
The
A
The
また、熱分解器20が、バイオマス供給口、並びに、非酸化性ガス供給口及び/又はスチーム吹込み口を有し、
熱分解ガス改質器40がスチーム吹込み口及び改質ガス排出口を有し、
熱分解器20と熱分解ガス改質器40との間に備えられた熱分解ガス導入管200とを備え、熱分解器20において発生した熱分解ガスを上記熱分解ガス改質器40へと導入し、
熱分解器20が、更に、予め加熱された熱担持媒体の導入口及び排出口を備え、上記熱担持媒体の持つ熱により、バイオマスの熱分解を実行し、
一方、熱分解ガス改質器40が、バイオマスの熱分解により発生した熱分解ガスのスチーム改質を実行し、
熱分解ガス改質器40が、更に、空気又は酸素吹込み口を備え、該空気又は酸素により、バイオマスの熱分解により発生した熱分解ガスを部分燃焼することにより、スチーム改質を実行し、
熱分解ガス導入管200が、熱分解器20内に形成される、熱担持媒体層の上面より下方の熱分解器20の側面に備えられ、
予熱器10と熱分解器20との間に予熱器10から下方に向かって、第1バルブ50、ホッパ60、及び第2バルブ70が備えられ、制御装置100が、ホッパ60内の熱担持媒体30の重量又は上面位置を監視し、監視結果に基づいて第1バルブ50及び第2バルブ70の動作を制御して、予熱器10から熱分解器20を通した熱担持媒体30の供給を制御する、制御装置100を組み込むバイオマスのガス化装置を提供することができる。
Further, the
The
A pyrolysis
The
On the other hand, the
The
The pyrolysis
A
本実施の形態の他の形態では、バイオマスを、非酸化性ガス雰囲気下又は非酸化性ガスとスチームとの混合ガス雰囲気下において加熱する熱分解器20と、上記熱分解器20において発生したガスを、スチームの存在下に改質する熱分解ガス改質器40とを備え、かつ、予め加熱された熱担持媒体30を、上記熱分解器20に投入させて、上記熱担持媒体30物の持つ熱により、バイオマスの熱分解を実行し、次いで、該バイオマスの熱分解により発生した熱分解ガスを、上記熱分解ガス改質器40に導入して、該熱分解ガスのスチーム改質を実行し、
上記バイオマスの熱分解により発生した熱分解ガスが、上記熱分解器20内に形成される、上記熱担持媒体層の上面より下方の上記熱分解器20の側面に備えられた熱分解ガス導入管200を通って、上記熱分解ガス改質器40に導入され、次いで、該熱分解ガス改質器40に、別途、導入された空気又は酸素により、上記の導入された熱分解ガスが、部分酸化されると同時に、上記空気又は酸素と同時に導入されたスチームにより改質される、バイオマスのガス化方法において、
予熱器10と熱分解器20との間に予熱器10から下方に向かって、第1バルブ50、ホッパ60、及び第2バルブ70を備え、予熱器10から熱分解器20を通した熱担持媒体30の供給を監視して制御する、バイオマスのガス化方法が提供される。
In another embodiment of the present embodiment, the
A pyrolysis gas introduction tube provided on the side surface of the
A
本実施の形態の態様の一例について説明する。 An example of the embodiment of the present embodiment will be described.
熱担持媒体30、即ち、ヒートキャリアは、熱分解器20に導入される前に、予熱器10において予め加熱される。熱担持媒体30は、好ましくは650~800℃、より好ましくは700~750℃に加熱される。上記下限(650℃)未満では、熱分解器20においてバイオマス、例えば、高灰分バイオマスを十分に熱分解することができず、熱分解ガスの発生量が低下する。一方、上記上限(800℃)を超えては、リンやカリ(カリウム)の揮散を引き起こし、五酸化二リン及びカリ(カリウム)による配管の閉塞及び腐食を引き起こす原因になる。また、余分な熱を与えるばかりで著しい効果の増大は期待できず、却って、コスト高を招くばかりである。また、設備の熱効率低下の原因にもなる。
The heat-supporting
予熱器10において所定温度に加熱された熱担持媒体30は、次いで、熱分解器20に導入される。熱分解器20において、熱担持媒体30は、別途、バイオマス供給口220から熱分解器20に供給されたバイオマスと接触される。熱担持媒体30とバイオマスとの接触により、バイオマスが加熱されて熱分解し、熱分解ガスが生成する。生成した熱分解ガスは、熱分解ガス導入管200を通過して、熱分解ガス改質器40に導入される。この際、生成した熱分解ガスに含まれるタール及び煤塵等は、熱分解ガス導入管200内に保有される熱担持媒体30により捕捉され、タールの一部又は大部分は熱担持媒体30により加熱されてガス化され、残存したタール及び煤塵等は、熱担持媒体30に付着したまま、熱分解器20の底部から排出される。
The heat-supporting
熱分解ガス改質器40には、熱分解器20においてバイオマスを熱分解することにより生成した熱分解ガスが、熱分解ガス導入管200を通って導入される。熱分解ガス改質器40に導入された熱分解ガスは、空気又は酸素により部分酸化され、それにより、熱分解ガス改質器40内が加熱される。これにより、熱分解ガスとスチームとが反応して、熱分解ガスを水素に富むガスへと改質することができる。
The pyrolysis gas generated by thermally decomposing the biomass in the
熱分解器20におけるバイオマスの熱分解に必要な熱の殆どは、上記の温度に予め加熱された熱担持媒体30の持つ熱により供給される。熱担持媒体30の熱分解器20への導入、並びに、熱担持媒体30の熱分解器20からの排出は、例えば、配管の上下に1個ずつ合計2個のバルブを備えた、いわゆる2段式バルブ方式(図2及び図3)を使用して行われている。
Most of the heat required for the thermal decomposition of biomass in the
熱担持媒体30の熱分解器20への導入及び熱担持媒体30の熱分解器20からの排出速度を制御することにより、熱分解器20において熱担持媒体層を形成せしめると共に、その層の厚さを適切な値に制御し、かつ、熱分解器20の温度を上記所定温度に制御することができる。ここで、熱担持媒体30の熱分解器20からの排出速度が速過ぎると、熱分解器20の温度が高くなり、一方、排出速度が遅過ぎると、熱担持媒体30が放熱して、熱分解器20の温度が低くなる。
By introducing the heat-bearing
以上のように、予熱器10から熱分解器20への熱担持媒体30の導入、及び熱分解器20からの熱担持媒体30の排出速度を制御することにより、安定した熱分解器20における熱分解ガスの生成を制御することができる。したがって、第1バルブ50、第2バルブ70及び第3バルブ90からの熱担持媒体30の供給速度の制御は、安定した熱分解器20における熱分解ガスの生成をもたらす。本実施の形態のバイオマスのガス化装置における制御装置100は、以上のバルブの熱担持媒体30の供給速度を制御して、安定した熱分解器20における熱分解ガスの生成をもたらす。
As described above, by introducing the heat-bearing medium 30 from the
図8に示すように、制御装置100は、予熱器10、ホッパ60及び熱分解器20のいずれか1つ以上に設けられた検知器110からの情報を検知部101が受け取り、受け取った情報を演算部102が処理をして、演算後の情報を制御部103に伝達し、最後に、制御部103からの指令にしたがい、第1スイッチ120、第2スイッチ130、第1バルブ50、第2バルブ70、第3バルブ90、水蒸気噴霧器80等が制御される。図8に示すように、2つ又は3つ以上の制御装置100が設けられてもよいし、1つの制御装置100だけが設けられてもよい。
As shown in FIG. 8, the
以下、本実施の形態を実施例により更に詳細に説明するが、本実施の形態はこれら実施例により限定されるものではない。 Hereinafter, the present embodiment will be described in more detail with reference to the examples, but the present embodiment is not limited to these examples.
実施例において使用したバイオマス原料、並びに、該バイオマス原料の熱分解及びガス改質に使用したガス化装置は、下記の通りである。 The biomass raw material used in the examples and the gasifier used for the thermal decomposition and gas reforming of the biomass raw material are as follows.
バイオマス原料としては、下水汚泥を造粒して使用した。造粒後の下水汚泥の大きさは、最大寸法が6~15mm程度のものであった。該下水汚泥の性状を表1に示す。また、該下水汚泥を燃焼して得られた灰の組成を表2に示す。 As a biomass raw material, sewage sludge was granulated and used. The maximum size of the sewage sludge after granulation was about 6 to 15 mm. The properties of the sewage sludge are shown in Table 1. Table 2 shows the composition of the ash obtained by burning the sewage sludge.
表1の各値に関して、水分、揮発分及び固定炭素は、JIS M8812に準拠し、灰分は、JIS Z 7302-4:2009に準拠し、かつ、高位発熱量は、JIS M8814に準拠して測定したものである。また、元素組成のうち、炭素(C)、水素(H)及び窒素(N)は、いずれもJIS Z 7302-8:2002に準拠し、硫黄(S)は、JIS Z 7302‐7:2002に準拠し、かつ、塩素(Cl)は、JIS Z 7302‐6:1999に準拠して測定したものである。また、酸素(O)は、100質量%から、C、H、N、S、Cl及び灰分の各質量%を差し引いて求めたものである。ここで、灰分、揮発分、固定炭素及び元素組成は、いずれも乾燥基準で算出したものである。また、水分は、バイオマス原料(下水汚泥)の受け入れ時のものである。 For each value in Table 1, moisture, volatile matter and fixed carbon are measured according to JIS M8812, ash content is measured according to JIS Z 7302-4: 2009, and high calorific value is measured according to JIS M8814. It was done. In addition, among the elemental compositions, carbon (C), hydrogen (H) and nitrogen (N) all conform to JIS Z 7302-8: 2002, and sulfur (S) conforms to JIS Z 7302-7: 2002. Compliant and chlorine (Cl) was measured in accordance with JIS Z 7302-6: 1999. Further, oxygen (O) was obtained by subtracting each mass% of C, H, N, S, Cl and ash content from 100 mass%. Here, the ash content, the volatile content, the fixed carbon, and the elemental composition are all calculated on a drying basis. Moisture is the one at the time of receiving the biomass raw material (sewage sludge).
表2の各値に関して、二酸化ケイ素、酸化アルミニウム、酸化第二鉄、酸化マグネシウム、酸化カルシウム、酸化ナトリウム、酸化カリウム、五酸化二リン及び酸化マンガンは、JIS M8815に準拠して測定したものである。また、水銀、クロム、カドミウム、酸化銅、酸化鉛、酸化亜鉛及びニッケルは、JIS Z 7302‐5:2002に準拠して測定したものである。 Regarding each value in Table 2, silicon dioxide, aluminum oxide, ferric oxide, magnesium oxide, calcium oxide, sodium oxide, potassium oxide, diphosphorus pentoxide and manganese oxide were measured in accordance with JIS M8815. .. Mercury, chromium, cadmium, copper oxide, lead oxide, zinc oxide and nickel were measured in accordance with JIS Z 7302-5: 2002.
ガス化装置は、基本的には、熱分解器20、熱分解ガス改質器40及び予熱器10を有するものであり(図1参照)、熱分解器20と熱分解ガス改質器40とは、熱分解器20において発生した熱分解ガスを、熱分解ガス改質器40へと導入する熱分解ガス導入管200により接続されている。
The gasifier basically includes a
ここで、熱分解器20の上部に予熱器10が1器備えられており、該予熱器10は、熱分解器20に供給する熱担持媒体30を予め加熱するものであり、加熱された熱担持媒体30は、熱分解器20に供給されて、バイオマスの熱分解に必要な熱を供給した後、その底部から抜き出され、再び、予熱器10に戻される。一方、熱分解器20において発生した熱分解ガスは、熱分解ガス導入管200を通って、熱分解ガス改質器40へと導入される。
Here, one
ここで、熱分解ガス改質器40へは、別途、空気又は酸素が、空気又は酸素導入管261,262から導入されて、これにより、熱分解ガスが部分燃焼され、かつ、同時にスチームが、スチーム吹込み口242から導入されて、熱分解ガスがスチームにより改質され、これにより得られた改質ガスが、改質ガス排出口230から取り出される。また、空気又は酸素及びスチームは、上記の空気又は酸素導入管261及びスチーム吹込み口242に代えて、熱分解ガス導入管200に備えられた、空気又は酸素導入管262及びスチーム吹込み口243からに導入することもできるし、全ての空気又は酸素導入管261,262及びスチーム吹込み口242,243からに導入することもできる。
Here, air or oxygen is separately introduced into the
熱分解器20の直胴部分の内径は約550mmであり、高さは約1100mmであり、内容積は約260リットルであった。また、熱分解ガス改質器40の直胴部分の内径は約600mmであり、高さは約120 0mmであり、内容積は約340リットルであった。
The inner diameter of the straight body portion of the
また、熱分解ガス導入管200は、熱分解器20側においては、熱分解器20内に形成される熱担持媒体層の上面より下方の熱分解器20の側面に備えられており、一方、熱分解ガス改質器40側においては、熱分解ガス改質器40の底面近傍の側面に備えられている。また、熱分解ガス導入管200は、重力方向に対して略水平に備えられている。該熱分解ガス導入管200としては、長さ約1000mm及び内径約80mmの配管が使用され、その内部は断熱材で被覆されて、かつ、上記突出部も該断熱材で形成されている。熱担持媒体30としては、直径(最大径)10~12mmの略球形のアルミナ製ボールを使用する。
Further, the pyrolysis
熱分解器20、並びに、予熱器10内部に、熱担持媒体30を予め夫々の容器の70%程度の高さまで充填し、次いで、該熱担持媒体30を、予熱器10において略700℃の温度に加熱する。次いで、該熱担持媒体30を、熱分解器20の頂部から200キログラム/時間の量で導入し、かつ、熱分解器20の底部から適量を抜出し、熱担持媒体30の循環を開始する。
The heat-supporting
熱担持媒体30の循環により、熱分解器20内部の気相温度及び容器自体の温度が徐々に上昇した。このような熱担持媒体30の循環を継続しながら、同時に、予熱器10の内部の熱担持媒体30の温度を800℃まで徐々に昇温する。熱担持媒体30が当該温度に達した後、更に、循環を継続して、熱分解器20内部の気相温度を徐々に上昇させ、熱分解器20の気相温度が550℃を超えるころから、バイオマス供給口220、非酸化性ガス供給口250及びスチーム吹込み口241から熱分解器20に、夫々、バイオマス原料、窒素ガス及びスチームを導入し、熱分解器20の温度が600℃になるようにコントロールする。
Due to the circulation of the heat-carrying
このとき、熱担持媒体30は、熱分解器20において、層状に堆積しており、その堆積量は、熱分解器20の内容積の約60体積%である。熱分解器20からの熱担持媒体30の抜出し量は、いずれも供給量と同一であり、熱分解器20において200キログラム/時間であった。また、抜出し時の熱担持媒体30の温度は650℃である。但し。熱分解器20からの熱担持媒体30の抜出し量は、その温度状況に応じて適宜コントロールすることも可能である。
At this time, the heat-supporting
上記の操作において、バイオマス原料としての下水汚泥を、定量フィーダーを使用して、バイオマス供給口220(図2参照)から熱分解器20に、徐々に供給量を増やしつつ、最終的に約22キログラム/時間(乾燥基準)になるように連続的に導入する。
In the above operation, the amount of sewage sludge as a biomass raw material is gradually increased from the biomass supply port 220 (see FIG. 2) to the
熱分解器20の温度は、バイオマス原料の導入に伴って徐々に低下するが、同時に、窒素ガス及び過熱蒸気を、その供給量を調節しながら熱分解器20に導入することによって、熱分解器20の温度を600℃ に保持する。また、熱分解器20内の圧力を101.3kPaに保持する。
The temperature of the
ここで、窒素ガスは、熱分解器20の上部に設けられた非酸化性ガス供給口250から、最終的に1000リットル/時間の一定量で導入される。また、スチームとしては、過熱蒸気(160℃、0.6MPa)が使用され、熱分解器20の上部に設けられたスチーム吹込み口241から、最終的に1キログラム/時間の一定量で導入される。熱分解器20におけるバイオマス原料の滞留時間は、約1時間である。これにより、熱分解器20において熱分解により生じたガスが15キログラム/時間で得られる。また、チャー及び灰が合計で6.5キログラム/時間で熱分解残渣(チャー)排出口210から排出される。
Here, nitrogen gas is finally introduced at a fixed amount of 1000 liters / hour from the non-oxidizing
熱分解器20において得られる熱分解ガスは、続いて、熱分解器20の側面下部から熱分解ガス導入管200を通過して、熱分解ガス改質器40に導入される。
The pyrolysis gas obtained in the
熱分解ガスの導入当初は、熱分解ガス改質器40内の温度は不安定になるが、熱分解ガス改質器40の下部に設けられたスチーム吹込み口242から導入される過熱蒸気の量、及び、空気又は酸素導入管261から導入される酸素の量を調節することにより、熱分解ガスを部分燃焼させて、熱分解ガス改質器40内部の温度が1000℃ になるように調節する。この時、熱分解ガス改質器40は、圧力101.3kPaに保持されている。熱分解ガス改質器40の下部に設けられたスチーム吹込み口242からの過熱蒸気は、最終的に3.7キログラム/時間の一定量で導入された。空気又は酸素導入口261からの酸素は、最終的に2.3m3-normal/時間の一定量で導入される。但し、この酸素量は熱分解ガス改質器40内部の温度上昇度合いによって、適宜増減させる。
At the beginning of the introduction of the pyrolysis gas, the temperature inside the
上記操作により、熱分解器20が温度600℃及び圧力101.3kPaに保持され、かつ、熱分解ガス改質器40が温度950℃及び圧力101.3kPaに保持される。これにより、温度1000℃の改質ガスが31キログラム/時間の量で改質ガス排出口230から得られる。
By the above operation, the
得られる改質ガスをゴム製バッグに捕集し、ガスクロマトグラフィーによりガス組成を測定する。表3には、得られる改質ガスの組成を示した。また、該操業を3日間連続して実施することができる。該操業期間中、トラブル、とりわけ、タールに起因するトラブルのない良好な連続運転を維持することができる。また、操業期間中、熱分解ガス導入管200内で熱担持媒体30がタール等により閉塞するというトラブルを生ずることもなく、熱分解器20 から熱分解ガス改質器40への熱分解ガスのスムーズな導入が維持される。また、熱分解ガス改質器40出口から取り出された改質ガス中のタール量は、約10mg/m3-normalである。
The obtained reformed gas is collected in a rubber bag, and the gas composition is measured by gas chromatography. Table 3 shows the composition of the obtained reformed gas. In addition, the operation can be carried out continuously for 3 days. During the operation period, good continuous operation can be maintained without troubles, especially troubles caused by tar. Further, during the operation period, the heat-supporting
このように改質ガスを得ることはでき、ガス化装置における熱担持媒体30の安定的な連続供給を実現することにより、熱分解器20の圧力変動を抑え、ガス分離における分離能の低下の問題を解決して、品質の安定したガスを提供することができる。
The reformed gas can be obtained in this way, and by realizing a stable continuous supply of the heat-carrying
本実施の形態のバイオマスのガス化装置は、予熱器10、熱分解器20、熱分解ガス改質器40を備え、さらに、予熱器10から熱分解器20への熱担持媒体30の供給及び熱分解器20からの熱担持媒体30の排出を制御する制御装置を組み込むことにより、ガス化装置における熱担持媒体30の安定的な連続供給を実現し、熱分解器20の圧力変動を抑え、ガス分離における分離能の低下等問題を解決して、品質の安定したガスを提供することができる。
The biomass gasifier of the present embodiment includes a
本実施の形態のバイオマスのガス化装置は、バイオマス、好ましくは、比較的灰分含有量の高いバイオマスから、水素等の有価ガスを多く含む改質ガスを発生させることができ、かつ、バイオマス中の灰に含まれる五酸化二リン及びカリ(カリウム)の揮散によって引き起こされる配管の閉塞及び腐食を予防し得るばかりではなく、N2Oの発生を抑制し得、かつ、タール及び煤塵の発生量をも低減し得ることから、今後、バイオマス、とりわけ、比較的灰分含有量の高いバイオマスのガス化装置として、大いに利用されることが期待される。 The biomass gasifier of the present embodiment can generate a reformed gas containing a large amount of valuable gas such as hydrogen from biomass, preferably biomass having a relatively high ash content, and is contained in the biomass. not only can prevent clogging and corrosion of the piping caused by the volatilization of diphosphorus pentoxide and potassium (potassium) contained in the ash, resulting suppressing the occurrence of N 2 O, and the generation amount of tar and dust It is expected that it will be widely used as a gasifier for biomass, especially biomass with a relatively high ash content, because it can be reduced.
10 予熱器
20 熱分解器
30 熱担持媒体
40 熱分解ガス改質器
50 第1バルブ
51a 第1ダンパバルブ(第1開閉部)
51b 第2ダンパバルブ(第2開閉部)
52 スイングバルブ
60 ホッパ
70 第2バルブ
72 スイングバルブ(調整部)
80 水蒸気噴霧器
91a 第1ダンパバルブ
91b 第2ダンパバルブ
91 ダンパバルブ
92 スイングバルブ
100 制御装置
10
51b 2nd damper valve (2nd opening / closing part)
52
80
Claims (9)
前記予熱器で予め加熱された熱担持媒体の供給を受け、熱担持媒体の熱によりバイオマスの熱分解を実行する熱分解器と、
熱分解により発生した熱分解ガスを、空気又は酸素により少なくとも部分的に燃焼する熱分解ガス改質器と、
前記予熱器と前記熱分解器との間に設けられ、予熱器からの熱担持媒体を熱分解器に供給するための供給機構と、
を備え、
前記供給機構は、
熱担持媒体を一時的に貯留するための開閉部と、
前記開閉部の下方に設けられ、揺動又は回転することで前記開閉部から供給された熱担持媒体を熱分解器に供給する調整部と、
を有する、バイオマスのガス化装置。 A preheater that preheats the heat-supporting medium and
A thermal decomposer that receives a supply of a heat-bearing medium preheated by the preheater and executes thermal decomposition of biomass by the heat of the heat-bearing medium.
A pyrolysis gas reformer that at least partially burns the pyrolysis gas generated by pyrolysis with air or oxygen.
A supply mechanism provided between the preheater and the pyrolyzer for supplying the heat-carrying medium from the preheater to the pyrolyzer, and
With
The supply mechanism
An opening / closing part for temporarily storing the heat-carrying medium and
An adjusting unit provided below the opening / closing unit and supplying the heat-carrying medium supplied from the opening / closing unit to the pyrolyzer by swinging or rotating.
Biomass gasifier with.
前記第2開閉部が閉状態の間に前記第1開閉部を開状態とし、前記第1開閉部が閉状態の間に前記第2開閉部を開状態とする制御装置を備えた、請求項1に記載のバイオマスのガス化装置。 The opening / closing portion has a first opening / closing portion and a second opening / closing portion provided below the first opening / closing portion.
A claim comprising a control device for opening the first opening / closing part while the second opening / closing part is closed and opening the second opening / closing part while the first opening / closing part is closed. The biomass gasification device according to 1.
前記ホッパ内の熱担持媒体の重量又は上面位置に基づいて、前記予熱器から前記熱分解器への前記熱担持媒体の供給を制御する制御装置と、
を備える、請求項1乃至3のいずれか1項に記載のバイオマスのガス化装置。 A hopper provided between the preheater and the pyrolyzer,
A control device that controls the supply of the heat-supporting medium from the preheater to the pyrolyzer based on the weight or top surface position of the heat-supporting medium in the hopper.
The biomass gasification device according to any one of claims 1 to 3, further comprising.
前記揺動部の揺動周期時間又は揺動距離を変更することで、前記熱分解器への前記熱担持媒体の供給量を制御する制御装置を備える、請求項1乃至6のいずれか1項に記載のバイオマスのガス化装置。 The adjusting part is composed of a swinging part.
Any one of claims 1 to 6, further comprising a control device for controlling the supply amount of the heat-bearing medium to the pyrolyzer by changing the swing cycle time or swing distance of the swing portion. Biomass gasifier according to.
前記制御装置が、前記回転部の回転数を変更することで、前記熱分解器への前記熱担持媒体の供給量を制御する、請求項1乃至7のいずれか1項に記載のバイオマスのガス化装置。 The adjusting part is composed of a rotating part.
The biomass gas according to any one of claims 1 to 7, wherein the control device controls the supply amount of the heat-bearing medium to the pyrolyzer by changing the rotation speed of the rotating portion. Gasification device.
前記第3バルブが開状態のときに、水蒸気を噴霧する水蒸気噴霧器と、を備える請求項1乃至8のいずれか1項に記載のバイオマスのガス化装置。
A third valve provided below the pyrolyzer and
The biomass gasification device according to any one of claims 1 to 8, further comprising a steam sprayer that sprays steam when the third valve is in the open state.
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| JP2020080395A JP2023085579A (en) | 2020-04-30 | 2020-04-30 | Biomass gasification device |
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|---|---|---|---|---|
| GB2615574A (en) * | 2022-02-11 | 2023-08-16 | Wild Hydrogen Ltd | Method and apparatus for gasification of biogenic material |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5499103A (en) * | 1977-09-19 | 1979-08-04 | Schingnitz Manfred | High pressure vaporization of powder fuel and apparatus therefor |
| JP2012201770A (en) * | 2011-03-24 | 2012-10-22 | Raito Kogyo Co Ltd | Organic matter gasification system and method for dissolving thermal decomposer differential pressure therein |
| WO2019065851A1 (en) * | 2017-09-29 | 2019-04-04 | 株式会社ジャパンブルーエナジー | Biomass gasification device |
| WO2020008622A1 (en) * | 2018-07-06 | 2020-01-09 | 株式会社 翼エンジニアリングサービス | Method for producing hydrogen using biomass as raw material |
-
2020
- 2020-04-30 JP JP2020080395A patent/JP2023085579A/en active Pending
-
2021
- 2021-04-30 WO PCT/JP2021/017234 patent/WO2021221163A1/en not_active Ceased
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5499103A (en) * | 1977-09-19 | 1979-08-04 | Schingnitz Manfred | High pressure vaporization of powder fuel and apparatus therefor |
| JP2012201770A (en) * | 2011-03-24 | 2012-10-22 | Raito Kogyo Co Ltd | Organic matter gasification system and method for dissolving thermal decomposer differential pressure therein |
| WO2019065851A1 (en) * | 2017-09-29 | 2019-04-04 | 株式会社ジャパンブルーエナジー | Biomass gasification device |
| WO2020008622A1 (en) * | 2018-07-06 | 2020-01-09 | 株式会社 翼エンジニアリングサービス | Method for producing hydrogen using biomass as raw material |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2615574A (en) * | 2022-02-11 | 2023-08-16 | Wild Hydrogen Ltd | Method and apparatus for gasification of biogenic material |
| GB2615574B (en) * | 2022-02-11 | 2024-11-27 | Wild Hydrogen Ltd | Method and apparatus for gasification of biogenic material |
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