WO2017175737A1 - Cooling apparatus for carbonized biomass - Google Patents
Cooling apparatus for carbonized biomass Download PDFInfo
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- WO2017175737A1 WO2017175737A1 PCT/JP2017/014002 JP2017014002W WO2017175737A1 WO 2017175737 A1 WO2017175737 A1 WO 2017175737A1 JP 2017014002 W JP2017014002 W JP 2017014002W WO 2017175737 A1 WO2017175737 A1 WO 2017175737A1
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- biomass
- solid fuel
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B39/00—Cooling or quenching coke
- C10B39/04—Wet quenching
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B39/00—Cooling or quenching coke
- C10B39/16—Cooling or quenching coke combined with sorting
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B45/00—Other details
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
- C10B53/02—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of cellulose-containing material
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
- C10B53/08—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form in the form of briquettes, lumps and the like
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/40—Solid fuels essentially based on materials of non-mineral origin
- C10L5/44—Solid fuels essentially based on materials of non-mineral origin on vegetable substances
- C10L5/442—Wood or forestry waste
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L9/00—Treating solid fuels to improve their combustion
- C10L9/08—Treating solid fuels to improve their combustion by heat treatments, e.g. calcining
- C10L9/086—Hydrothermal carbonization
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F25—REFRIGERATION OR COOLING; COMBINED HEATING AND REFRIGERATION SYSTEMS; HEAT PUMP SYSTEMS; MANUFACTURE OR STORAGE OF ICE; LIQUEFACTION SOLIDIFICATION OF GASES
- F25D—REFRIGERATORS; COLD ROOMS; ICE-BOXES; COOLING OR FREEZING APPARATUS NOT OTHERWISE PROVIDED FOR
- F25D7/00—Devices using evaporation effects without recovery of the vapour
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2200/00—Components of fuel compositions
- C10L2200/04—Organic compounds
- C10L2200/0461—Fractions defined by their origin
- C10L2200/0469—Renewables or materials of biological origin
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/02—Combustion or pyrolysis
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/06—Heat exchange, direct or indirect
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/18—Spraying or sprinkling
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/32—Molding or moulds
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/02—Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
- C10L5/34—Other details of the shaped fuels, e.g. briquettes
- C10L5/36—Shape
- C10L5/361—Briquettes
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Definitions
- the present invention relates to a biomass carbide cooling device.
- Patent Document 1 biocoke having excellent strength is obtained by semi-carbonizing by pulverizing biomass under pressure while heating.
- Patent Document 1 has a problem that the cooling efficiency is low because it is cooled in a pressurized state after molding and is naturally cooled by the atmosphere. Even if cooling by water cooling is performed to improve the cooling efficiency, water cooling in a pressurized state is difficult, and bio coke is biomass formed after pulverization, so that a part thereof is pulverized and handling becomes difficult. In particular, in the unsteady state where heating is not performed, the molded bio-coke may collapse and the equipment may be blocked. Or, for simplification, when carbonized (heated) and then cooled in a water tank or the like, the biomass solid fuel floats because of its low specific gravity, and the recovery becomes complicated.
- the present invention has been made in order to solve the above-mentioned problems, and an object of the present invention is to reduce equipment blockage while improving the efficiency of cooling a semi-carbonized biomass molded body.
- a carbonization furnace for carbonizing a biomass molded body to obtain a biomass carbide provided on the downstream side of the carbonization furnace, classifying means for classifying the biomass carbide, provided on the downstream side of the classification means, and classified Cooling means for cooling the biomass carbide
- the biomass molded body is a molded body obtained by pulverizing raw material biomass and then molding, wherein the cooling means sprays the biomass carbide by watering. It is characterized by cooling.
- the present invention is to reduce equipment blockage while improving the efficiency of cooling a semi-carbonized biomass molded body.
- FIG. 26A is a schematic diagram of the present invention
- FIG. 27 is a process flow.
- the biomass solid fuel obtained by the fuel production process 100 of FIG. 27 becomes a product through the classification process 200 and the cooling process 300.
- a biomass solid fuel is produced using a known method.
- the raw material biomass is subjected to the crushing and crushing step 110 and then molded in the molding step 120, and then heated in the heating step 130 using the kiln 1 of FIG. 26A.
- a binder such as a binder is not added, and the molding is simply performed by compressing and pressurizing the biomass powder.
- An unheated biomass molded body (White Pellet: hereinafter referred to as WP) immediately after the molding step 120 is low in strength because it is simply pressure-molded biomass powder, and is easily pulverized during handling. Moreover, it expands and collapses due to water absorption.
- the biomass molded body is heated (low-temperature carbonization) at 150 to 400 ° C. in the heating process 130 (kiln 1), so that the shape and shape of the molded body are maintained, while maintaining strength and water resistance.
- a biomass solid fuel (Pelletizing Before Torrefaction: hereinafter referred to as PBT) is produced. Details of the fuel manufacturing process 100 will be described later.
- the classification process 200 and the cooling process 300 are performed using the vibration conveyor 2 of FIG. 26A.
- the vibration conveyor 2 is divided into two sections by a partition plate 24, and becomes a classification unit 21 and a cooling unit 22, respectively.
- the PBT discharged from the kiln 1 is transported by the vibration of the flat plate 22b and the PBT sequentially supplied from the kiln 1, and is discharged as a product through the classification unit 21 and the cooling unit 22.
- the vibration conveyor 2 of FIG. 26A is inclined, the horizontal conveyor which does not incline may be sufficient.
- the PBT and the fine powder are classified (classifying step 200) by vibrating the PBT on the sieve 21a.
- the cooling unit 22 has a sprinkler 22a and a vibrating flat plate 22b, and the sprinkler 22a sprinkles water on the flat plate 22b.
- Cooling (cooling process 300) is performed by spraying water on the PBT on the flat plate 22b and discharged as a product.
- the cooling may be only watering, or an air nozzle or the like may be provided in addition to the watering part 22a and air cooling may be used in combination. Further, the watering nozzle may be a two-fluid nozzle of air + water.
- the flat plate 22b is a smooth plate having no holes or irregularities, and a metal plate or a resin plate is used. By using a smooth plate, the PBT in the cooling unit 22 becomes slippery, and the movement in the cooling unit 22 becomes smooth.
- the classification unit 21 and the cooling unit 22 are separated by the partition plate 24, the water that has sprinkled into the cooling unit 22 is reduced from entering the classification unit 21. Thereby, the water absorption of the fine powder classified in the classification part 21 is suppressed, and the obstruction
- thermometer 11 is provided at the exit of the kiln 1, and the control unit 30 executes or stops watering based on the measured temperature.
- the thermometer 11 may be at any other position as long as the temperature of the kiln 1 can be measured.
- PBT having strength and water resistance is obtained only by heating WP with kiln 1, but when the temperature of kiln 1 is below a predetermined value, unheated WP or heating is not performed. Since it is insufficient, a biomass molded body in which strength and water resistance are not ensured is discharged from the kiln 1.
- the water sprinkling unit 22 expands and collapses due to water absorption due to insufficient water resistance, causing equipment blockage.
- the controller 30 determines that the temperature is insufficient for PBT production and stops the watering of the watering part 22a. Therefore, even if it is a case where WP and PBT with insufficient heating are discharged when the temperature of the kiln 1 is low, collapse in the sprinkling part 22 can be suppressed and equipment blockage can be reduced.
- FIG. 28 is a flowchart for continuing / stopping watering based on temperature, and is executed by the control unit 30.
- step S1 the kiln 1 outlet temperature T is measured by the thermometer 11.
- step S2 it is determined whether or not the measured temperature T is equal to or lower than a predetermined value ⁇ . If YES, the watering is stopped in step S3, and if NO, the watering is executed in step S4.
- the WP in the kiln 1 is stopped when the kiln 1 is stopped and the temperature becomes lower than a predetermined value, the WP remains in the kiln 1. In this case, even if the temperature is low, carbonization of WP proceeds and a large amount of pyrolysis gas is generated, which is complicated because a separate gas treatment is required. Moreover, excessively carbonized WP has a small residual amount of volatile matter and is disadvantageous as a fuel, and this also needs to be treated separately, which further increases man-hours. Therefore, the conveyance stop in the kiln 1 is not preferable.
- the thermometer 11 directly measures the temperature of the PBT at the kiln 1 outlet, not the atmosphere temperature at the kiln 1 outlet.
- PBT solid fuel
- PBT solid fuel
- the thermometer 11 only needs to be able to directly measure the temperature of the PBT at the outlet of the kiln 1, and may be a contact thermometer or a non-contact thermometer such as an infrared ray.
- a kiln 1 carbonization furnace that carbonizes a biomass molded body to obtain biomass carbide (PBT), and a classification unit 21 (classification means) that is provided downstream of the kiln 1 and classifies biomass carbide (PBT).
- a cooling unit 22 cooling means that is provided downstream of the classification unit 21 and cools the classified biomass carbide (PBT).
- the biomass molded body was a molded body obtained by pulverizing the raw material biomass and then molded, and the cooling unit 22 cooled the biomass carbide (PBT) by watering.
- biomass carbide When the biomass carbide is cooled by immersion in water, it is difficult to handle because the biomass carbide floats on the water and diffuses into the water surface. On the other hand, even in the case of cooling by watering, the molded biomass is easily pulverized because it forms a pulverized product. If watered as it is, biomass powder may absorb water and the equipment may be blocked. Therefore, blockage can be avoided by watering after classification.
- air cooling and watering may be used in combination, or a two-fluid nozzle of air + water may be used.
- the cooling unit 22 includes a vibrating flat plate 22b (flat plate) and a sprinkling unit 22a that sprinkles water on the flat plate 22b.
- the flat plate 22b is a metal plate or a resin plate, and biomass carbide ( PBT) was transported.
- Biomass carbide partially collapses during transportation, so that a small amount of biomass carbide remains after classification. Smaller diameters are more likely to adhere to each other by watering, and handling during transportation tends to be complicated.
- the biomass carbide sprayed by the resistance of the irregularities of the net accumulates, and the conveyance becomes inefficient and there is a risk of blockage. Therefore, by using a metal plate or a resin plate having a low sliding resistance with the biomass carbide, it is possible to reduce the resistance during conveyance and perform efficient conveyance.
- a control unit 30 (control means) is provided to stop watering of the watering unit 22a.
- the kiln 1 In the unsteady state such as when starting and stopping, the kiln 1 is at a low temperature below a predetermined value (low temperature that is insufficient for PBT production), so that unmolded biomass (WP) or carbonization is insufficient and strength and water resistance Biomass compacts that are inferior in properties are discharged, but they swell and collapse due to watering, and there is a risk of equipment blockage. Therefore, watering can be stopped and blockage can be prevented.
- WP unmolded biomass
- thermometer 11 is capable of directly measuring the temperature of biomass carbide (PBT).
- PBT solid fuel
- PBT solid fuel
- WP water resistance
- strength can be obtained by carbonizing WP at a predetermined temperature or higher, while excessive carbonization deteriorates the calorie yield. Therefore, by directly measuring the temperature of the PBT, it becomes possible to perform carbonization with high accuracy, and it is possible to obtain water resistance and strength while ensuring a heat yield.
- a separation part 24 that separates the classification part 22 and the cooling part 23 was provided. By separating these, water intrusion into the classification unit 22 can be reduced, and accumulation and blockage during classification can be suppressed.
- a classification process and a cooling process may be performed using a system as shown in FIG. 26B.
- This system 402 includes a vibration sieve device 403A and a cooling vibration conveyor 403B.
- the vibration sieve device 403A and the cooling vibration conveyor 403B are configured separately, and the vibration sieve device 403A is arranged on the upstream side in the PBT transport direction, and the cooling vibration conveyor 403B is arranged on the downstream side. Note that the description of the functions and structures common to the configuration in FIG. 26A will be omitted to avoid redundant description.
- the vibration sieve device 403A has a classification unit 421 provided with a sieve 421a.
- PBT is supplied from a rotary kiln (not shown in FIG. 26B) as in the configuration of FIG. 26A.
- the PBT is conveyed while being vibrated on the sieve 421a, whereby the PBT and fine powder are classified (classifying step).
- the vibration sieve device 403A in the figure is inclined, it may be a horizontal one that does not incline.
- the size of the screen 421a may be appropriately changed according to a desired value. Those that have collapsed during manufacture or small PBT that do not reach a predetermined size fall under this sieve 421a and are processed separately. The PBT remaining on the sieve 421a is discharged from the discharge portion 421b of the vibration sieve device 403A.
- the cooling vibration conveyor 403B has a cooling unit 422 provided with a sprinkling unit 422a, a vibrating flat plate 422b, and the like, and PBT from the vibration sieve device 403A is supplied onto the flat plate 422b.
- the cooling vibration conveyor 403B also includes a control unit that controls the operation of the watering unit 422a and the like, as in the configuration of FIG. 26A.
- the flat plate 422b is a smooth plate having no holes or irregularities, and a metal plate or a resin plate is used. By using a smooth plate, the PBT becomes slippery and the movement is smooth.
- the cooling vibration conveyor 403B in the figure is inclined, it may be a horizontal one that is not inclined.
- cooling may be only watering or air cooling may be used in combination.
- the watering nozzle may be a two-fluid nozzle of air + water.
- Biomass solid fuel is a molding obtained by crushing biomass after crushing, compressing and molding biomass that has become scrap or powder to form a lump, and a heating process that heats the lump after the forming process Spent solids are used as fuel (corresponding to PBT described later). Since this biomass solid fuel does not require a steam explosion process and a binder, an increase in cost can be suppressed.
- the block obtained by the molding process and before the heating step is also referred to as “unheated block”. This unheated lump corresponds to the above-mentioned WP.
- the biomass used as a raw material may be woody or grassy, and the tree species and parts are not particularly limited.
- examples include bark, walnut shell, sago palm, EFB (empty fruit bunch of palm oil processing residue), meranti, rubber tree and the like, and may be one kind or a mixture of two or more kinds.
- a block is formed using a known molding technique.
- the lump is preferably a pellet or briquette and can be of any size.
- the heating step the molded lump is heated.
- the biomass solid fuel obtained after the heating step preferably has an immersion water COD (chemical oxygen demand) of 3000 ppm or less when immersed in water.
- the biomass solid fuel preferably has a COD ratio represented by (COD of biomass solid fuel after heating step / COD of unheated biomass solid fuel) of 0.98 or less.
- COD chemical oxygen demand
- COD chemical oxygen demand of immersion water when biomass solid fuel is immersed in water
- COD refers to the preparation of an immersion water sample for COD measurement in 1973. This is the COD value analyzed according to JIS K0102 (2010) -17, in accordance with the Agency Notification No. 13 (b) Method for testing metals contained in industrial waste.
- the biomass solid fuel obtained after the heating step preferably has a grindability index (HGI) based on JIS M 8801 of 15 or more and 60 or less, and more preferably 20 or more and 60 or less.
- HGI grindability index
- the BET specific surface area is preferably from 0.15 to 0.8 m 2 / g, more preferably from 0.15 to 0.7 m 2 / g.
- the equilibrium moisture after immersion in water is preferably 15 to 65 wt%, and more preferably 15 to 60 wt%.
- Biomass solid fuel has a fuel ratio (fixed carbon / volatile content) of 0.2 to 0.8, an anhydrous base high calorific value of 4800 to 7000 (kcal / kg), and a molar ratio O / C of oxygen O to carbon C.
- the molar ratio H / C of hydrogen H to carbon C is 0.8 to 1.3.
- the biomass solid fuel can be obtained, for example, by adjusting the species of biomass used as a raw material, its part, the heating temperature in the heating step, and the like.
- the industrial analysis values, elemental analysis values, and higher calorific values in this specification are based on JIS M 8812, 8813, and 8814.
- the method for producing a biomass solid fuel includes a molding step of forming biomass powder of crushed and pulverized biomass to obtain an unheated lump, and a heating step of heating the unheated lump to obtain a heated solid.
- the heating temperature in the heating step is preferably 150 ° C. to 400 ° C. By setting the temperature of the heating step within this range, a biomass solid fuel having the above characteristics can be obtained.
- the heating temperature is appropriately determined depending on the shape and size of the biomass as a raw material and the lump, but is preferably 150 to 400 ° C, more preferably 200 to 350 ° C. More preferably, it is 230 to 300 ° C. More preferably, it is 250 to 290 ° C.
- the heating time in the heating step is not particularly limited, but is preferably 0.2 to 3 hours.
- the particle size of the biomass powder is not particularly limited, but is about 100 to 3000 ⁇ m on average, preferably 400 to 1000 ⁇ m on average.
- the measuring method of the particle size of biomass powder may use a well-known measuring method. As will be described later, in biomass solid fuel (PBT), the connection or adhesion between biomass powders is maintained by solid crosslinking, so the particle size of biomass powders is not particularly limited as long as it can be molded. In addition, since the fine pulverization causes a cost increase, a known range may be used as long as the particle size is in a range where both cost and moldability are compatible.
- B / A 0.7 to 1 where A is the bulk density of the unheated mass before the heating step and B is the bulk density of the heated solid after the heating step.
- the value of the bulk density A is not particularly limited as long as it is a known range in which biomass powder is molded to obtain an unheated lump. Moreover, since the bulk density changes depending on the type of raw material biomass, it may be set as appropriate.
- H2 / H1 1.1 to 2.5, where HGI of the unheated mass (hard glove grindability index of JIS M8801) is H1, and HGI of the heated solid is H2.
- the characteristics of the biomass solid fuel may be determined within a suitable range depending on the species of biomass used as a raw material.
- One example will be described below, but the present invention is not limited to these tree species and combinations thereof.
- preferable ranges are shown for the types of biomass raw materials used in the present invention, the properties of the obtained solid fuel (corresponding to PBT described later), and the production method thereof.
- COD is preferably 1000 ppm or less, more preferably 900 ppm or less, further preferably 800 ppm or less, and the COD ratio is preferably 0.80 or less, more preferably 0.70 or less, and even more preferably 0.68 or less.
- the equilibrium moisture after immersion in water is preferably 15 wt% to 45 wt%, more preferably 18 wt% to 35 wt%, and further preferably 18 wt% to 32 wt%.
- the BET specific surface area is 0.25m 2 /g ⁇ 0.8m 2 / g, more preferably 0.28m 2 /g ⁇ 0.6m 2 / g, 0.32m 2 / g ⁇ More preferably, it is 0.5 m 2 / g.
- HGI is preferably 20 to 60, more preferably 20 to 55, and still more preferably 22 to 55.
- the HGI of coal (bituminous coal) suitable as a boiler fuel for power generation is around 50, and the closer to around 50 is preferable, considering that it is mixed and ground with coal.
- the HGI ratio (described later) is preferably 1.0 to 2.5.
- the fuel ratio is preferably 0.2 to 0.8, more preferably 0.2 to 0.7, and still more preferably 0.2 to 0.65.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 4900 to 7000 kcal / kg, and further preferably 4950 to 7000 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.1 to 0.62, more preferably 0.1 to 0.61, and further preferably 0.1 to 0.60.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.8 to 1.3, more preferably 0.85 to 1.3, and even more preferably 0.9 to 1.3.
- the heating temperature in the heating step is preferably 200 to 350 ° C, more preferably 210 to 330 ° C, and further preferably 220 to 300 ° C.
- solid fuel B a biomass solid fuel (hereinafter sometimes referred to as solid fuel B) when the raw material is European red pine are as follows.
- COD is preferably 900 ppm or less, more preferably 800 ppm or less, further preferably 700 ppm or less, and the COD ratio is preferably 0.75 or less, more preferably 0.68 or less, and even more preferably 0.64 or less.
- the equilibrium moisture after immersion in water is preferably 15 wt% to 45 wt%, more preferably 18 wt% to 40 wt%, and even more preferably 18 wt% to 31 wt%.
- the BET specific surface area is 0.30m 2 /g ⁇ 0.7m 2 / g, more preferably 0.30m 2 /g ⁇ 0.6m 2 / g, 0.30m 2 / g ⁇ More preferably, it is 0.5 m 2 / g.
- HGI is preferably 25 to 60, more preferably 30 to 55, and even more preferably 35 to 55.
- the HGI ratio (described later) is preferably 1.0 to 2.5.
- the fuel ratio is preferably 0.2 to 0.8, more preferably 0.2 to 0.7, and still more preferably 0.2 to 0.65.
- the anhydrous base high calorific value is preferably 4950 to 7000 kcal / kg, more preferably 5000 to 7000 kcal / kg, and further preferably 5100 to 7000 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.1 to 0.60, more preferably 0.2 to 0.60, and still more preferably 0.3 to 0.60.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.8 to 1.3, more preferably 0.85 to 1.3, and even more preferably 0.9 to 1.3.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 240 to 290 ° C.
- solid fuel C As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel C) when the raw material is an almond old tree are as follows.
- COD is preferably 2100 ppm or less, more preferably 2000 ppm or less, further preferably 1500 ppm or less, and the COD ratio is preferably 0.80 or less, more preferably 0.75 or less, and further preferably 0.55 or less.
- the equilibrium moisture after immersion in water is preferably 25 wt% to 60 wt%, more preferably 30 wt% to 50 wt%, and even more preferably 30 wt% to 45 wt%.
- the BET specific surface area is 0.20m 2 /g ⁇ 0.70m 2 / g, more preferably 0.22m 2 /g ⁇ 0.65m 2 / g, 0.25m 2 / g ⁇ More preferably, it is 0.60 m 2 / g.
- HGI is preferably 15 to 60, more preferably 18 to 55, and still more preferably 20 to 55.
- the HGI ratio (described later) is preferably 1.0 to 2.0.
- the fuel ratio is preferably 0.2 to 0.8, more preferably 0.25 to 0.7, and further preferably 0.30 to 0.65.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 4800 to 6500 kcal / kg, and further preferably 4900 to 6500 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.10 to 0.70, more preferably 0.20 to 0.60, and still more preferably 0.30 to 0.60.
- the molar ratio H / C of hydrogen H to carbon C is preferably 0.8 to 1.3, more preferably 0.85 to 1.3, and still more preferably 0.9 to 1.20.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 240 to 290 ° C.
- solid fuel D A mixture of almond shells and old almond wood: solid fuel D
- the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel D) when the raw material is a mixture of almond shells and almond old wood are as follows.
- COD is preferably 2500 ppm or less, more preferably 2000 ppm or less, further preferably 1500 ppm or less, and the COD ratio is preferably 0.75 or less, more preferably 0.68 or less, and further preferably 0.50 or less.
- the equilibrium moisture after immersion in water is preferably 15 wt% to 50 wt%, more preferably 20 wt% to 40 wt%, and even more preferably 20 wt% to 35 wt%.
- the BET specific surface area is 0.20m 2 /g ⁇ 0.70m 2 / g, more preferably 0.27m 2 /g ⁇ 0.70m 2 / g, 0.30m 2 / g ⁇ More preferably, it is 0.60 m 2 / g.
- HGI is preferably 20 to 60, more preferably 20 to 55, and still more preferably 23 to 55.
- the HGI ratio (described later) is preferably 1.0 to 2.0.
- the fuel ratio is preferably 0.2 to 0.8, more preferably 0.30 to 0.7, and still more preferably 0.35 to 0.65.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 4800 to 6500 kcal / kg, and further preferably 4900 to 6300 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.10 to 0.70, more preferably 0.20 to 0.60, and still more preferably 0.30 to 0.55.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.8 to 1.3, more preferably 0.8 to 1.25, and even more preferably 0.85 to 1.20.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 240 to 290 ° C.
- Solid Fuel E As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel E) when the raw material is an acacia xylem are as follows.
- COD is preferably 950 ppm or less, more preferably 850 ppm or less, further preferably 800 ppm or less, and the COD ratio is preferably 0.95 or less, more preferably 0.85 or less, and even more preferably 0.80 or less.
- the equilibrium moisture after immersion in water is preferably 20 wt% to 60 wt%, more preferably 20 wt% to 55 wt%, and even more preferably 23 wt% to 53 wt%.
- the BET specific surface area is 0.40m 2 /g ⁇ 0.70m 2 / g, more preferably 0.50m 2 /g ⁇ 0.70m 2 / g, 0.55m 2 / g ⁇ More preferably, it is 0.70 m 2 / g.
- the fuel ratio is preferably 0.2 to 0.6, more preferably 0.2 to 0.5, and still more preferably 0.2 to 0.4.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 4800 to 6000 kcal / kg, and further preferably 4800 to 5500 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.40 to 0.70, more preferably 0.45 to 0.70, and still more preferably 0.48 to 0.65.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.8 to 1.3, more preferably 1.0 to 1.3, and even more preferably 1.1 to 1.3.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 240 to 290 ° C.
- COD is preferably 2500 ppm or less, more preferably 2000 ppm or less, further preferably 1200 ppm or less, and the COD ratio is preferably 0.30 or less, more preferably 0.20 or less, and further preferably 0.15 or less.
- the equilibrium moisture after immersion in water is preferably 15 wt% to 50 wt%, more preferably 20 wt% to 45 wt%, and even more preferably 25 wt% to 40 wt%.
- the BET specific surface area is 0.35m 2 /g ⁇ 0.55m 2 / g, more preferably 0.40m 2 /g ⁇ 0.55m 2 / g, 0.40m 2 / g ⁇ More preferably, it is 0.50 m 2 / g.
- the fuel ratio is preferably 0.4 to 0.8, more preferably 0.42 to 0.75, and still more preferably 0.45 to 0.75.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 5000 to 7000 kcal / kg, and further preferably 5200 to 6500 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.25 to 0.60, more preferably 0.30 to 0.60, and still more preferably 0.30 to 0.55.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.8 to 1.3, more preferably 0.8 to 1.2, and still more preferably 0.9 to 1.2.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 240 to 290 ° C.
- solid fuel G (Almond shell and walnut shell mixture: solid fuel G)
- the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel G) when the raw material is a mixture of almond shells and walnut shells are as follows.
- COD is preferably 2500 ppm or less, more preferably 2100 ppm or less, further preferably 1500 ppm or less, and the COD ratio is preferably 0.65 or less, more preferably 0.55 or less, and further preferably 0.45 or less.
- the equilibrium moisture after immersion in water is preferably 20 wt% to 45 wt%, more preferably 20 wt% to 40 wt%, and even more preferably 25 wt% to 35 wt%.
- the BET specific surface area is 0.15m 2 /g ⁇ 0.35m 2 / g, more preferably 0.19m 2 /g ⁇ 0.33m 2 / g, 0.20m 2 / g ⁇ More preferably, it is 0.30 m 2 / g.
- the HGI is preferably 18 to 60, more preferably 20 to 60.
- the HGI ratio is preferably 1.0 or more.
- the fuel ratio is preferably 0.2 to 0.7, more preferably 0.25 to 0.65, and further preferably 0.28 to 0.60.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 4800 to 6000 kcal / kg, and further preferably 5000 to 6000 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.30 to 0.65, more preferably 0.40 to 0.70, and still more preferably 0.40 to 0.60.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.8 to 1.3, more preferably 0.9 to 1.25, and even more preferably 0.9 to 1.2.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 240 to 290 ° C.
- Solid fuel H As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel H) when the raw material is sago palm are as follows.
- COD is preferably 2000 ppm or less, more preferably 1600 ppm or less, further preferably 800 ppm or less, and the COD ratio is preferably 0.85 or less, more preferably 0.60 or less, and further preferably 0.4 or less.
- the equilibrium moisture after immersion in water is preferably 20 wt% to 35 wt%, more preferably 20 wt% to 33 wt%, and even more preferably 22 wt% to 30 wt%.
- the BET specific surface area is 0.15m 2 /g ⁇ 0.35m 2 / g, more preferably 0.18m 2 /g ⁇ 0.33m 2 / g, 0.18m 2 / g ⁇ More preferably, it is 0.30 m 2 / g.
- the HGI is preferably 20 to 60, more preferably 25 to 55, and even more preferably 30 to 55.
- the HGI ratio is preferably 1.0 to 2.5, more preferably 1.3 to 2.3, and still more preferably 1.5 to 2.2.
- the fuel ratio is preferably 0.2 to 0.8, more preferably 0.25 to 0.8, and even more preferably 0.5 to 0.8.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 4900 to 6500 kcal / kg, and further preferably 5000 to 6000 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.20 to 0.65, more preferably 0.20 to 0.60, and still more preferably 0.2 to 0.55.
- the molar ratio H / C of hydrogen H to carbon C is preferably 0.8 to 1.3, more preferably 0.85 to 1.3, and still more preferably 0.85 to 1.2.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 240 to 290 ° C.
- EFB Solid Fuel I
- solid fuel I the properties of biomass solid fuel (hereinafter sometimes referred to as solid fuel I) when the raw material is EFB (empty fruit bunch of palm oil processing residue) are as follows.
- COD is preferably 2350 ppm or less, more preferably 2300 ppm or less, further preferably 2000 ppm or less, and the COD ratio is preferably 0.98 or less, more preferably 0.96 or less, and further preferably 0.85 or less.
- the equilibrium moisture after immersion in water is preferably 23 wt% to 45 wt%, more preferably 20 wt% to 40 wt%, and even more preferably 20 wt% to 35 wt%.
- the BET specific surface area is 0.25m 2 /g ⁇ 0.65m 2 / g, more preferably 0.30m 2 /g ⁇ 0.60m 2 / g, 0.35m 2 / g ⁇ More preferably, it is 0.55 m 2 / g.
- the fuel ratio is preferably 0.25 to 0.8, more preferably 0.30 to 0.8, and still more preferably 0.36 to 0.8.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 4900 to 7000 kcal / kg, and further preferably 5000 to 7000 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.15 to 0.65, more preferably 0.15 to 0.60, and still more preferably 0.15 to 0.55.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.5 to 1.3, more preferably 0.55 to 1.3, and even more preferably 0.6 to 1.2.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 240 to 260 ° C.
- Solid fuel J As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel J) when the raw material is meranti are as follows.
- COD is preferably 330 ppm or less, more preferably 320 ppm or less, further preferably 300 ppm or less, and the COD ratio is preferably 0.98 or less, more preferably 0.95 or less, and even more preferably 0.90 or less.
- the equilibrium moisture after immersion in water is preferably 15 wt% to 30 wt%, more preferably 15 wt% to 27 wt%, and even more preferably 18 wt% to 25 wt%.
- the fuel ratio is preferably 0.2 to 0.6, more preferably 0.2 to 0.5, and further preferably 0.2 to 0.45.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg, more preferably 4800 to 6500 kcal / kg, and further preferably 4800 to 6000 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.3 to 0.60, more preferably 0.35 to 0.60, and still more preferably 0.40 to 0.60.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.9 to 1.2, more preferably 0.95 to 1.2, and even more preferably 1.0 to 1.2.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 230 to 290 ° C.
- the fuel ratio is preferably 0.2 to 0.8, more preferably 0.2 to 0.7.
- the anhydrous base high calorific value is preferably 4800 to 7000 kcal / kg.
- the molar ratio O / C of oxygen O to carbon C is preferably 0.1 to 0.7.
- the molar ratio H / C between hydrogen H and carbon C is preferably 0.8 to 1.3.
- the heating temperature in the heating step is preferably 200 to 350 ° C., more preferably 220 to 300 ° C., and further preferably 230 to 290 ° C.
- the present inventors in the order of the process of performing the heating process of heating the unheated lump after the molding process, the components derived from biomass that is the raw material without using a binder. It is speculated that a biomass solid fuel with high water resistance can be produced that is used to maintain the connection or adhesion between biomass powders and does not collapse even when immersed in water. As a result of the analysis by the present inventors, the following knowledge about the mechanism by which the biomass solid fuel acquires water resistance was obtained.
- the present inventors have prepared three types of biomass solid fuels having different production methods, specifically, unheated solid fuel obtained by molding pulverized biomass (White Pellet: hereinafter sometimes referred to as WP), and pulverization.
- the solid fuel (Pelletizing Before Torrefaction: hereinafter sometimes referred to as PBT) obtained by molding and heating the formed biomass is subjected to FT-IR analysis, GC-MS analysis, SEM observation, etc. The mechanism of water resistance of the fuel was analyzed. Note that no binder is used in either WP or PBT.
- abietic acid etc. terpenes such as abietic acid and its derivatives
- FIG. 18 is a diagram showing a mechanism (estimation) of solid bridge development in PBT.
- biomass powder in which the liquid due to melting of abietic acid is pulverized as the temperature rises (consolidated by molding after pulverization, Elution into the gap between adjacent biomass powders, evaporation of abietic acid and thermal decomposition occur, and the hydrophobic substance adheres to the gap between the biomass powders to develop crosslinking (solid crosslinking).
- attachment of biomass powder is maintained by the abietic acid derived from the biomass etc. which are raw materials, without adding a binder. Therefore, it is considered that the biomass powders are connected or adhered to each other to suppress water entry and improve water resistance.
- Abietic acid or a derivative thereof has a melting point of about 139 to 142 ° C and a boiling point of about 250 ° C. Therefore, it is inferred that heating causes abietic acid or the like to melt near the melting point to cause liquid crosslinking, and abietic acid or the like thermally decomposes near the boiling point to develop solid crosslinking.
- Terpenes such as abietic acid are generally contained in biomass (Hokkaido Prefectural Forest Products Experiment Station Monthly Report No. 171, April 1966, Japan Wood Conservation Society “Wood Preservation” Vol. 34-2 (2008), etc.) . Although there is a slight difference in content depending on the type of biomass ("Use of essential oil", Oohiro Goro, Report of the 6th Research Subcommittee of the Japan Wood Society, Table 1, Table 1 of the Japan Wood Society 1999), etc. ⁇ Example A> to ⁇ In all of Examples I>, since water resistance (not disintegrated even after immersion in water, see Table 6) is exhibited by heating at 230 ° C. or higher, water resistance is generally increased by heating at least 230 ° C. to 250 ° C. for biomass in general. It is considered to be granted.
- FIG. 19 to 22 are diagrams showing the results of FT-IR analysis of biomass solid fuel.
- the raw material was European red pine of Example B below, which was obtained by analyzing a solid fuel (PBT) obtained by heating at 250 ° C., which was formed into a pellet after pulverization. The same raw material is pulverized and unheated after molding (WP) is also shown.
- PBT solid fuel
- WP unheated after molding
- the amount of COOH groups is WP> PBT
- the amount of C ⁇ C bonds is PBT> WP.
- the COOH group elution amount in the acetone extract (FIG. 21) is WP> PBT, indicating that PBT has few hydrophilic COOH groups.
- PBT has more C ⁇ C bonds than WP. Therefore, it turns out that PBT is excellent in water resistance.
- FIG. 23 is a diagram showing the results of GC-MS analysis of an acetone extract.
- the raw material is the European red pine of Example B as in FIGS. 19 to 22 above, and the solid fuel (PBT) heated at 250 ° C. after being crushed and formed into pellets and unheated (WP) are used. It was.
- PBT solid fuel
- the amount of elution of abietic acid, which is a kind of terpene, into acetone is less than that of WP, and abietic acid is melted by heating to form a liquid bridge, and then volatilization of abietic acid, etc. This is considered to indicate that a solid bridge is formed.
- PBT also improves the strength of solid fuel due to the development of solid cross-linking, and has good grindability without adding a binder by heating at least 230 ° C to 250 ° C as well as water resistance (HGI, grinding speed described later). And it is inferred that good handling properties (a pulverization test described later) can be obtained. Furthermore, as described above, COD is reduced in PBT. This is because the tar content of the biomass raw material is volatilized by heating, and at the same time, the solid fuel surface of PBT is covered with solidified abietic acid, and the solid fuel surface is hydrophobic. This is considered to be because the elution of tar remaining in the biomass raw material is suppressed.
- Example A (Examples A-1 to A-6)
- the biomass was crushed and then pulverized, and a biomass solid fuel A (PBT) was obtained through a molding process for molding the pulverized biomass and a subsequent heating process.
- No binder is used in any step.
- a raw material biomass a mixture of 40% by weight of rice pine, 58% by weight of rice bran, 1% by weight of cedar, and 1% by weight of rice bran was used. In the molding process of each example, it was molded into a pellet shape having a diameter of 8 mm.
- Comparative Example A is an unheated biomass solid fuel (WP) that has been molded after crushing and pulverization and has not undergone a heating step. In Comparative Example A, no binder is used. The raw material biomass is the same as in Example A-1. The properties of the solid fuel of Comparative Example A are also shown in Table 1.
- HGI is based on JIS M 8801, and the higher the value, the better the grindability.
- Table 1 also shows the results of the higher calorific value (anhydrous basis), the fuel ratio calculated based on the industrial analysis value (air-dry basis), and the elemental analysis value (air-dry basis), and the oxygen O obtained based on this. , Carbon C, and hydrogen H, respectively.
- FIG. 1 shows the correlation between the heating temperature in the heating step and the COD (chemical oxygen demand) and pH of the immersion water when the obtained biomass solid fuel is immersed in water (the pH will be described later).
- the preparation of the immersion water sample for COD measurement was conducted according to JIS K0102 (2010) -17 according to the test method of metals, etc. contained in the environmental waste notification No. 13 (ii) industrial waste in 1973.
- the COD of Comparative Example A is a high value of about 1200 ppm.
- biomass solid fuel heated at 230 ° C. or higher had a COD of 800 ppm or less, indicating that tar content was low. Therefore, it has been shown that the biomass solid fuels of Examples A-1 to A-6 are fuels that have less tar content and excellent handling properties even during outdoor storage. Note that the COD of the biomass solid fuels of Examples A-1 to A-6 heated at 230 ° C. or higher decreased as the heating temperature increased. This is because the COD value is reduced due to volatilization of tar content and the like accompanying heating.
- FIG. 2 shows the correlation between the heating temperature in the heating step, the pulverization property (HGI) of the obtained biomass solid fuel A, and the pulverization rate (described later), and the biomass solid fuels of Comparative Example A and Examples A-1 to A-6 It is a figure shown about.
- HGI pulverization property
- the pulverization speed in FIG. 2 was measured by measuring the weight (g / min) per unit time by measuring the weight of a 700 cc sample that was pulverized by a ball mill and passing through a 150 ⁇ m sieve as the sample after pulverization. Is.
- the ball mill is compliant with JIS M4002, and is used in a cylindrical container having an inner diameter of 305 mm ⁇ axial length of 305 mm.
- the standard grade ball bearings defined in JIS B1501 ( ⁇ 36.5 mm ⁇ 43, ⁇ 30.2 mm ⁇ 67, ⁇ 24.4 mm ⁇ 10 pieces, ⁇ 19.1 mm ⁇ 71 pieces, ⁇ 15.9 mm ⁇ 94 pieces), and rotated at a speed of 70 rpm for measurement.
- the pulverization rate is improved by heating, and the pulverization rate is rapidly increased particularly by heating at 230 ° C. or higher. It can be said that the pulverization rate of the biomass solid fuel A is increased and the pulverization rate is improved by elution and solidification of organic components such as tar accompanying heating. Therefore, even if the heating temperature in the heating step is 150 ° C. or higher and lower than 230 ° C., it is presumed that the HGI and the pulverization rate are improved as compared with the non-heated Comparative Example A.
- Table 2 shows the cumulative ratio under sieving of the biomass solid fuel A subjected to the pulverization test
- FIG. 3 shows the particle size distribution.
- a pulverization test was performed. A 1 kg sample was placed in a resin bag from a height of 8.6 m and dropped 20 times, and then a rotational strength test was performed based on JIS Z 8841 to measure the particle size distribution. The obtained particle size distribution is shown in FIG. If the 2 mm sieve product in the sample particle size distribution is 30 wt% or less, and the 0.5 mm sieve product is 15 wt% or less, it is assumed that the particle size can be handled in transportation, storage, and the like. From Table 2 and FIG. 3, the sample particle size after the rotational strength test became finer as the solid temperature increased, but all the samples cleared the above-mentioned evaluation criteria, suggesting that they can be handled without problems. It was done.
- Table 3 and FIG. 4 show the results of an immersion test of biomass solid fuel A in water.
- the solid fuel of each Example and Comparative Example was immersed in water, taken out after a predetermined time shown in Table 3 and FIG. 4, wiped off the moisture, and the solid moisture was measured.
- the solid fuel of Comparative Example A (WP) was disintegrated by immersion in water, and measurement of solid moisture was impossible.
- the water content reached equilibrium in about 10 hours after immersion, and the equilibrium water content was about 27 wt%.
- the water content reached equilibrium after about 100 hours, and the equilibrium water content was about 25 wt%.
- Examples A-3 to A-5 were also equilibrated at a water content of about 23 wt% after about 100 hours.
- Example A-6 also almost reached equilibrium after about 100 hours, and the equilibrium water content was about 28 wt% (the fluctuation is larger than in Examples A-3 to A-5, but is considered to be due to variations in raw materials). .
- These results are thought to be because the surface of the biomass solid fuel changed to hydrophobic due to elution and solidification of organic components such as tar with heating.
- Examples A-1 to A-6 (PBT) are stored outdoors. As a solid fuel, there are advantageous characteristics as a solid fuel.
- FIG. 5 shows the results of measurement of solid strength before and after immersion in water (based on JIS Z 8841 rotational strength test method) for Examples A-1 to A-6 and Comparative Example A.
- Comparative Example A collapsed after being immersed in water, and thus the rotational strength after immersion was not measurable.
- Examples A-1 to A-6 (PBT) those obtained by wiping off the surface moisture of the solid fuel that reached the equilibrium moisture and drying it at 35 ° C. for 22 hours using a constant temperature dryer were used.
- FIG. 6 is a diagram showing the results of measuring the mechanical durability before and after immersion in water.
- the mechanical durability DU is expressed by the following formula in accordance with American agricultural industry standard ASAE S 269.4 and German industrial standard DIN EN 15210-1. Measured based on In the formula, m0 is the sample weight before the rotation treatment, m1 is the sample weight on the sieve after the rotation treatment, and a sieve using a plate sieve with a circular hole diameter of 3.15 mm was used.
- Example A-2 The evaluation was based on the “Spontaneous ignition test” of the “UN Test and Criteria Manual: Dangerous Goods Shipment and Storage Regulations 16th edition”. A measurement was made to determine whether 1 to 2 cm 3 of the biomass solid fuel (heating temperature 250 ° C.) of Example A-2 was dropped from a height of 1 m onto an inorganic heat insulating board and ignited within 5 minutes after dropping or within 5 minutes after dropping. I went twice. None of the six tests ignited, and Example A-2 (PBT) was determined not to fall under Container Class I in the United Nations Test and Criteria Manual.
- FIG. 7 is a graph showing the measurement result of the BET specific surface area of the solid fuel A.
- the sample was adjusted to 2 to 6 mm as a pretreatment. After being cut and filled into a container, vacuum deaeration was performed at 100 ° C. for 2 hours to obtain a BET specific surface area. Nitrogen gas was used as the adsorption gas.
- FIG. 7 shows that the BET specific surface area increases with increasing heating temperature, and that pores develop with heating (pyrolysis).
- FIG. 8 shows the average pore diameter on the surface of the solid fuel A
- FIG. 9 shows the total pore volume. Both the average pore diameter and the total pore volume were measured using the same apparatus as the BET specific surface area.
- the “pore” here is a pore having a diameter of 2 nm to 100 nm. Since the average pore diameter decreases with increasing heating temperature in Example A-2 and later, it shows that many fine pores are generated. This is believed to be due to cellulose degradation.
- FIG. 10 shows the yield (solid yield and heat yield) of biomass solid fuel A after the heating step.
- the solid yield is the weight ratio before and after heating
- the heat yield is the calorific value ratio before and after heating. Note that, as described above, holding at the target temperature (heating temperature) of each example is not performed (the same applies to Examples B to K below).
- biomass solid fuel A with reduced COD, improved grindability, reduced water absorption, improved solid strength, and improved yield is obtained at low cost. It was shown that
- Natural exothermic index (SCI) ⁇ O2 adsorption amount * O2 adsorption heat * (1/100) ⁇ + ⁇ CO generation amount * (CO production heat + (1/2) * H2O production heat * H / C) * (1/100) ⁇ + ⁇ CO2 generation amount * (CO2 generation heat + (1/2) * H2O generation heat * H / C) * (1/100) ⁇ (1)
- the adsorption amount, generation amount, and H / C in the solid fuel of Example A-2 are as follows.
- FIG. 11 also shows SCI of bituminous coal in Table 4.
- the horizontal axis in FIG. 11 is arrival-based moisture, and the SCI of bituminous coal in FIG. 11 is prepared by adding moisture to the bituminous coal shown in Table 4 and preparing four types of samples each having different moisture. The SCI is calculated.
- the biomass solid fuel (PBT) of the present invention has a lower SCI (spontaneously exothermic) than bituminous coal and is comparable to high moisture bituminous coal. SCI (spontaneously exothermic). Thereby, it can be said that the biomass solid fuel A (PBT) is a good fuel with reduced risk of ignition during handling.
- FIGS. 15 to 17 are cross-sectional SEM photographs before and after immersion in water in Comparative Example A (WP), FIG. 15 is before immersion, FIG. 16 is after immersion for 2 seconds, and FIG. 17 is after immersion for 20 seconds.
- the cross section after immersion is a cross section obtained by cutting the solid fuel after immersion for 2 seconds or 20 seconds. The magnification and scale are shown below each photo.
- Comparative Example A Comparative Example A (FIGS. 15 to 17)
- the pores are enlarged after immersion in water. Since this is a molded product of biomass in which Comparative Example A (WP) is pulverized as described above, it is presumed that the biomass was absorbed by water soaking and pores (gap between biomass powders) were enlarged. Accordingly, it is considered that the pulverized biomass is separated from each other by further intrusion of moisture into the enlarged pores, and the solid fuel itself collapses (see FIG. 4).
- WP Comparative Example A
- Example A-2 solid bridges develop between the biomass powders by heating, the hydrophobicity is improved and it is difficult to absorb water, and it is presumed that there is little change due to immersion. Therefore, even after immersion, since the connection or adhesion between the pulverized biomass by solid crosslinking is maintained, it is unlikely to collapse as in Comparative Example A. Therefore, in the heated solid fuels of Examples A-1 to A-6 (PBT), as shown in FIG. 4, biomass solids in which collapse due to rain water or the like is suppressed and handling properties during outdoor storage are ensured. Fuel has been obtained.
- Example B-1 to Example B-4 PBT
- the temperature was raised to the target temperature (heating temperature described in Table 5) in the same manner as in Example A except that European red pine was used as the raw material biomass. did.
- Tables 5 and 6 show properties of the solid biomass fuel B (Example B-1 to Example B-4) obtained after the heating step.
- Comparative example B (WP) was shown in the same manner.
- Example A no binder is used in any of Examples B-1 to B-4 and Comparative Example B. Since the moisture after immersion in water is after immersion for 100 hours or more (168 hours in Example B), it is considered that the moisture in the solid fuel B has substantially reached equilibrium.
- the measuring method of each property of the biomass solid fuel is the same as in Example A above.
- the ball mill grindability described in Table 6 was measured as follows.
- the pulverization time of each biomass solid fuel B was 20 minutes, and the weight ratio under a 150 ⁇ m sieve after 20 minutes was used as a pulverization point.
- the ball mill uses what conforms to JIS M4002, and uses a standard class ball bearing ( ⁇ 36.5 mm ⁇ 43, ⁇ 30.2 mm ⁇ 67, ⁇ 36.5 mm ⁇ 67 ⁇ 24.4 mm ⁇ 10 pieces, ⁇ 19.1 mm ⁇ 71 pieces, ⁇ 15.9 mm ⁇ 94 pieces), and rotated at a speed of 70 rpm for measurement. The higher the value, the better the grindability. It was confirmed that the pulverization point increased as the heating temperature increased.
- Comparative Example B disintegrated immediately after being immersed in water.
- the biomass powders were kept connected or adhered to each other even after being immersed in water (168 hours) and did not collapse.
- the solid shape was maintained after immersion, so that moisture measurement was possible and the expression of water resistance could be confirmed.
- pulverization is improved and COD is reduced as compared with Comparative Example B.
- Example B-3 is particularly excellent from the viewpoint of water resistance (moisture after immersion), and the biomass solid fuels of Examples B-2 and B-3 exhibit particularly excellent physical properties from the viewpoint of yield.
- Example B-2 is a fuel having excellent water resistance and pulverization properties and reduced COD based on the development of solid bridges.
- Example C The raw material biomass was heated to the target temperature (heating temperature described in Table 5) and heated (Example C-1 to Example C-4: PBT) in the same manner as in Example A, except that almond old wood was used. .
- the ball mill grindability was measured by the same method as in Example B above.
- Tables 5 and 6 show properties of the biomass solid fuel C obtained after the heating step.
- the water after immersion in water is considered to be balanced because it is after immersion for 100 hours or longer (168 hours in Example C).
- Comparative example C (WP) was shown in the same manner. In Examples C-1 to C-4 and Comparative Example C, no binder is used.
- Comparative Example C disintegrated immediately after being immersed in water.
- the connection or adhesion between the biomass powders is maintained even after being immersed in water, and the water resistance is improved without being destroyed.
- improvement in grindability and reduction in COD are shown.
- Example C-2, Example C-3 and Example C-4 are excellent, and from the viewpoint of thermal yield, Example C-1, Example C-2 and Example C- 3 is excellent.
- the HGI of Example C-1 is lower than that of Comparative Example C, but this is considered to be due to variations in raw materials and measurement errors, and it is estimated that there is at least an HGI equivalent to or higher than that of Comparative Example C. .
- Example D The raw material biomass was heated to the target temperature (heating temperature described in Table 5) and heated (Example D-1) in the same manner as in Example A, except that (30 wt% almond shell + 70 wt% almond old wood) was used.
- the ball mill grindability was measured by the same method as in Example B above.
- Tables 5 and 6 show properties of the biomass solid fuel D obtained after the heating step.
- the water after immersion in water is assumed to be balanced after immersion for 100 hours or more (168 hours in Example D). The same applies to Comparative Example D (WP). In Examples D-1 to D-4 and Comparative Example D, no binder is used.
- Comparative Example D disintegrated immediately after being immersed in water.
- Examples D-1 to D-4 even after immersion in water, the connection or adhesion between the biomass powders is maintained, so that they do not collapse and the water resistance is improved.
- improvement in grindability and reduction in COD are shown.
- Examples D-2, D-3, and D-4 are excellent from the viewpoint of COD
- Examples D-1, D-2, and D-3 are particularly excellent from the viewpoint of thermal yield. showed that.
- Example E> The temperature was increased to the target temperature (heating temperature described in Table 5) in the same manner as in Example A, except that Acacia xylem was used as the raw material biomass, the biomass was molded into a tablet shape, and a ⁇ 70 mm tubular furnace was used as the heating device. Warmed and heated (Example E-1 to Example E-3: PBT). Properties of the biomass solid fuel E obtained after the heating step are shown in Tables 5 and 6. The water after immersion in water is considered to be balanced after immersion for 100 hours or more (168 hours in Example E). The same applies to Comparative Example E (WP). In Examples E-1 to E-3 and Comparative Example E, no binder is used.
- Example E the pH was measured by immersing the solid fuel at a solid-liquid ratio of 1:13.
- the immersion time of Comparative Example E in Table 6 indicates that the pH was measured, that is, the pH after 96 hours had elapsed after Comparative Example E was immersed.
- Example E Comparative Example E disintegrated immediately after immersion in water, but Examples E-1 to E-3 maintained water resistance without disintegration because the connection or adhesion between the biomass powders was maintained.
- Examples E-2 and E-3 are excellent from the viewpoint of water resistance (water after immersion in water), and Examples E-1 and E-2 are excellent from the viewpoint of heat yield.
- PBT heated at 240 to 270 ° C. is presumed to have formed the above-mentioned solid crosslinks, and is considered to have excellent water resistance, COD, pulverization properties, and the like. Further, the heat yield of Example E-1 exceeds 100%, but this is due to variations in raw materials and measurement errors.
- Example F The temperature was raised to the target temperature (heating temperature described in Table 5) and heated (Example F-1 to Example F-4: PBT) in the same manner as in Example E except that acacia bark was used as the raw material biomass.
- Tables 5 and 6 show the properties of the solid biomass fuel F obtained after the heating step.
- the water after immersion in water is considered to be balanced after immersion for 100 hours or more (168 hours or more in Example F).
- Comparative Example F WP
- no binder is used.
- Example F the pH was measured by immersing the solid fuel at a solid-liquid ratio of 1:13.
- the immersion time of Comparative Example F in Table 6 indicates that the pH was measured, that is, the pH after 96 hours had elapsed after Comparative Example F was immersed.
- Examples F-2, F-3, and F-4 are excellent from the viewpoint of COD and water resistance (moisture after immersion in water), and Examples F-1, F-2, and F are preferable from the viewpoint of thermal yield. -3 is excellent.
- Example G> The temperature was raised to the target temperature (heating temperature described in Table 5) in the same manner as in Example A except that (70 wt% almond shell + 30 wt% walnut shell) was used as the raw material biomass and a ⁇ 70 mm tubular furnace was used as the heating device. And heated (Example G-1 to Example G-4: PBT). Properties of the biomass solid fuel G obtained after the heating step are shown in Tables 5 and 6. Water after immersion in water is considered to be in equilibrium after being immersed for 100 hours or longer (144 hours or longer in Example G). The same applies to Comparative Example G (WP). In Examples G-1 to G-4 and Comparative Example G, no binder is used.
- Example G disintegrated immediately after being immersed in water, but Examples G-1 to G-4 maintained the connection or adhesion between the biomass powders and exhibited water resistance without disintegration.
- Examples G-2, G-3, and G-4 are excellent from the viewpoint of COD and water resistance (moisture after immersion in water), and Examples G-1 and G-2 and G are preferable from the viewpoint of thermal yield. -3 is excellent.
- the thermal yield of Example G-2 exceeds 100%, but this is due to variations in raw materials and measurement errors.
- Example H The sample was heated to the target temperature (heating temperature described in Table 5) and heated (Example H-1 to Example H-4: PBT) in the same manner as in Example A, except that sago palm was used as the raw material biomass.
- the ball mill grindability was measured by the same method as in Example B above. Properties of the biomass solid fuel H obtained after the heating step are shown in Tables 5 and 6.
- the water after immersion in water is considered to be balanced after immersion for 100 hours or more (168 hours in Example H).
- Comparative Example H (WP) In Examples H-1 to H-4 and Comparative Example H, no binder is used.
- the immersion time of Comparative Example H in Table 6 indicates that the pH was measured, that is, the pH after 24 hours had elapsed after Comparative Example H was immersed.
- Example H-1 to H-4 maintained water resistance without disintegration because the connection or adhesion between biomass powders was maintained.
- Example H-2, Example H-3, and Example H-4 are excellent from the viewpoint of COD, pH (slightly low) and water resistance (moisture after immersion in water), and Example H-1 and Example from the viewpoint of thermal yield H-2, example H-3, is excellent.
- Example I> The sample was heated to the target temperature (heating temperature described in Table 5) and heated (Example I-1) in the same manner as in Example A, except that EFB (empty fruit bunch of palm oil processing residue) was used as the raw material biomass.
- Example I-3 heated at 270 ° C. and Example I-4 heated at 300 ° C. was measured by the following method.
- a sample of 50 g is filled in a 1,000 cc polypropylene container, and is rotated with a MISUGI mixing man SKH-15DT at 60 rpm for 30 minutes (total 1,800 revolutions).
- m0 is the sample weight before the rotation treatment
- m1 is the sample weight on the sieve after the rotation treatment.
- Comparative Example I disintegrated immediately after immersion in water, but Examples I-1 to I-4 maintained the connection or adhesion between biomass powders and exhibited water resistance without disintegration.
- Examples I-2, I-3, and I-4 are excellent from the viewpoint of COD and water resistance (moisture after immersion in water), and Examples I-1, I-2, and I are excellent from the viewpoint of thermal yield. -3 is excellent.
- Example J The sample was heated to the target temperature (heating temperature described in Table 5) and heated (Example J-1, Example J-2: PBT) in the same manner as in Example A except that Meranti was used as the raw material biomass. Properties of the biomass solid fuel J obtained after the heating step are shown in Tables 5 and 6. The water after immersion in water is considered to be balanced after immersion for 100 hours or more (168 hours in Example J). The same applies to Comparative Example J (WP). In all of Examples J-1, J-2, and Comparative Example J, no binder is used.
- Example K The sample was heated to the target temperature (heating temperature described in Table 5) and heated (Example K) in the same manner as in Example A, except that a rubber tree was used as the raw material biomass and a ⁇ 70 mm tubular furnace was used as the heating device. -1).
- Table 5 shows properties of the biomass solid fuel K obtained after the heating step. The same applies to Comparative Example K (WP). In any case, no binder is used.
- Example K-1 As for the comparative example K, it is expected to collapse by immersion in water as in the other examples.
- Example K-1 the formation of the above-mentioned solid bridge is expected to improve water resistance, pulverization, reduce COD, etc. without being disintegrated even when immersed in water.
- Example K-1 is heated at 270 ° C., but the same effect can be estimated for a heating temperature of 230 to 270 ° C. as described above.
- the pellet diameters before and after immersion were measured by the same electronic caliper and measurement method as those in Table 7.
- Table 8 shows the measurement results.
- the measured value of the pellet diameter is an average value of 10 randomly selected in each of Examples A-1 to A-6.
- Tables 7 and 8 show that the expansion rate decreases as the temperature of the heating process increases. It is presumed that the expansion is suppressed by the formation of solid crosslinks accompanying heating. Although the radial expansion coefficient in Table 8 is higher than the length expansion coefficient in Table 7, this is because the immersion time is longer in Table 7, and because Example A is a pellet, it is mainly consolidated in the radial direction. Therefore, it is considered that the expansion also increases in the radial direction.
- the expansion coefficient is 10% or less even in Example A-1 having the largest radial expansion coefficient.
- the diameter and length expansion coefficient is preferably 10% or less, and more preferably 7% or less.
- the volume expansion coefficient is preferably 133% or less, and more preferably 123% or less.
- Example B is a pellet, and the diameter expansion coefficient calculated using the pellet diameter before immersion (initial dimension in Table 6) and the pellet diameter after immersion (dimension after immersion in Table 6) based on the formula (2) is It was 15% or less (hereinafter, the expansion coefficient of the diameter after Example B uses the formula (2)).
- the expansion coefficient of the diameter after Example B uses the formula (2).
- the radial expansion coefficient is preferably 20% or less, and more preferably 10% or less.
- the volume expansion coefficient is preferably 173% or less, and more preferably 133% or less.
- Example C is also a pellet, and the volume expansion coefficient is 123% or less on the assumption that the diameter expansion coefficient before and after immersion is 7.2% or less and the length expansion coefficient is 7.2% at the maximum. Similarly, the volume expansion coefficient is calculated).
- the diameter expansion coefficient in Example C is preferably 13% or less, and more preferably 7% or less.
- the volume expansion coefficient is preferably 144% or less, and more preferably 123% or less.
- Example D pellet
- the expansion coefficient before and after immersion is 8.8% or less, and the volume expansion coefficient based on it is 129% or less.
- the diameter expansion coefficient in Example D is preferably 10% or less, and more preferably 8% or less.
- the volume expansion coefficient is preferably 133% or less, and more preferably 126% or less.
- Example E has a tablet shape, the diameter ( ⁇ ) expansion coefficient is 2.5% or less, the height (H) expansion coefficient is 40% or less, and the volume expansion coefficient is 147% or less.
- the radial expansion coefficient is preferably 5% or less, and more preferably 2.3% or less.
- the height expansion coefficient is preferably 50% or less, and more preferably 20% or less.
- the volume expansion rate is preferably 165% or less, and more preferably 126% or less.
- Example F has a diameter expansion coefficient of 4.0% or less, a height expansion coefficient of 15% or less, and a volume expansion coefficient of 124% or less. Note that the height after immersion in Example F-3 is considered to be a measurement error or individual variation.
- the expansion coefficient is preferably 5% or less, and more preferably 3% or less.
- the height expansion coefficient is preferably 40% or less, and more preferably 10% or less.
- the volume expansion coefficient is preferably 154% or less, and more preferably 117% or less.
- the expansion coefficient before and after immersion is 8.8% or less, and the volume expansion coefficient based on it is 129% or less.
- the expansion coefficient is preferably 10% or less, and more preferably 8% or less.
- the volume expansion coefficient is preferably 133% or less, and more preferably 126% or less.
- Example H pellet
- the expansion coefficient before and after immersion is 6.9% or less, and the volume expansion coefficient based on it is 122% or less.
- the radial expansion coefficient is preferably 10% or less, and more preferably 7% or less.
- the volume expansion coefficient is preferably 133% or less, and more preferably 123% or less.
- Example I pellets
- the expansion coefficient before and after immersion is 4.1% or less, and the volume expansion coefficient based on it is 113% or less.
- the expansion coefficient is preferably 10% or less, and more preferably 5% or less.
- the volume expansion rate is preferably 133% or less, and more preferably 116% or less.
- Example J the diameter expansion coefficient before and after immersion is 5.4% or less, and the volume expansion coefficient based on it is 117% or less.
- the expansion coefficient is preferably 20% or less, and more preferably 10% or less.
- the volume expansion coefficient is preferably 173% or less, and more preferably 133% or less.
- the solid fuel (PBT) of the present invention using biomass as a raw material preferably has an expansion coefficient of 40% or less before and after immersion (including diameter and height). Is preferably about 275% or less. More preferably, the expansion coefficient of diameter and length is 30% or less, and the volume expansion coefficient is about 220% or less. More preferably, the expansion coefficient of diameter and length is 20% or less, and the volume expansion coefficient is about 173% or less. More preferably, the expansion coefficient of diameter and length is 10% or less, and the volume expansion coefficient is about 133% or less.
- the expansion rate after immersion in water is within a certain range, it is indicated that the biomass solid fuel (PBT) does not collapse even by immersion and has water resistance.
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Abstract
Description
図26Aは本発明の概略図、図27はプロセスフローである。図27の燃料製造工程100によって得られたバイオマス固体燃料は、分級工程200及び冷却工程300を経て製品となる。 [Embodiment]
FIG. 26A is a schematic diagram of the present invention, and FIG. 27 is a process flow. The biomass solid fuel obtained by the
(1)バイオマス成型体を炭化してバイオマス炭化物(PBT)を得るキルン1(炭化炉)と、キルン1の下流側に設けられ、バイオマス炭化物(PBT)を分級する分級部21(分級手段)と、分級部21の下流側に設けられ、分級されたバイオマス炭化物(PBT)を冷却する冷却部22(冷却手段)とを備え、
バイオマス成型体は、原料のバイオマスを粉砕した後成型して得られた成型体であって、冷却部22は、散水によりバイオマス炭化物(PBT)を冷却することとした。 [effect]
(1) A kiln 1 (carbonization furnace) that carbonizes a biomass molded body to obtain biomass carbide (PBT), and a classification unit 21 (classification means) that is provided downstream of the
The biomass molded body was a molded body obtained by pulverizing the raw material biomass and then molded, and the
バイオマス固体燃料は、バイオマスを破砕後粉砕し、屑または粉状となったバイオマスを圧縮・成型して塊状物とする成型工程、成型工程後の塊状物を加熱する加熱工程を経て得られた成型済固体物を燃料とするものである(後述のPBTに相当)。このバイオマス固体燃料は、水蒸気爆砕の工程、およびバインダーを要しないため、コストアップを抑制することができる。なお、本明細書においては、成型工程により得られ、加熱工程前の塊状物のことを「未加熱塊状物」とも記載する。この未加熱塊状物とは上述のWPに相当する。 [Manufacture of biomass solid fuel (PBT) in the fuel manufacturing process]
Biomass solid fuel is a molding obtained by crushing biomass after crushing, compressing and molding biomass that has become scrap or powder to form a lump, and a heating process that heats the lump after the forming process Spent solids are used as fuel (corresponding to PBT described later). Since this biomass solid fuel does not require a steam explosion process and a binder, an increase in cost can be suppressed. In the present specification, the block obtained by the molding process and before the heating step is also referred to as “unheated block”. This unheated lump corresponds to the above-mentioned WP.
(米松、米栂、杉、および桧:固体燃料A)
本発明の一態様として、原料が米松、米栂、杉、および桧から選ばれる少なくとも1種を含む場合のバイオマス固体燃料(以下、固体燃料Aと記載することがある)の性状は以下のとおりである。 [Types of raw material biomass and properties of solid fuel]
(Yonematsu, rice straw, cedar, and firewood: solid fuel A)
As one aspect of the present invention, the properties of biomass solid fuel (hereinafter sometimes referred to as solid fuel A) when the raw material contains at least one selected from rice pine, rice bran, cedar, and straw are as follows: It is.
本発明の一態様として、原料が欧州アカマツである場合のバイオマス固体燃料(以下、固体燃料Bと記載することがある)の性状は以下のとおりである。 (European red pine: Solid fuel B)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel B) when the raw material is European red pine are as follows.
本発明の一態様として、原料がアーモンド古木である場合のバイオマス固体燃料(以下、固体燃料Cと記載することがある)の性状は以下のとおりである。 (Almond old wood: solid fuel C)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel C) when the raw material is an almond old tree are as follows.
本発明の一態様として、原料がアーモンド殻とアーモンド古木の混合物である場合のバイオマス固体燃料(以下、固体燃料Dと記載することがある)の性状は以下のとおりである。 (A mixture of almond shells and old almond wood: solid fuel D)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel D) when the raw material is a mixture of almond shells and almond old wood are as follows.
本発明の一態様として、原料がアカシア木部である場合のバイオマス固体燃料(以下、固体燃料Eと記載することがある)の性状は以下のとおりである。 (Acacia Kibe: Solid Fuel E)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel E) when the raw material is an acacia xylem are as follows.
本発明の一態様として、原料がアカシアバークである場合のバイオマス固体燃料(以下、固体燃料Fと記載することがある)の性状は以下のとおりである。 (Acacia bark: solid fuel F)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel F) when the raw material is acacia bark are as follows.
本発明の一態様として、原料がアーモンド殻と胡桃殻の混合物である場合のバイオマス固体燃料(以下、固体燃料Gと記載することがある)の性状は以下のとおりである。 (Almond shell and walnut shell mixture: solid fuel G)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel G) when the raw material is a mixture of almond shells and walnut shells are as follows.
本発明の一態様として、原料がサゴヤシである場合のバイオマス固体燃料(以下、固体燃料Hと記載することがある)の性状は以下のとおりである。 (Sago: solid fuel H)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel H) when the raw material is sago palm are as follows.
本発明の一態様として、原料がEFB(パーム油加工残渣の空果房)である場合のバイオマス固体燃料(以下、固体燃料Iと記載することがある)の性状は以下のとおりである。 (EFB: Solid Fuel I)
As one aspect of the present invention, the properties of biomass solid fuel (hereinafter sometimes referred to as solid fuel I) when the raw material is EFB (empty fruit bunch of palm oil processing residue) are as follows.
本発明の一態様として、原料がメランティである場合のバイオマス固体燃料(以下、固体燃料Jと記載することがある)の性状は以下のとおりである。 (Melanty: Solid fuel J)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel J) when the raw material is meranti are as follows.
本発明の一態様として、原料がゴムの木である場合のバイオマス固体燃料(以下、固体燃料Kと記載することがある)の性状は以下のとおりである。 (Rubber tree: solid fuel K)
As one aspect of the present invention, the properties of a biomass solid fuel (hereinafter sometimes referred to as solid fuel K) when the raw material is a rubber tree are as follows.
(例A-1~A-6)
バイオマスを破砕後粉砕し、粉砕されたバイオマスを成型する成型工程およびその後の加熱工程を経てバイオマス固体燃料A(PBT)を得た。いずれの工程においてもバインダーは使用されない。原料のバイオマスとして、米松40重量%、米栂58重量%、杉1重量%、桧1重量%の混合物を用いた。各例の成型工程においては、直径8mmのペレット形状に成型した。各実施例における加熱工程ではφ600mm電気式バッチ炉にそれぞれの原料を4kg投入し、2℃/minの昇温速度で各実施例における目標温度(表1における加熱温度)まで昇温させ、加熱した。以下、目標温度と加熱温度は同一のものを指す。各例A-1~A-6いずれにおいても目標温度(加熱温度)における保持は行っていない(以下の例B~例Kも同様)。例A-1~A-6の加熱工程における加熱温度と、加熱工程後に得られたバイオマス固体燃料Aの性状を表1に示す。 <Example A>
(Examples A-1 to A-6)
The biomass was crushed and then pulverized, and a biomass solid fuel A (PBT) was obtained through a molding process for molding the pulverized biomass and a subsequent heating process. No binder is used in any step. As a raw material biomass, a mixture of 40% by weight of rice pine, 58% by weight of rice bran, 1% by weight of cedar, and 1% by weight of rice bran was used. In the molding process of each example, it was molded into a pellet shape having a diameter of 8 mm. In the heating process in each example, 4 kg of each raw material was put into a φ600 mm electric batch furnace, heated to the target temperature in each example (heating temperature in Table 1) at a heating rate of 2 ° C./min, and heated. . Hereinafter, the target temperature and the heating temperature are the same. In each of Examples A-1 to A-6, the target temperature (heating temperature) is not maintained (the same applies to Examples B to K below). Table 1 shows the heating temperature in the heating process of Examples A-1 to A-6 and the properties of the biomass solid fuel A obtained after the heating process.
比較例Aは破砕、粉砕後に成型したのみで加熱工程を経ていない、未加熱のバイオマス固体燃料(WP)である。比較例Aについてもバインダーは不使用である。原料のバイオマスは、例A-1と同様である。比較例Aの固体燃料の性状についても表1に示す。 (Comparative Example A)
Comparative Example A is an unheated biomass solid fuel (WP) that has been molded after crushing and pulverization and has not undergone a heating step. In Comparative Example A, no binder is used. The raw material biomass is the same as in Example A-1. The properties of the solid fuel of Comparative Example A are also shown in Table 1.
図1は加熱工程における加熱温度と、得られたバイオマス固体燃料を水中に浸漬した際の浸漬水のCOD(化学的酸素要求量)およびpHの相関を示すものである(pHについては後述)。COD測定用浸漬水試料の調製は、昭和48年環境庁告示第13号(イ)産業廃棄物に含まれる金属等の検定方法に従い、CODはJIS K0102(2010)-17によって分析した。 [COD]
FIG. 1 shows the correlation between the heating temperature in the heating step and the COD (chemical oxygen demand) and pH of the immersion water when the obtained biomass solid fuel is immersed in water (the pH will be described later). The preparation of the immersion water sample for COD measurement was conducted according to JIS K0102 (2010) -17 according to the test method of metals, etc. contained in the environmental waste notification No. 13 (ii) industrial waste in 1973.
例A-1~A-6および比較例Aの固体燃料を固液比1:3で浸漬し、pHを測定した。図1から、例A-2および例A-3については若干値が低くなるものの、全ての例A-1~A-6において概ねpHは6前後であり、加熱前の比較例Aと比べて特に変化はないことが示される。したがって、例A-1~A-6を屋外貯蔵した際に出る排水のpHについては特に問題ないことが示される。 [PH]
The solid fuels of Examples A-1 to A-6 and Comparative Example A were immersed at a solid-liquid ratio of 1: 3, and the pH was measured. From FIG. 1, although the values for Examples A-2 and A-3 are slightly lower, in all of Examples A-1 to A-6, the pH is approximately around 6, compared with Comparative Example A before heating. There is no particular change. Therefore, it is shown that there is no particular problem with respect to the pH of the drainage discharged when Examples A-1 to A-6 are stored outdoors.
図2は加熱工程における加熱温度と、得られたバイオマス固体燃料Aの粉砕性(HGI)、および粉砕速度(後述)の相関を、比較例Aおよび例A-1~A-6のバイオマス固体燃料について示す図である。 [Crushability]
FIG. 2 shows the correlation between the heating temperature in the heating step, the pulverization property (HGI) of the obtained biomass solid fuel A, and the pulverization rate (described later), and the biomass solid fuels of Comparative Example A and Examples A-1 to A-6 It is a figure shown about.
表2は粉化試験を行ったバイオマス固体燃料Aの篩下積算割合、図3はその粒度分布図である。ペレットのハンドリング特性を評価するために、粉化試験を実施した。サンプル1kgを8.6mの高さから樹脂製の袋に入れて20回落下させた後、JIS Z 8841に基づき回転強度試験を行い、粒度分布を測定した。得られた粒度分布を図3に示す。サンプル粒度分布における2mm篩下品が30wt%以下、および0.5mm篩下品が15wt%以下であれば搬送、貯蔵等におけるハンドリングが可能な粒度であるとみなすものとする。表2および図3より、回転強度試験後のサンプル粒度は固体温度が高くなるにつれて細かくなったが、いずれのサンプルにおいても上述の評価基準をクリアしており、問題無くハンドリング可能であることが示唆された。 [Powdering test]
Table 2 shows the cumulative ratio under sieving of the biomass solid fuel A subjected to the pulverization test, and FIG. 3 shows the particle size distribution. In order to evaluate the handling characteristics of the pellets, a pulverization test was performed. A 1 kg sample was placed in a resin bag from a height of 8.6 m and dropped 20 times, and then a rotational strength test was performed based on JIS Z 8841 to measure the particle size distribution. The obtained particle size distribution is shown in FIG. If the 2 mm sieve product in the sample particle size distribution is 30 wt% or less, and the 0.5 mm sieve product is 15 wt% or less, it is assumed that the particle size can be handled in transportation, storage, and the like. From Table 2 and FIG. 3, the sample particle size after the rotational strength test became finer as the solid temperature increased, but all the samples cleared the above-mentioned evaluation criteria, suggesting that they can be handled without problems. It was done.
表3および図4はバイオマス固体燃料Aの水中浸漬試験結果である。各実施例および比較例の固体燃料を水中に浸し、表3および図4に示す所定時間経過後に取り出して水分を拭き取って固体水分を測定した。比較例A(WP)の固体燃料は水中浸漬によって崩壊し、固体水分の測定は不可能であった。これに対し、例A-1の固体燃料では浸漬後約10時間で水分量が平衡に達し、平衡水分量は約27wt%であった。また、例A-2の固体燃料では約100時間経過後に水分量が平衡に達し、平衡水分は約25wt%であった。例A-3~A-5についても約100時間後に水分量約23wt%で平衡となった。例A-6も約100時間経過後にほぼ平衡に達し、平衡水分量は約28wt%であった(例A-3~A-5よりも振れが大きいが、原料のばらつきによるものと考えられる)。これらの結果は、加熱に伴うタール等有機成分の溶出・固化により、バイオマス固体燃料の表面が疎水性に変化したためと考えられ、例A-1~A-6(PBT)は屋外貯蔵されることが多い固体燃料として有利な特性を示している。 [Water immersion]
Table 3 and FIG. 4 show the results of an immersion test of biomass solid fuel A in water. The solid fuel of each Example and Comparative Example was immersed in water, taken out after a predetermined time shown in Table 3 and FIG. 4, wiped off the moisture, and the solid moisture was measured. The solid fuel of Comparative Example A (WP) was disintegrated by immersion in water, and measurement of solid moisture was impossible. On the other hand, in the solid fuel of Example A-1, the water content reached equilibrium in about 10 hours after immersion, and the equilibrium water content was about 27 wt%. In the solid fuel of Example A-2, the water content reached equilibrium after about 100 hours, and the equilibrium water content was about 25 wt%. Examples A-3 to A-5 were also equilibrated at a water content of about 23 wt% after about 100 hours. Example A-6 also almost reached equilibrium after about 100 hours, and the equilibrium water content was about 28 wt% (the fluctuation is larger than in Examples A-3 to A-5, but is considered to be due to variations in raw materials). . These results are thought to be because the surface of the biomass solid fuel changed to hydrophobic due to elution and solidification of organic components such as tar with heating. Examples A-1 to A-6 (PBT) are stored outdoors. As a solid fuel, there are advantageous characteristics as a solid fuel.
(回転強度)
図5は例A-1~A-6および比較例Aについて、水中浸漬前後の固体強度(JIS Z 8841 回転強度試験方法 に基づく)を測定した結果である。上述のとおり比較例A(WP)については水中浸漬後崩壊したため、浸漬後の回転強度は測定不可能であった。例A-1~A-6(PBT)については、平衡水分に達した固体燃料の表面水分を拭き取った後、恒温乾燥機にて35℃で22時間乾燥させたものを使用した。加熱工程を経た例A-1~A-6(PBT)の強度はほとんど低下しておらず、水中浸漬前の比較例A(WP)と比べても粉化が発生しにくく、ハンドリング性を維持できるものと言える。 [Solid strength before and after immersion in water]
(Rotational strength)
FIG. 5 shows the results of measurement of solid strength before and after immersion in water (based on JIS Z 8841 rotational strength test method) for Examples A-1 to A-6 and Comparative Example A. As described above, Comparative Example A (WP) collapsed after being immersed in water, and thus the rotational strength after immersion was not measurable. For Examples A-1 to A-6 (PBT), those obtained by wiping off the surface moisture of the solid fuel that reached the equilibrium moisture and drying it at 35 ° C. for 22 hours using a constant temperature dryer were used. The strength of Examples A-1 to A-6 (PBT) that had undergone the heating process was hardly decreased, and pulverization was less likely to occur compared to Comparative Example A (WP) before immersion in water, and handling was maintained. It can be said that it can be done.
図6は水中浸漬前後の機械的耐久性を測定した結果を示す図である。例A-1~A-6、比較例Aの固体燃料について、アメリカ農業工業者規格ASAE S 269.4、およびドイツ工業規格DIN EN 15210-1に準拠して機械的耐久性DUを以下の式に基づいて測定した。式中、m0は回転処理前の試料重量、m1は回転処理後の篩上試料重量であり、篩は円孔径3.15mmの板ふるいを用いた。 (Mechanical durability)
FIG. 6 is a diagram showing the results of measuring the mechanical durability before and after immersion in water. For the solid fuels of Examples A-1 to A-6 and Comparative Example A, the mechanical durability DU is expressed by the following formula in accordance with American agricultural industry standard ASAE S 269.4 and German industrial standard DIN EN 15210-1. Measured based on In the formula, m0 is the sample weight before the rotation treatment, m1 is the sample weight on the sieve after the rotation treatment, and a sieve using a plate sieve with a circular hole diameter of 3.15 mm was used.
回転強度と同様、機械的耐久性についても加熱工程を経た例A-1~A-6(PBT)の強度はほとんど低下しておらず、水中浸漬前の比較例A(WP)と比べても粉化が発生しにくく、ハンドリング性を維持できることが示されている。 DU = (m1 / m0) × 100
Similar to the rotational strength, the mechanical durability of the examples A-1 to A-6 (PBT) that had undergone the heating process was hardly decreased, and even compared with the comparative example A (WP) before being immersed in water. It has been shown that pulverization hardly occurs and handling property can be maintained.
「国連試験および判定基準マニュアル:危険物船舶運送及び貯蔵規則16訂版」の「自然発火性試験」に基づき評価を行った。例A-2のバイオマス固体燃料(加熱温度250℃)1~2cm3を1mの高さから無機質断熱板上に落下させ、落下途中又は落下後5分以内に発火するか否かの測定を6回行った。6回の試験いずれも発火せず、例A-2(PBT)は上記国連試験および判定基準マニュアルの容器等級Iに該当しないと判定された。 [Spontaneous ignition]
The evaluation was based on the “Spontaneous ignition test” of the “UN Test and Criteria Manual: Dangerous Goods Shipment and Storage Regulations 16th edition”. A measurement was made to determine whether 1 to 2 cm 3 of the biomass solid fuel (
自然発火性と同様、「危険物船舶運送及び貯蔵規則16訂版」の「自己発火性試験」に基づき評価を行った。試料容器(一辺が10cmのステンレス網立方体)に例A-2のバイオマス固体燃料(加熱温度250℃)を充填し、恒温槽内部に吊り下げ、140℃の温度で24時間連続して物質の温度を測定した。発火又は200℃を超える温度上昇の認められた物質は、自己発熱性物質と認め、更に一辺が2.5cmの試料容器を使用し同様の試験を行い、発火又は60℃を超える温度上昇の有無を確認した。試験結果に基づき、例A-2(PBT)は自己発熱性物質に該当しないと判定された。 [Self-heating]
As with spontaneous ignition, the evaluation was based on the “Self-Ignition Test” of the “Dangerous Goods Ship Transport and Storage Rules 16th Edition”. Fill a sample container (stainless steel cube with a side of 10 cm) with the biomass solid fuel of Example A-2 (
(BET比表面積)
図7は固体燃料AのBET比表面積の測定結果を示す図である。例A-1~A-6および比較例Aの固体燃料につき、自動比表面積/細孔径分布測定装置(日本ベル(株)製BELSORP-min II)を用い、前処理として試料を2~6mmにカットして容器内に充填した後に、100℃で2時間真空脱気してBET比表面積を求めた。なお吸着ガスには窒素ガスを用いた。図7から、加熱温度の上昇に伴ってBET比表面積は増加しており、加熱(熱分解)にともなって細孔が発達していくことが示される。 [Pore size distribution]
(BET specific surface area)
FIG. 7 is a graph showing the measurement result of the BET specific surface area of the solid fuel A. For the solid fuels of Examples A-1 to A-6 and Comparative Example A, using an automatic specific surface area / pore diameter distribution measuring device (BELSORP-min II manufactured by Nippon Bell Co., Ltd.), the sample was adjusted to 2 to 6 mm as a pretreatment. After being cut and filled into a container, vacuum deaeration was performed at 100 ° C. for 2 hours to obtain a BET specific surface area. Nitrogen gas was used as the adsorption gas. FIG. 7 shows that the BET specific surface area increases with increasing heating temperature, and that pores develop with heating (pyrolysis).
図8は固体燃料A表面の平均細孔直径、図9は全細孔容積を示す図である。平均細孔直径、全細孔容積いずれもBET比表面積と同じ装置を用いて測定した。なお、ここでいう「細孔」とは直径2nm~100nmの孔とする。平均細孔直径は例A-2以降で加熱温度の上昇にともなって減少していることから、細かな細孔が多数生成していくことを示している。これはセルロースの分解に起因すると考えられる。 (Average pore diameter, total pore volume)
FIG. 8 shows the average pore diameter on the surface of the solid fuel A, and FIG. 9 shows the total pore volume. Both the average pore diameter and the total pore volume were measured using the same apparatus as the BET specific surface area. The “pore” here is a pore having a diameter of 2 nm to 100 nm. Since the average pore diameter decreases with increasing heating temperature in Example A-2 and later, it shows that many fine pores are generated. This is believed to be due to cellulose degradation.
図10は加熱工程を経た後のバイオマス固体燃料Aの収率(固体収率および熱収率)である。固体収率は加熱前後の重量比、熱収率は加熱前後の発熱量比である。なお上述のとおり各実施例の目標温度(加熱温度)における保持は行っていない(以下の例B~例Kも同様)。 [yield]
FIG. 10 shows the yield (solid yield and heat yield) of biomass solid fuel A after the heating step. The solid yield is the weight ratio before and after heating, and the heat yield is the calorific value ratio before and after heating. Note that, as described above, holding at the target temperature (heating temperature) of each example is not performed (the same applies to Examples B to K below).
例A-2の固体燃料につき以下の方法で自然発熱性を測定した。試料1kgを容器に装入し、80℃の恒温槽中に反応器を入れて、試料に空気を流して得られたガスのO2、CO、CO2濃度を測定した。加熱前後の濃度から試料の加熱に基づくO2吸着量、CO発生量、CO2発生量を計算し、以下の式(1)に基づき自然発熱性指数(SCI)を算出する。 [Spontaneously exothermic]
The natural heat generation property of the solid fuel of Example A-2 was measured by the following method. 1 kg of the sample was placed in a container, the reactor was placed in a constant temperature bath at 80 ° C., and the
= {O2吸着量*O2吸着熱*(1/100)}+{CO発生量*(CO生成熱+(1/2)*H2O生成熱*H/C)*(1/100)}
+{CO2発生量*(CO2生成熱+ (1/2)*H2O生成熱*H/C)*(1/100)} ・・・式(1) Natural exothermic index (SCI)
= {O2 adsorption amount * O2 adsorption heat * (1/100)} + {CO generation amount * (CO production heat + (1/2) * H2O production heat * H / C) * (1/100)}
+ {CO2 generation amount * (CO2 generation heat + (1/2) * H2O generation heat * H / C) * (1/100)} (1)
CO発生量 0.03[ml/kg・min]
CO2発生量 0.02[ml/kg・min]
H/C(例A-2の固体燃料における水素、炭素のモル比) 1.28[mol/mol](表1参照)
また、式(1)で用いた吸着熱、各生成熱は以下のとおりである。 O2 adsorption amount 0.42 [ml / kg ・ min]
CO emissions 0.03 [ml / kg ・ min]
CO2 generation 0.02 [ml / kg ・ min]
H / C (Molar ratio of hydrogen and carbon in the solid fuel of Example A-2) 1.28 [mol / mol] (see Table 1)
Further, the heat of adsorption and the heat of formation used in the formula (1) are as follows.
CO生成熱 110.5[kJ/mol]
H2O生成熱 285.83[kJ/mol]
CO2生成熱 393.5[kJ/mol]
以上に基づき例A-2にかかる固体燃料のSCIを算出したところ、SCI=1.3であった。なお、バイオマス固体燃料Aは石炭に性状が近接していることから、O2吸着熱は石炭への吸着熱と同一のものを用いた。 O2 adsorption heat 253 [kJ / mol] (same value as O2 adsorption heat on coal)
CO generation heat 110.5 [kJ / mol]
Heat of H2O generation 285.83 [kJ / mol]
CO2 generation heat 393.5 [kJ / mol]
Based on the above, the SCI of the solid fuel according to Example A-2 was calculated to be SCI = 1.3. In addition, since the property of biomass solid fuel A is close to that of coal, the same heat of adsorption of O2 as that of adsorption on coal was used.
図12~図14は例A-2における水中浸漬前後の固体燃料(PBT)の断面SEM写真である。図12は浸漬前、図13は2秒浸漬後、図14は20秒浸漬後である。同様に図15~図17は比較例A(WP)における水中浸漬前後の断面SEM写真であり、図15は浸漬前、図16は2秒浸漬後、図17は20秒浸漬後である。なお例A-2、比較例Aいずれも、浸漬後の断面とは2秒または20秒浸漬後の固体燃料を切断した断面のことである。また、各写真下に倍率およびスケールを示す。 [Surface photo]
12 to 14 are cross-sectional SEM photographs of the solid fuel (PBT) before and after immersion in water in Example A-2. 12 is before immersion, FIG. 13 is after 2 seconds immersion, and FIG. 14 is after 20 seconds immersion. Similarly, FIGS. 15 to 17 are cross-sectional SEM photographs before and after immersion in water in Comparative Example A (WP), FIG. 15 is before immersion, FIG. 16 is after immersion for 2 seconds, and FIG. 17 is after immersion for 20 seconds. In both Example A-2 and Comparative Example A, the cross section after immersion is a cross section obtained by cutting the solid fuel after immersion for 2 seconds or 20 seconds. The magnification and scale are shown below each photo.
例B-1~例B-4(PBT)においては、原料のバイオマスとして欧州アカマツを用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した。加熱工程後に得られたバイオマス固体燃料B(例B-1~例B-4)の性状を表5及び表6に示す。比較例B(WP)についても同様に示した。なお例Aと同様、例B-1~例B-4、比較例Bいずれもバインダーは不使用である。水中浸漬後の水分は100時間以上浸漬後のものであるため(例Bでは168時間)、実質的に固体燃料B内の水分は平衡に達していると看做す。バイオマス固体燃料の各性状の測定方法は、上記例Aと同様である。なお、表6に記載のボールミル粉砕性は、下記のように測定した。 <Example B>
In Example B-1 to Example B-4 (PBT), the temperature was raised to the target temperature (heating temperature described in Table 5) in the same manner as in Example A except that European red pine was used as the raw material biomass. did. Tables 5 and 6 show properties of the solid biomass fuel B (Example B-1 to Example B-4) obtained after the heating step. Comparative example B (WP) was shown in the same manner. As in Example A, no binder is used in any of Examples B-1 to B-4 and Comparative Example B. Since the moisture after immersion in water is after immersion for 100 hours or more (168 hours in Example B), it is considered that the moisture in the solid fuel B has substantially reached equilibrium. The measuring method of each property of the biomass solid fuel is the same as in Example A above. The ball mill grindability described in Table 6 was measured as follows.
各バイオマス固体燃料Bの粉砕時間を20分として、20分後の150μm篩下の重量比を粉砕ポイントとした。なお、ボールミルはJIS M4002に準拠したものを用い、内径305mm×軸方向長さ305mmの円筒容器にJIS B1501に規定された並級ボールベアリング(Φ36.5mm×43個、Φ30.2mm×67個、Φ24.4mm×10個、Φ19.1mm×71個、Φ15.9mm×94個)を入れて70rpmの速度で回転させて測定した。数値が高い方が粉砕性は向上していることを示す。加熱温度の上昇にともない、粉砕ポイントは上昇することを確認した。 [Ball mill grindability]
The pulverization time of each biomass solid fuel B was 20 minutes, and the weight ratio under a 150 μm sieve after 20 minutes was used as a pulverization point. In addition, the ball mill uses what conforms to JIS M4002, and uses a standard class ball bearing (Φ36.5 mm × 43, Φ30.2 mm × 67, Φ36.5 mm × 67 Φ24.4 mm × 10 pieces, Φ19.1 mm × 71 pieces, Φ15.9 mm × 94 pieces), and rotated at a speed of 70 rpm for measurement. The higher the value, the better the grindability. It was confirmed that the pulverization point increased as the heating temperature increased.
原料のバイオマスとして、アーモンド古木を用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例C-1~例C-4:PBT)。ボールミル粉砕性については上記例Bと同様の方法で測定した。加熱工程後に得られたバイオマス固体燃料Cの性状を表5及び表6に示す。例Bと同様、水中浸漬後の水分は100時間以上の浸漬後(例Cでは168時間)であるため平衡しているものと看做す。比較例C(WP)についても同様に示した。なお例C-1~例C-4、比較例Cいずれもバインダーは不使用である。 <Example C>
The raw material biomass was heated to the target temperature (heating temperature described in Table 5) and heated (Example C-1 to Example C-4: PBT) in the same manner as in Example A, except that almond old wood was used. . The ball mill grindability was measured by the same method as in Example B above. Tables 5 and 6 show properties of the biomass solid fuel C obtained after the heating step. As in Example B, the water after immersion in water is considered to be balanced because it is after immersion for 100 hours or longer (168 hours in Example C). Comparative example C (WP) was shown in the same manner. In Examples C-1 to C-4 and Comparative Example C, no binder is used.
原料のバイオマスとして、(30wt%アーモンド殻+70wt%アーモンド古木)を用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例D-1~例D-4:PBT)。ボールミル粉砕性については上記例Bと同様の方法で測定した。加熱工程後に得られたバイオマス固体燃料Dの性状を表5及び表6に示す。水中浸漬後の水分は100時間以上の浸漬後(例Dでは168時間)であり、平衡しているものと看做す。また比較例D(WP)についても同様に示した。なお例D-1~例D-4、比較例Dいずれもバインダーは不使用である。 <Example D>
The raw material biomass was heated to the target temperature (heating temperature described in Table 5) and heated (Example D-1) in the same manner as in Example A, except that (30 wt% almond shell + 70 wt% almond old wood) was used. -Example D-4: PBT). The ball mill grindability was measured by the same method as in Example B above. Tables 5 and 6 show properties of the biomass solid fuel D obtained after the heating step. The water after immersion in water is assumed to be balanced after immersion for 100 hours or more (168 hours in Example D). The same applies to Comparative Example D (WP). In Examples D-1 to D-4 and Comparative Example D, no binder is used.
原料のバイオマスとしてアカシア木部を用い、バイオマスをタブレット形状に成型し、加熱装置としてφ70mmの管状炉を用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例E-1~例E-3:PBT)。加熱工程後に得られたバイオマス固体燃料Eの性状を表5及び表6に示す。水中浸漬後の水分は100時間以上の浸漬後(例Eでは168時間)であり、平衡しているものと看做す。また比較例E(WP)についても同様に示す。なお例E-1~例E-3、比較例Eいずれもバインダーは不使用である。例EにおいてpHの測定は、固体燃料を固液比1:13で浸漬して測定した。ここで、表6における比較例Eの浸漬時間はpHを測定した時間、すなわち比較例Eを浸漬して96時間経過後のpHを測定したことを示す。 <Example E>
The temperature was increased to the target temperature (heating temperature described in Table 5) in the same manner as in Example A, except that Acacia xylem was used as the raw material biomass, the biomass was molded into a tablet shape, and a φ70 mm tubular furnace was used as the heating device. Warmed and heated (Example E-1 to Example E-3: PBT). Properties of the biomass solid fuel E obtained after the heating step are shown in Tables 5 and 6. The water after immersion in water is considered to be balanced after immersion for 100 hours or more (168 hours in Example E). The same applies to Comparative Example E (WP). In Examples E-1 to E-3 and Comparative Example E, no binder is used. In Example E, the pH was measured by immersing the solid fuel at a solid-liquid ratio of 1:13. Here, the immersion time of Comparative Example E in Table 6 indicates that the pH was measured, that is, the pH after 96 hours had elapsed after Comparative Example E was immersed.
原料のバイオマスとしてアカシアバークを用いた以外は、例Eと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例F-1~例F-4:PBT)。加熱工程後に得られたバイオマス固体燃料Fの性状を表5及び表6に示す。水中浸漬後の水分は100時間以上の浸漬後(例Fでは168時間以上)であり、平衡しているものと看做す。また比較例F(WP)についても同様に示す。なお例F-1~例F-4、比較例Fいずれもバインダーは不使用である。例FにおいてpHの測定は、固体燃料を固液比1:13で浸漬して測定した。ここで、表6における比較例Fの浸漬時間はpHを測定した時間、すなわち比較例Fを浸漬して96時間経過後のpHを測定したことを示す。 <Example F>
The temperature was raised to the target temperature (heating temperature described in Table 5) and heated (Example F-1 to Example F-4: PBT) in the same manner as in Example E except that acacia bark was used as the raw material biomass. Tables 5 and 6 show the properties of the solid biomass fuel F obtained after the heating step. The water after immersion in water is considered to be balanced after immersion for 100 hours or more (168 hours or more in Example F). The same applies to Comparative Example F (WP). In Examples F-1 to F-4 and Comparative Example F, no binder is used. In Example F, the pH was measured by immersing the solid fuel at a solid-liquid ratio of 1:13. Here, the immersion time of Comparative Example F in Table 6 indicates that the pH was measured, that is, the pH after 96 hours had elapsed after Comparative Example F was immersed.
原料のバイオマスとして(70wt%アーモンド殻+30wt%胡桃殻)を用い、加熱装置としてφ70mmの管状炉を用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例G-1~例G-4:PBT)。加熱工程後に得られたバイオマス固体燃料Gの性状を表5及び表6に示す。水中浸漬後の水分は100時間以上の浸漬後(例Gでは144時間以上)であり、平衡しているものと看做す。比較例G(WP)についても同様に示す。なお例G-1~例G-4、比較例Gいずれもバインダーは不使用である。 <Example G>
The temperature was raised to the target temperature (heating temperature described in Table 5) in the same manner as in Example A except that (70 wt% almond shell + 30 wt% walnut shell) was used as the raw material biomass and a φ70 mm tubular furnace was used as the heating device. And heated (Example G-1 to Example G-4: PBT). Properties of the biomass solid fuel G obtained after the heating step are shown in Tables 5 and 6. Water after immersion in water is considered to be in equilibrium after being immersed for 100 hours or longer (144 hours or longer in Example G). The same applies to Comparative Example G (WP). In Examples G-1 to G-4 and Comparative Example G, no binder is used.
原料のバイオマスとしてサゴヤシを用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例H-1~例H-4:PBT)。ボールミル粉砕性については上記例Bと同様の方法で測定した。加熱工程後に得られたバイオマス固体燃料Hの性状を表5及び表6に示す。水中浸漬後の水分は100時間以上の浸漬後(例Hでは168時間)であり、平衡しているものと看做す。比較例H(WP)についても同様に示す。なお例H-1~例H-4、比較例Hいずれもバインダーは不使用である。表6における比較例Hの浸漬時間はpHを測定した時間、すなわち比較例Hを浸漬して24時間経過後のpHを測定したことを示す。 <Example H>
The sample was heated to the target temperature (heating temperature described in Table 5) and heated (Example H-1 to Example H-4: PBT) in the same manner as in Example A, except that sago palm was used as the raw material biomass. The ball mill grindability was measured by the same method as in Example B above. Properties of the biomass solid fuel H obtained after the heating step are shown in Tables 5 and 6. The water after immersion in water is considered to be balanced after immersion for 100 hours or more (168 hours in Example H). The same applies to Comparative Example H (WP). In Examples H-1 to H-4 and Comparative Example H, no binder is used. The immersion time of Comparative Example H in Table 6 indicates that the pH was measured, that is, the pH after 24 hours had elapsed after Comparative Example H was immersed.
原料のバイオマスとしてEFB(パーム油加工残渣の空果房)を用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例I-1~例I-4:PBT)。加熱工程後に得られたバイオマス固体燃料Iの性状を表5及び表6に示す。水中浸漬後の水分は100時間以上の浸漬後(例Iでは168時間)であり、平衡しているものと看做す。比較例I(WP)についても同様に示す。なお例I-1~例I-4、比較例Iいずれもバインダーは不使用である。 <Example I>
The sample was heated to the target temperature (heating temperature described in Table 5) and heated (Example I-1) in the same manner as in Example A, except that EFB (empty fruit bunch of palm oil processing residue) was used as the raw material biomass. ~ Example I-4: PBT). Properties of the biomass solid fuel I obtained after the heating step are shown in Tables 5 and 6. The water after immersion in water is assumed to be balanced after immersion for 100 hours or more (168 hours in Example I). The same applies to Comparative Example I (WP). In Examples I-1 to I-4 and Comparative Example I, no binder is used.
DU=(m1/m0)×100
により機械的耐久性(DU)を算出した。式中、m0は回転処理前の試料重量、m1は回転処理後の篩上試料重量である。 The mechanical durability before and after immersion in water for Example I-3 heated at 270 ° C. and Example I-4 heated at 300 ° C. was measured by the following method. A sample of 50 g is filled in a 1,000 cc polypropylene container, and is rotated with a MISUGI mixing man SKH-15DT at 60 rpm for 30 minutes (total 1,800 revolutions). The sample after rotation is sieved with a sieve having a circular hole diameter of 3.15 mm, and the following formula:
DU = (m1 / m0) × 100
Was used to calculate mechanical durability (DU). In the formula, m0 is the sample weight before the rotation treatment, and m1 is the sample weight on the sieve after the rotation treatment.
原料のバイオマスとしてメランティを用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例J-1、例J-2:PBT)。加熱工程後に得られたバイオマス固体燃料Jの性状を表5及び表6に示す。水中浸漬後の水分は100時間以上の浸漬後(例Jでは168時間)であり、平衡しているものと看做す。比較例J(WP)についても同様に示す。なお例J-1、例J-2、および比較例Jいずれもバインダーは不使用である。 <Example J>
The sample was heated to the target temperature (heating temperature described in Table 5) and heated (Example J-1, Example J-2: PBT) in the same manner as in Example A except that Meranti was used as the raw material biomass. Properties of the biomass solid fuel J obtained after the heating step are shown in Tables 5 and 6. The water after immersion in water is considered to be balanced after immersion for 100 hours or more (168 hours in Example J). The same applies to Comparative Example J (WP). In all of Examples J-1, J-2, and Comparative Example J, no binder is used.
原料のバイオマスとしてゴムの木を用い、加熱装置としてφ70mmの管状炉を用いた以外は、例Aと同様にして目標温度(表5に記載の加熱温度)まで昇温させ、加熱した(例K-1)。加熱工程後に得られたバイオマス固体燃料Kの性状を表5に示す。比較例K(WP)についても同様に示す。いずれもバインダーは不使用である。 <Example K>
The sample was heated to the target temperature (heating temperature described in Table 5) and heated (Example K) in the same manner as in Example A, except that a rubber tree was used as the raw material biomass and a φ70 mm tubular furnace was used as the heating device. -1). Table 5 shows properties of the biomass solid fuel K obtained after the heating step. The same applies to Comparative Example K (WP). In any case, no binder is used.
PATとPBTの耐水性を比較するため、これらバイオマス固体燃料について、食塩水を用いて、吸水後のナトリウムの分布を調べた。PATの試料としては、原料の欧州アカマツを250℃で加熱した後直径6mmのペレットに成型した固体燃料を用いた。PBTの試料としては、原料の欧州アカマツを直径6mmのペレットに成型した後250℃で加熱した固体燃料(固体燃料B)を用いた。PBTとPATを0.9wt%の生理食塩水に5日間浸漬した。その結果、ペレット外観は図24に示したとおり、PBTはペレット形状を保持した(図24の左)が、PATは大きく崩壊した(図24の右)。また、PATおよびPBTを、それぞれ、生理食塩水に浸漬する前と0.9wt%の生理食塩水に5日間浸漬後について、その断面をEPMA(Electron Probe MicroAnalyser)分析にかけ、Na分布を比較した。Na分布は、PBTはペレット表面にとどまり内部に浸透していないのに対し、PATでは内部にまで広く分布していた(図25参照)。これはPBTの方がPATより生理食塩水の浸入が少ないことを意味する。この結果からも、PBTは隣接するバイオマス粉同士の間隙を抽出成分の熱分解物が固架橋し、疎水性になったために水の侵入を防いでいるのに対し、PATでは、バイオマス粉同士の間隙に水が浸入できるため水がペレット内部にまで浸透し、バイオマス粉同士の間隙を押し広げた結果、崩壊に至ったと推察される。 <Water absorption distribution>
In order to compare the water resistance of PAT and PBT, the distribution of sodium after water absorption was examined for these biomass solid fuels using saline. As a sample of PAT, a solid fuel obtained by heating a raw European red pine at 250 ° C. and then molding the pellet into a pellet having a diameter of 6 mm was used. As a PBT sample, a solid fuel (solid fuel B) heated at 250 ° C. after forming a raw red pine as a 6 mm diameter pellet was used. PBT and PAT were immersed in 0.9 wt% physiological saline for 5 days. As a result, as shown in FIG. 24, the PBT retained the pellet shape (left in FIG. 24), but the PAT collapsed greatly (right in FIG. 24). Further, before immersion of PAT and PBT in physiological saline and after immersion in 0.9 wt% physiological saline for 5 days, the sections were subjected to EPMA (Electron Probe MicroAnalyzer) analysis, and the Na distribution was compared. As for Na distribution, PBT remained on the pellet surface and did not penetrate inside, whereas PAT was widely distributed even inside (see FIG. 25). This means that PBT has less saline intrusion than PAT. Also from this result, PBT prevents the invasion of water because the pyrolysis product of the extraction component is solid-crosslinked in the gap between adjacent biomass powders and becomes hydrophobic. Since water can penetrate into the gap, water penetrates to the inside of the pellet, and as a result of pushing the gap between the biomass powders, it is assumed that it has collapsed.
例A-1、A-3の固体燃料につき水中浸漬前後のペレット長さを測定した。ペレット長さについては、浸漬前のペレットを10個選択し、電子ノギス(ミツトヨ製:CD-15CX、繰り返し精度は0.01mmであり小数点2桁の部分を四捨五入した。)により測定するとともに、同じペレットを72時間水中浸漬させた後、再度電子ノギスにより長さを測定した。なお浸漬前後いずれにおいてもペレット端が斜めの場合は最も先端部分までを長さとして計測した。計測結果を表7に示す。表7に示すとおり、例A-1のペレット長さは平均で4.6%、例A-3は平均で0.2%増加した。 [Expansion coefficient before and after immersion in water]
The pellet length before and after immersion in water was measured for the solid fuels of Examples A-1 and A-3. For the pellet length, 10 pellets before immersion were selected and measured with an electronic caliper (Mitutoyo: CD-15CX, the repeatability was 0.01 mm, and the two decimal places were rounded off) and the same. After immersing the pellet in water for 72 hours, the length was measured again with an electronic caliper. In addition, when the pellet end was slanted before and after immersion, the length up to the tip was measured. Table 7 shows the measurement results. As shown in Table 7, the pellet length of Example A-1 increased by an average of 4.6%, and Example A-3 increased by an average of 0.2%.
2 振動コンベア
11 温度計
21 分級部(分級手段)
22 冷却部(冷却手段)
22a 散水部(散水手段)
22b 平板
24 隔成部
30 制御部(制御手段)
100 燃料製造工程
110 粉砕工程
120 成型工程
130 加熱工程
200 分級工程
300 冷却工程
402 システム
403A 振動篩装置
403B 冷却振動コンベア
421 分級部
421a 篩
421b 排出部
422 冷却部
422a 散水部
422b 平板 DESCRIPTION OF
22 Cooling unit (cooling means)
22a Watering part (watering means)
22b
100
Claims (5)
- バイオマス成型体を炭化してバイオマス炭化物を得る炭化炉と、
前記炭化炉の下流側に設けられ、前記バイオマス炭化物を分級する分級手段と、
前記分級手段の下流側に設けられ、分級された前記バイオマス炭化物を冷却する冷却手段と
を備え、
前記バイオマス成型体は、原料のバイオマスを粉砕した後成型して得られた成型体であって、
前記冷却手段は、散水により前記バイオマス炭化物を冷却すること
を特徴とするバイオマス炭化物の冷却装置。 A carbonization furnace for carbonizing a biomass molded body to obtain biomass carbide,
A classification means provided on the downstream side of the carbonization furnace for classifying the biomass carbide;
A cooling means provided on the downstream side of the classification means, and for cooling the classified biomass carbide,
The biomass molded body is a molded body obtained by pulverizing raw material biomass and then molding,
The said cooling means cools the said biomass carbide | carbonized_material by watering. The cooling device of the biomass carbide | carbonized_material characterized by the above-mentioned. - 請求項1に記載のバイオマス炭化物の冷却装置において、
前記冷却手段は、振動する平板と、この平板上に散水する散水部と、を有し、
前記平板は金属板または樹脂板であって、振動により前記バイオマス炭化物を搬送すること
を特徴とするバイオマス炭化物の冷却装置。 The biomass carbide cooling device according to claim 1,
The cooling means has a vibrating plate and a watering part that sprays water on the plate,
The said flat plate is a metal plate or a resin plate, and conveys the said biomass carbide | carbonized_material by vibration, The biomass carbide | carbonized_material cooling device characterized by the above-mentioned. - 請求項1または請求項2に記載のバイオマス炭化物の冷却装置において、
前記炭化炉出口の温度を計測する温度計を設け、
前記温度計により計測された温度が所定値以下となった場合、前記散水手段を停止する制御手段を設けたこと
を特徴とするバイオマス炭化物の冷却装置。 In the biomass carbide cooling device according to claim 1 or 2,
A thermometer for measuring the temperature of the carbonization furnace outlet is provided,
A biomass carbide cooling apparatus, comprising: a control unit that stops the watering unit when the temperature measured by the thermometer becomes a predetermined value or less. - 請求項3に記載のバイオマス炭化物の冷却装置において、
前記温度計は、前記バイオマス炭化物の温度を直接計測可能であること
を特徴とするバイオマス炭化物の冷却装置。 The biomass carbide cooling device according to claim 3,
The said thermometer can directly measure the temperature of the said biomass carbide | carbonized_material. The cooling device of the biomass carbide | carbonized_material characterized by the above-mentioned. - 請求項1ないし請求項4のいずれか1項に記載のバイオマス炭化物の製造装置において、
前記分級手段と前記冷却手段とを隔成する隔成部を設けたこと
を特徴とするバイオマス炭化物の冷却装置。 In the biomass carbide manufacturing apparatus according to any one of claims 1 to 4,
A biomass carbide cooling apparatus, comprising: a separating section that separates the classification means and the cooling means.
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NZ747132A NZ747132B2 (en) | 2016-04-06 | 2017-04-03 | Cooling apparatus for carbonized biomass |
RU2018138556A RU2746733C2 (en) | 2016-04-06 | 2017-04-03 | Carbonized biomass cooling equipment |
AU2017247757A AU2017247757B2 (en) | 2016-04-06 | 2017-04-03 | Cooling apparatus for carbonized biomass |
KR1020187031771A KR20180133445A (en) | 2016-04-06 | 2017-04-03 | Cooling system of biomass carbide |
MYPI2018001688A MY189949A (en) | 2016-04-06 | 2017-04-03 | Cooling apparatus for carbonized biomass |
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WO2020184698A1 (en) * | 2019-03-13 | 2020-09-17 | 日本製紙株式会社 | Method for producing solid fuel |
WO2020184699A1 (en) * | 2019-03-13 | 2020-09-17 | 日本製紙株式会社 | Method for producing solid fuel |
JP7473529B2 (en) | 2019-03-13 | 2024-04-23 | 日本製紙株式会社 | Method for producing solid fuel |
WO2020203163A1 (en) * | 2019-03-29 | 2020-10-08 | 日本製紙株式会社 | Method for producing solid fuel |
JP7474750B2 (en) | 2019-03-29 | 2024-04-25 | 日本製紙株式会社 | Method for producing solid fuel |
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Also Published As
Publication number | Publication date |
---|---|
NZ747132A (en) | 2021-11-26 |
JPWO2017175737A1 (en) | 2019-02-14 |
MY189949A (en) | 2022-03-22 |
KR20180133445A (en) | 2018-12-14 |
JP7080168B2 (en) | 2022-06-03 |
RU2746733C2 (en) | 2021-04-19 |
US20190112530A1 (en) | 2019-04-18 |
CA3020513A1 (en) | 2017-10-12 |
AU2017247757A1 (en) | 2018-11-01 |
RU2018138556A3 (en) | 2020-05-12 |
RU2018138556A (en) | 2020-05-12 |
AU2017247757B2 (en) | 2020-02-20 |
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