US20040060236A1 - Apparatus for gasifying solid fuel - Google Patents
Apparatus for gasifying solid fuel Download PDFInfo
- Publication number
- US20040060236A1 US20040060236A1 US10/250,681 US25068103A US2004060236A1 US 20040060236 A1 US20040060236 A1 US 20040060236A1 US 25068103 A US25068103 A US 25068103A US 2004060236 A1 US2004060236 A1 US 2004060236A1
- Authority
- US
- United States
- Prior art keywords
- gas
- pyrolyzer
- pyrolysis gas
- solid fuel
- steam
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Abandoned
Links
- 239000004449 solid propellant Substances 0.000 title claims abstract description 55
- 239000007789 gas Substances 0.000 claims abstract description 203
- 238000000197 pyrolysis Methods 0.000 claims abstract description 98
- 238000002485 combustion reaction Methods 0.000 claims abstract description 75
- 238000002407 reforming Methods 0.000 claims abstract description 50
- 239000002737 fuel gas Substances 0.000 claims abstract description 32
- 239000003779 heat-resistant material Substances 0.000 claims abstract description 23
- 230000004888 barrier function Effects 0.000 claims abstract description 17
- 238000000629 steam reforming Methods 0.000 claims abstract description 15
- 238000005979 thermal decomposition reaction Methods 0.000 claims abstract description 14
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 10
- 239000001301 oxygen Substances 0.000 claims abstract description 10
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 10
- 238000004891 communication Methods 0.000 claims abstract description 5
- 238000007664 blowing Methods 0.000 claims abstract description 3
- 239000000919 ceramic Substances 0.000 claims description 27
- 238000010438 heat treatment Methods 0.000 claims description 14
- 239000000446 fuel Substances 0.000 claims description 9
- 239000007787 solid Substances 0.000 claims 2
- 239000002699 waste material Substances 0.000 description 56
- 238000002309 gasification Methods 0.000 description 24
- 239000004215 Carbon black (E152) Substances 0.000 description 16
- 229930195733 hydrocarbon Natural products 0.000 description 16
- 150000002430 hydrocarbons Chemical class 0.000 description 16
- 239000004033 plastic Substances 0.000 description 9
- 229920003023 plastic Polymers 0.000 description 9
- 238000006243 chemical reaction Methods 0.000 description 8
- 238000010276 construction Methods 0.000 description 8
- 238000002156 mixing Methods 0.000 description 8
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 6
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 6
- 229910002091 carbon monoxide Inorganic materials 0.000 description 6
- 239000001257 hydrogen Substances 0.000 description 6
- 229910052739 hydrogen Inorganic materials 0.000 description 6
- 230000015572 biosynthetic process Effects 0.000 description 5
- 239000003245 coal Substances 0.000 description 5
- 238000005755 formation reaction Methods 0.000 description 5
- 238000002844 melting Methods 0.000 description 5
- 230000008018 melting Effects 0.000 description 5
- 239000000203 mixture Substances 0.000 description 5
- 239000012530 fluid Substances 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- 239000002028 Biomass Substances 0.000 description 3
- 230000009471 action Effects 0.000 description 3
- 239000000428 dust Substances 0.000 description 3
- -1 e.g. Substances 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 230000009467 reduction Effects 0.000 description 3
- 238000006057 reforming reaction Methods 0.000 description 3
- 238000009825 accumulation Methods 0.000 description 2
- 238000003763 carbonization Methods 0.000 description 2
- 238000006298 dechlorination reaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000010812 mixed waste Substances 0.000 description 2
- 238000005192 partition Methods 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 230000035484 reaction time Effects 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- 239000004071 soot Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000013589 supplement Substances 0.000 description 2
- 230000001502 supplementing effect Effects 0.000 description 2
- 238000011144 upstream manufacturing Methods 0.000 description 2
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N Alumina Chemical compound [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 239000010796 biological waste Substances 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- 239000002657 fibrous material Substances 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 239000011147 inorganic material Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 239000008188 pellet Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 238000005201 scrubbing Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 229920003002 synthetic resin Polymers 0.000 description 1
- 239000000057 synthetic resin Substances 0.000 description 1
- 238000002303 thermal reforming Methods 0.000 description 1
- 238000009827 uniform distribution Methods 0.000 description 1
Images
Classifications
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B3/00—Hydrogen; Gaseous mixtures containing hydrogen; Separation of hydrogen from mixtures containing it; Purification of hydrogen
- C01B3/02—Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen
- C01B3/32—Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen by reaction of gaseous or liquid organic compounds with gasifying agents, e.g. water, carbon dioxide, air
- C01B3/34—Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen by reaction of gaseous or liquid organic compounds with gasifying agents, e.g. water, carbon dioxide, air by reaction of hydrocarbons with gasifying agents
- C01B3/38—Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen by reaction of gaseous or liquid organic compounds with gasifying agents, e.g. water, carbon dioxide, air by reaction of hydrocarbons with gasifying agents using catalysts
- C01B3/382—Multi-step processes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J12/00—Chemical processes in general for reacting gaseous media with gaseous media; Apparatus specially adapted therefor
- B01J12/005—Chemical processes in general for reacting gaseous media with gaseous media; Apparatus specially adapted therefor carried out at high temperatures, e.g. by pyrolysis
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J6/00—Heat treatments such as Calcining; Fusing ; Pyrolysis
- B01J6/008—Pyrolysis reactions
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J8/00—Chemical or physical processes in general, conducted in the presence of fluids and solid particles; Apparatus for such processes
- B01J8/02—Chemical or physical processes in general, conducted in the presence of fluids and solid particles; Apparatus for such processes with stationary particles, e.g. in fixed beds
- B01J8/0242—Chemical or physical processes in general, conducted in the presence of fluids and solid particles; Apparatus for such processes with stationary particles, e.g. in fixed beds the fluid flow within the bed being predominantly vertical
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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
- C10B49/00—Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated
- C10B49/02—Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated with hot gases or vapours, e.g. hot gases obtained by partial combustion of the charge
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/02—Fixed-bed gasification of lump fuel
- C10J3/06—Continuous processes
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/02—Fixed-bed gasification of lump fuel
- C10J3/06—Continuous processes
- C10J3/16—Continuous processes simultaneously reacting oxygen and water with the carbonaceous material
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/46—Gasification of granular or pulverulent flues in suspension
- C10J3/466—Entrained flow processes
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/58—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels combined with pre-distillation of the fuel
- C10J3/60—Processes
- C10J3/64—Processes with decomposition of the distillation products
- C10J3/66—Processes with decomposition of the distillation products by introducing them into the gasification zone
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/027—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/027—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
- F23G5/0276—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage using direct heating
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B2203/00—Integrated processes for the production of hydrogen or synthesis gas
- C01B2203/02—Processes for making hydrogen or synthesis gas
- C01B2203/0205—Processes for making hydrogen or synthesis gas containing a reforming step
- C01B2203/0227—Processes for making hydrogen or synthesis gas containing a reforming step containing a catalytic reforming step
- C01B2203/0244—Processes for making hydrogen or synthesis gas containing a reforming step containing a catalytic reforming step the reforming step being an autothermal reforming step, e.g. secondary reforming processes
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B2203/00—Integrated processes for the production of hydrogen or synthesis gas
- C01B2203/08—Methods of heating or cooling
- C01B2203/0872—Methods of cooling
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B2203/00—Integrated processes for the production of hydrogen or synthesis gas
- C01B2203/12—Feeding the process for making hydrogen or synthesis gas
- C01B2203/1205—Composition of the feed
- C01B2203/1211—Organic compounds or organic mixtures used in the process for making hydrogen or synthesis gas
- C01B2203/1235—Hydrocarbons
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B2203/00—Integrated processes for the production of hydrogen or synthesis gas
- C01B2203/80—Aspect of integrated processes for the production of hydrogen or synthesis gas not covered by groups C01B2203/02 - C01B2203/1695
- C01B2203/84—Energy production
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2200/00—Details of gasification apparatus
- C10J2200/15—Details of feeding means
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0913—Carbonaceous raw material
- C10J2300/0916—Biomass
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0913—Carbonaceous raw material
- C10J2300/093—Coal
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0913—Carbonaceous raw material
- C10J2300/0946—Waste, e.g. MSW, tires, glass, tar sand, peat, paper, lignite, oil shale
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0953—Gasifying agents
- C10J2300/0956—Air or oxygen enriched air
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0953—Gasifying agents
- C10J2300/0973—Water
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0983—Additives
- C10J2300/0993—Inert particles, e.g. as heat exchange medium in a fluidized or moving bed, heat carriers, sand
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/12—Heating the gasifier
- C10J2300/1215—Heating the gasifier using synthesis gas as fuel
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/16—Integration of gasification processes with another plant or parts within the plant
- C10J2300/1603—Integration of gasification processes with another plant or parts within the plant with gas treatment
- C10J2300/1606—Combustion processes
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/16—Integration of gasification processes with another plant or parts within the plant
- C10J2300/1671—Integration of gasification processes with another plant or parts within the plant with the production of electricity
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/30—Pyrolysing
- F23G2201/301—Treating pyrogases
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/40—Gasification
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2900/00—Special features of, or arrangements for incinerators
- F23G2900/50204—Waste pre-treatment by pyrolysis, gasification or cracking
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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
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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
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Definitions
- the present invention relates to an apparatus for gasifiying solid fuel, and more specifically, to such an apparatus producing pyrolysis gas by a thermal-decomposition reaction and reforming the pyrolysis gas to crude fuel gas.
- An apparatus for gasifiying solid fuel which has a pyrolyzer or thermal-decomposition furnace charged with solid fuel, such as waste, e.g., waste plastic, sludge, shredder dust, or municipal refuse, or coal or the like.
- solid fuel such as waste, e.g., waste plastic, sludge, shredder dust, or municipal refuse, or coal or the like.
- the solid fuel is thermally decomposed to produce pyrolysis gas in reducing atmosphere of a non or less oxygen condition at a high temperature.
- combustion furnaces or incinerators may be generally used as the pyrolyzer, such as a waste gasification melting furnace, a coal gasifier, a rotary kiln type of pyrolyzer (an external heating type of pyrolyzer), a batch type of pyrolyzer (a self-burning type of pyrolyzer) and so forth.
- the present inventor et al. have recently developed a waste gasification melting system which comprises a high-temperature air generator for continuously supplying an amount of hot air at a high temperature exceeding 800° C., and a waste gasification melting furnace (pebble furnace) containing a number of spherical ceramics (pebbles).
- the high temperature air is introduced from a top of the waste gasification melting furnace to the inner area of the furnace downwardly, so that the waste on the spherical ceramics (pebbles) is melted and slagged.
- the molten slag flows downwardly through the gaps of the pebbles to be discharged out of the furnace from the furnace bed part.
- the pyrolysis gas produced by the thermal-decomposition of waste is conducted out of the furnace and introduced into a cleaning-up means or purification means.
- This type of waste gasification melting system can be designed to be relatively small scale equipment and therefore, it has a construction applicable to waste gasification equipment for middle or small scale facilities.
- the waste of a middle or small scale facility usually includes a wide variety of wastes, such as synthetic resin, kitchen refuse, biological waste, fibrous material, inorganic material and so forth.
- waste includes a relatively large amount of waste plastics to be incinerated in a waste gasification furnace as generally in use
- the molten plastic material clings to its furnace bed part. It is apprehensive of condition that the combustion air is prevented from flowing through the furnace bed part into the furnace.
- unburned residue is apt to clingingly deposit on the furnace bed part, which residue is difficult to be removed therefrom.
- the present invention provides an apparatus for gasifying solid fuel which thermally decomposes the solid fuel by a combustion reaction of a low oxygen density so as to produce pyrolysis gas, comprising a solid fuel pyrolyzer and a steam reformer;
- said pyrolyzer has an air inlet positioned at a bottom part thereof to blow combustion air into the pyrolyzer, a bed of the pyrolyzer located above the air inlet, and a pyrolysis gas exit positioned at an upper part of a body of the pyrolyzer and conducting the pyrolysis gas out of the pyrolyzer, the bed being constituted by a layered stack of many spherical heat-resistant materials which form a number of narrow gaps for draft of the combustion air over the whole bed;
- said steam reformer has a reforming area for producing crude fuel gas by a steam reforming reaction of said pyrolysis gas, a pyrolysis gas inlet which is in communication with said pyrolysis gas exit and which introduces the pyrolysis gas into the reforming area, a mixed gas inlet for introducing mixed gas of steam and air into the reforming area, a reformed gas effluent passage for conducting reformed gas of the reforming area out of the reformer, and a permeable heat-barrier positioned between the reforming area and the reformed gas effluent passage, the barrier being constituted by a layered stack of many spherical heat-resistant materials which form a number of narrow gaps for draft of said pyrolysis gas and said mixed gas.
- the present invention provides a pyrolyzer of an apparatus for gasifying solid fuel which thermally decomposes the solid fuel by a combustion reaction of a low oxygen density so as to produce pyrolysis gas, comprising:
- an air inlet positioned at a bottom part of the pyrolyzer and upwardly blowing combustion air into the pyrolyzer; a bed of the pyrolyzer located above the air inlet; and a pyrolysis gas exit positioned at an upper part of a body of the pyrolyzer and conducting the pyrolysis gas out of the pyrolyzer, the bed being constituted by a layered stack of many spherical heat-resistant materials, which form a number of narrow gaps for draft of the combustion air over the whole bed.
- the present invention provides a steam reformer of an apparatus for gasifying solid fuel which reforms pyrolysis gas produced by a thermal-decomposition reaction of the solid fuel, comprising:
- a reforming area which produces crude fuel gas by a steam reforming reaction of said pyrolysis gas; a pyrolysis gas inlet which introduces the pyrolysis gas of the solid fuel pyrolyzer into the reforming area; a mixed gas inlet for introducing mixed gas of steam and air into the reforming area; a reformed gas effluent passage for conducting reformed gas of the reforming area out of the reformer; and a permeable heat-barrier positioned between the reforming area and the reformed gas effluent passage, the barrier being constituted by a layered stack of many spherical heat-resistant materials, which form a number of narrow gaps for draft of said pyrolysis gas and said mixed gas.
- the pyrolyzer blows combustion air thereinto from the bottom part so that the combustion air is introduced into the pyrolyzer through the gaps of the layered stack of spherical heat-resistant materials.
- the narrow gaps of the stack disperse the combustion air uniformly over the whole bed of the pyrolyzer, and the bed blows the combustion air into the pyrolyzer substantially equally from the bottom. Therefore, the dispersibility of air in the pyrolyzer is improved.
- the solid fuel such as waste lying on the bed, is subjected to complete combustion in its lowermost zone, owing to a combustion reaction of a high air ratio, and gasification in its intermediate zone, and further, carbonization in its uppermost zone, owing to reduction combustion of a low air ratio.
- the pyrolysis gas generated from the upper surface of the solid fuel is introduced into the reforming area of the reformer.
- the solid fuel reduces its volume and combustion residue deposits on the bed.
- the lowermost zone of the solid fuel is supplied with combustion air from the gaps of the spherical heat-resistant materials uniformly over the whole bed, and maintains the high temperature atmosphere owing to the heat accumulation effect of the spherical heat-resistant materials at a high temperature.
- the mixed gas of air and steam is introduced into the reforming area of the reformer.
- the heat-barrier permeably separates the reforming area and the reformed gas effluent passage.
- the barrier is constituted in a form of layered stack by a number of spherical heat-resistant materials, the layered stack being provided with a number of narrow gaps for draft of the reformed gas.
- the barrier functions as a heat-insulating partition for preventing the heat of reforming area from being released to the reformed gas effluent passage and thermally insulating the reforming area, and also acts to efficiently disperse the pyrolysis gas and the mixed gas, so as to effectively mix them with each other, thereby achieving reduction in mixing time of the pyrolysis gas and the mixed gas. As the result, the steam reforming reaction is accelerated, and its reaction time is reduced. Also, the barrier acts to trap soot, condensate of tar components and so forth, which are included in the pyrolysis gas, thereby functioning as cleanup means for cleaning-up the reformed gas.
- FIG. 1 is a system flow diagram of a waste gasification apparatus according to a preferred embodiment of the present invention
- FIG. 2 is a vertical cross-sectional view showing constructions of a pyrolyzer and a reformer as shown in FIG. 1;
- FIG. 3 is a vertical cross-sectional view partially illustrating an arrangement of a bed of the pyrolyzer.
- FIG. 4 is a vertical cross-sectional view partially illustrating a structure of a permeable barrier in the reformer.
- Spherical ceramics such as alumina ceramic balls, are preferably used as the aforementioned spherical heat-resistant materials.
- the diameter (outer diameter) of the spherical heat-resistant material is set to be in a range of 5 mm ⁇ 10 mm, preferably in a range of 20 mm ⁇ 100 mm.
- the cross-section of the spherical heat-resistant material is not limited to a round, but may be designed to be an ellipse or a profile of an oblate sphere. In a case where the high temperature air can be set to have a temperature below 500° C., a metal sphere made of stainless steel can be used as the spherical heat-resistant material.
- the mixed gas of air and steam has a temperature equal to or higher than 300° C., preferably, equal to or higher than 400° C.
- normal temperature steam or process steam produced in a steam boiler and normal temperature air of the ambient atmosphere are heated by a heating device or heater to the high temperature, and they are mixed with each other in a predetermined mixture ratio (weight ratio).
- Mixed gas of air and steam at a relatively low temperature may be heated by the heating device.
- the sensible heat of the crude fuel gas after reforming process or the heat of combustion obtained from the combustion reaction of the purified fuel gas may be utilized as a heat source of the heating device for heating the air, steam or mixed gas.
- the solid fuel gasification apparatus is provided with a mixing control device for controlling the mixture ratio of air and steam.
- the air and steam are mixed with each other under control of the mixing control device so that the mixed gas including an appropriate weight ratio of steam is fed to the reforming area.
- the steam and air react with hydrocarbon in the pyrolysis gas, the pyrolysis gas is reformed to be a reformed gas including a relatively large quantity of hydrogen and carbon monoxide, and the reformed gas is conducted out of the reformer through the reformed gas effluent passage as being a crude or unpurified fuel gas.
- the crude fuel gas is introduced into a heat exchanger for heating air of an ambient condition at normal temperature and/or steam at a relatively low temperature, and the normal temperature air and/or steam are heated by the sensible heat of the crude fuel gas.
- the thermal efficiency of the whole system is improved by such utilization of the sensible heat of crude fuel gas.
- the temperature of air fed to the pyrolyzer is set to be preferably equal to or higher than 150° C., if desired, equal to or higher than 300° C.
- the temperature of high temperature air is variably set to suitably meet the operating conditions of the pyrolyzer and the sort of solid fuel, and if desired, the temperature thereof may be set to be 400° C/ ⁇ 1000° C., or otherwise, a temperature above 1000° C.
- the temperature of mixed gas fed to the reformer is variably set to appropriately meet the properties of pyrolysis gas, the temperature of reforming area, the components of crude fuel gas and so forth, and if desired, the temperature of mixed gas may be set to be 700° C. ⁇ 1000° C., or otherwise, a temperature above 1000° C.
- the air in the mixed gas takes an exothermic reaction with hydrocarbon in the pyrolysis gas so as to supplement the heat required for an endothermic reaction between the steam in the mixed gas and the hydrocarbon in the pyrolysis gas.
- the solid fuel gasification apparatus includes a dedusting device, desulfurization device, dechlorination device, denitration device and so forth, as purification means for purifying the crude fuel gas.
- the purified fuel gas or syngas is fed to a combustion device of combustion equipment or thermic engine as being a fuel therefor, and the heat energy of the combustion device causes a power generator to be driven so as to supply electrical energy to instruments or equipment out of the system.
- a combined power generation system or a relatively small scale cogeneration system in which waste is used as a fuel, can be provided by combining the gasifying apparatus of the present invention with a power generating system, such as a gas-turbine power generator system.
- FIG. 1 is a system flow diagram of a waste gasification apparatus which is a preferred embodiment of the present invention.
- the solid fuel a variety of thermally decomposable fuels can be exemplified, such as waste, coal, and biomass fuel.
- the embodiment as described hereinafter relates to a waste gasification apparatus in which a quantity of mixed waste including waste plastics material and the like is used as the solid fuel.
- the waste gasification system comprises a pyrolyzer for thermally decomposing the waste and a reformer for reforming pyrolysis gas of the pyrolyzer to crude fuel gas or unpurified gas.
- the pyrolyzer is connected to a heat exchanger through an air supply passage HA and connected to the reformer through a pyrolysis gas delivery passage PG.
- the reformer is connected to a heat exchanger and a steam/air heating device by means of a reformed gas effluent passage HG and a mixed gas supply passage MG, respectively.
- An amount of waste is charged into the pyrolyzer, and a quantity of high-temperature air heated by the heat exchanger is fed to the pyrolyzer through the air supply passage HA.
- a part of the heated air through the passage HA is, if desired, introduced into the reformer through a branch passage SA.
- the waste is thermally decomposed in the pyrolyzer into pyrolysis gas and residue in the existence of combustion air.
- the pyrolysis gas produced in the pyrolyzer is introduced into the reformer through the pyrolysis gas delivery passage PG.
- the mixed gas of air and steam heated up to a relatively high temperature by the steam/air heating device is fed from its heat exchanger to the reformer through the mixed gas supply passage MG, and the gas is mixed with the pyrolysis gas in the reformer.
- Hydrocarbon contained in the pyrolysis gas reacts with the steam and air.
- the reaction between hydrocarbon and steam is, in general, an endothermic reaction as indicated by the following chemical formula (1), whereas the reaction between hydrocarbon and air is, in general, an exothermic reaction as indicated by the following chemical formula (2):
- the steam reacts with the pyrolysis gas produced by the thermal-decomposition of waste, so that the pyrolysis gas is reformed to a reformed gas (crude or unpurified fuel gas), which contains a relatively large quantity of carbon monoxide and hydrogen.
- a reformed gas which contains a relatively large quantity of carbon monoxide and hydrogen.
- the heat generated by the exothermic reaction between hydrocarbon and air is consumed as the heat required for the endothermic reforming reaction between hydrocarbon and steam.
- the pyrolysis gas reacts with the mixed gas, and the steam reforming reaction proceeds so that the pyrolysis gas is reformed to the crude fuel gas containing a relatively large quantity of carbon monoxide and hydrogen.
- the reformed gas is fed to the heat exchanger to be cooled down by heat exchange with air at a normal temperature, and then, the gas is supplied to a combustion device or internal combustion engine, such as boiler, gas turbine or the like.
- gas cleanup devices (not shown), such as a ceramic filter, gas scrubber, desulfurizer, dechlorination device, denitrizer or the like are installed in the fuel gas supply passage LG.
- the purified reformed gas is supplied to the combustion device or internal combustion engine as a relatively high-quality fuel gas or syngas, and partially supplied to the steam/air heating device.
- the steam/air heating device heats the steam and air by the heat of combustion of the fuel gas.
- the combustion device or internal combustion engine produces heating medium such as steam, or generates electric power by means of the heat of combustion of the fuel gas.
- the heating medium or electric power is supplied to facilities out of the system, as well as partially used as steam or electric power to be supplied to the respective devices within the system.
- FIG. 2 is a cross-sectional view which shows the construction of a pyrolyzer 1 and the construction of a reformer 5 .
- the pyrolyzer 1 comprises a body of pyrolyzer 10 defining a thermal-decomposition area 20 .
- the body 10 is provided with a waste charging port 11 at its top portion and an air inlet 18 at its bottom portion.
- a top closure 13 for shutting the waste charging port 11 closes the port 11 , whereby the substantially closed thermal-decomposition area 20 is formed in the body 10 .
- Spherr 6 ical ceramics 32 is packed in a bottom section of the body 10 , so that a bed of the pyrolyzer 30 for draft of combustion air therethrough is provided at the bottom of the pyrolyzer.
- the diameter of the spherical ceramics 32 is, preferably, predetermined to be in a range of 20 ⁇ 100 mm.
- the diameter of the spherical ceramics 32 is set to be 50 mm.
- a support structure 31 (shown by a phantom line) for supporting the spherical ceramics 32 thereon, such as a mesh or bars, stretches over or bridges the air inlet 18 .
- the spherical ceramics 32 on the support structure 31 and a bottom wall 17 constitute the bed 30 extending throughout the overall area of the bottom of pyrolyzer.
- the air inlet 18 is connected with the air supply passage HA, on which a forced draft blower (not shown) is installed. Combustion air introduced into the air inlet 18 under pressure of the blower upwardly blows into the thermal-decomposition area 20 through gaps among the spherical ceramics 32 . constituting the bed 30 .
- a pyrolysis gas delivery port 15 is formed at an upper portion of the body 10 , and an upstream end of the pyrolysis gas delivery passage PG is connected to the delivery port 15 .
- a downstream end of the passage PG is connected to a pyrolysis gas inlet 55 of the reformer 5 .
- the reformer 5 comprises a reforming vessel part 50 constituting a vertical reactor vessel, and a reformed gas flowing part 70 which conducts the reformed gas to the reformed gas effluent passage HG
- a mixed gas inlet 54 is provided on a top wall 53 or an upper portion of a wall 52 of the reforming vessel part 50 , and a downstream end of the mixed gas supply passage MG is connected to the inlet 54 .
- the wall 52 forms an inner wall surface of the reforming area 51 .
- a support structure 61 (shown by a phantom line), such as a mesh or bars, is provided on the walls 52 to bridge the walls 52 or spread between the walls 52 .
- a permeable heat-barrier 60 constituted by a layered stack of the spherical ceramics 62 is formed on the support structure 61 .
- a horizontal flow passage 71 of the reformed gas flowing part 70 extends beneath the stack 60 .
- the passage 71 continues to a vertical flow passage 72 .
- a downstream side of the barrier 60 which is the underside thereof in this embodiment, is in communication with the passages 70 , 71 .
- the passages 70 , 71 effect an inertial dust collecting action or a gravitational dust collecting action.
- the passages 70 , 71 also act to decompose precursors of dioxin or dioxins in an atmosphere of a low oxygen density at a high temperature, preferably above 640° C., more preferably, above 740° C. Further, the passages 70 , 71 functions as a gas cleanup space for cleaning-up the reformed gas by residence thereof at such a high temperature.
- a top wall 73 of the passage 72 is formed with a reformed gas outlet 74 , and an upstream end of the reformed gas effluent passage HG is connected to the outlet 74 .
- An induced draft blower (not shown) is provided on the fuel gas supply passage LG, and the reformed gas is introduced into the heat exchanger (FIG.1) from the vertical passage 72 through the reformed gas effluent passage HG under the pressure of the blower.
- FIGS. 3 and 4 are vertical cross-sectional views showing constructions of the bed 30 and the heat-barrier 60 .
- a number of the spherical ceramics 32 are placed on the bottom wall 17 and the support structure 31 in a multiple layered formation, and the bed 30 is formed by the spherical ceramics 32 .
- the waste W charged into the thermal-decomposition area 20 through the waste charging port 11 is supported on the bed 30 .
- a number of gaps or openings 35 are formed among the spherical ceramics 32 .
- the stack of spherical ceramics in a multiple layered formation prevents the waste W from gravitationally falling therethrough.
- the gaps 35 form narrow fluid passages which are disposed in a uniformly distributed condition over the whole area of the bed 30 and which irregularly continue to each other. Therefore, the bed 30 constitutes air dispersing means which blows the combustion air introduced into the air inlet 18 , substantially uniformly and upwardly from the whole area of the bed.
- the dynamic pressure of the combustion air introduced into the air inlet 18 is partially converted into the static pressure by the airway resistance of the bed 30 .
- the combustion air passes through the gaps 35 distributed over the whole bed 30 , and evenly flows from the upper surface of the bed 30 into the thermal-decomposition area 20 in a relatively slow velocity.
- the spherical ceramics 32 is in a heat transfer contact with the combustion air at a high temperature passing through the gaps 35 , and absorb the heat thereof to accumulate the sensible heat of the combustion air.
- the spherical ceramics 32 also receive the heat of combustion of the waste and accumulate the heat thereof.
- a number of the spherical ceramics 62 which are placed on the support structure 61 in a multiple layered formation, have substantially the same construction as the bed 30 has.
- the stack of spherical ceramics in a multiple layered formation constitutes the permeable heat-barrier 60 which partitions the reforming area 51 .
- the gaps 65 of the barrier 60 provide narrow passages which are disposed in a uniform distribution over the whole area of the barrier 60 and which irregularly continue to each other. Therefore, the pyrolysis gas and the hot mixed gas flowing into the reforming area 51 disperse to the respective narrow fluid passages of the barrier 60 and effectively mix with each other in the respective narrow fluid passages.
- the steam reforming reaction of hydrocarbon in the pyrolysis gas and the steam proceeds effectively while the hot gases pass through the gaps 65 of the barrier 60 , and the reaction time of the steam reforming reaction is reduced.
- the barrier 60 acts to trap soot, condensate of tar components and so forth in the pyrolysis gas, and functions as gas cleanup means for cleaning-up the pyrolysis gas.
- the hydrocarbon in the pyrolysis gas reacts with the steam and air in the high temperature atmosphere, owing to mixing of the pyrolysis gas and the high temperature mixed gas in the reforming area 51 and the gaps 65 , so that the steam reforming reaction of the hydrocarbon in the pyrolysis gas proceeds.
- the spherical ceramics 62 accumulates the heat of the high temperature gases in their heat transfer contact therewith, and the gaps 65 are kept in a high temperature condition.
- the heat-barrier 60 prevents the heat of reforming area 51 from radiating to the horizontal flow passage 71 , and thermally insulates the reforming area 51 so as to keep the reforming area 51 in the high temperature condition.
- the waste which has been, if desired, prepared to be appropriate dimensions or grain sizes, is thrown into the pyrolyzer 1 through the waste charging port 11 , so that the waste W lies on the bed 30 .
- the port 11 is shut by the top cover 13 , and a burner for initial combustion (not shown) is operated, which is provided on the bed portion or wall portion of the pyrolyzer.
- the combustion air is fed to the air inlet 18 through the air supply passage HA.
- the combustion air passes through the gaps 35 among the spherical ceramics of the bed 30 and flows into the thermal-decomposition area 20 , so that initial combustion of the waste starts.
- the substantially closed area above the waste W is kept in a combustion atmosphere of a low oxygen density (low air ratio).
- An oxidation combustion reaction in a condition of a relatively high oxygen density (high air ratio) proceeds at a lowermost portion of the waste W, whereas a reduction combustion reaction in a condition of a relatively low oxygen density proceeds at an uppermost portion of the waste W.
- the formations of the waste W can be classified as illustrated in FIG. 2, in accordance with the process of the combustion reaction.
- the process of the combustion reaction proceeds in different manners in respective layers, i.e., a combustion zone (lowermost layer) W 1 , a gasification zone (intermediate layer) W 2 and a carbonization zone (uppermost layer) W 3 .
- the pyrolysis gas generated from an upper surface of the waste W is conducted through the pyrolysis gas delivery port 15 to the pyrolysis gas delivery passage PG, and the gas enters into the reforming area 51 through the pyrolysis gas inlet 55 .
- the mixed gas of air and steam at a relatively high temperature has been introduced into the reforming area 51 through the mixed gas supply passage MG, so that the reforming area 51 and the barrier 60 have been preheated to raise the temperature and accumulate the heat.
- the pyrolysis gas of the pyrolyzer 1 initially mixes with the mixed gas in the reforming area 51 and then, mixes effectively therewith while passing through the gaps 65 .
- the hydrocarbon contained in the pyrolysis gas reacts with the steam and air under the condition of high temperature atmosphere, whereby the pyrolysis gas is reformed into crude fuel gas containing a relatively large amount of carbon monoxide and hydrogen with the steam reforming reaction of the hydrocarbon.
- the pyrolysis gas has a temperature of approximately 200 ⁇ 300° C.
- the mixed gas has a temperature equal to or higher than 300° C., preferably, a temperature equal to or higher than 400° C.
- the air in the mixed gas reacts with the hydrocarbon in the pyrolysis gas so as to supplement the heat required for reforming reaction between the steam in the mixed gas and the hydrocarbon in the pyrolysis gas. Inclusion of excessive quantity of air in the mixed gas results in greater loss of useful fuel components (carbon monoxide and hydrogen) in the reformed gas. Therefore, the quantity of air in the mixed gas is preferably limited to a minimum quantity necessary for supplementing the heat required for the steam reforming reaction.
- the mixing ratio of air and steam is set to be a predetermined ratio in a range from 2:8 to 7:3, e.g., 5:5.
- the crude fuel gas produced by the reforming reaction flows through the gaps 65 of the spherical ceramics of the barrier 60 down to the horizontal flow passage 71 and exits to the reformed gas effluent passage HG through the vertical flow passage 72 .
- the volume of the waste W is reduced and combustion residue deposits on the bed 30 .
- the lowermost zone of the waste W is supplied with the combustion air through the gaps 35 of the spherical ceramics and keeps its atmosphere of a high temperature by the heat accumulation effect of the spherical ceramics 30 , so that the oxidizing combustion reaction of the waste is promoted.
- Molten waste plastics and the like in the waste W are subjected to re-combustion in the gaps 35 . Therefore, incinerated ash after perfect or complete combustion lies on the bed 30 , and after combustion operation of the pyrolyzer 1 is stopped, incinerated ash remaining on the bed 30 can be relatively easily discharged.
- spherical ceramic forms are employed in the aforementioned embodiment, spherical metal forms may be used as the spherical heat-resistant materials.
- any type of heat exchanger or heater may be employed as the heat exchanger and the air/steam heating device as set forth above, such as a high performance heat exchanger of a recuperator, metal coil or metal fin type; a high temperature air generator or a high temperature steam generator with use of regenerators of honeycomb structure as disclosed in Japanese patent application No. 10-189 (Japanese patent laid-open publication No. 10-246428), Japanese patent application No. 8-230682 (Japanese patent laid-open publication No. 10-73236) and so forth; or a regenerative type of heat exchanger having a number of pellets, pebbles or ball type regenerators contained therein.
- the gasification apparatus of the present invention can constitute a biomass fuel gasification apparatus or a coal gasification apparatus with use of biomass fuel or coal as the solid fuel.
- a relatively small scale apparatus for gasifying solid fuel in which the pyrolysis gas produced in the pyrolyzer for solid fuel is successfully reformed to the crude fuel gas.
- a pyrolyzer for solid fuel constituting such an apparatus for gasifying solid fuel can be provided, which can effectively incinerate the waste including a relatively large amount of waste plastics and the like, and which can produce the pyrolysis gas from the waste.
- a steam reformer constituting the aforesaid apparatus for gasifying solid fuel can be provided, which can effectively reform the pyrolysis gas to the crude fuel gas by mixing the pyrolysis gas of the gasifier with the steam.
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Abstract
The present invention provides a relatively small scale apparatus for gasifying solid fuel in which pyrolysis gas produced in a pyrolyzer by thermal-decomposition reaction of the solid fuel can be reformed to crude fuel gas. The apparatus comprises a solid fuel pyrolyzer 1 and a steam reformer 5, and thermally decomposes the solid fuel with a combustion reaction of a low oxygen density to produce the pyrolysis gas, and reforms the pyrolysis gas to produce the crude fuel gas. The pyrolyzer has an air inlet 18 positioned at a bottom part thereof and upwardly blowing combustion air into the pyrolyzer; a bed of pyrolyzer 30 located above the air inlet; and a pyrolysis gas exit positioned at an upper part of a body of the pyrolyzer and conducting the pyrolysis gas out of the pyrolyzer. The bed is made by a layered stack of many spherical heat-resistant materials 32 which form a number of narrow gaps for draft of the combustion air over the whole bed. The steam reformer has a reforming area 51 which produces the crude fuel gas by a steam reforming reaction of the pyrolysis gas, a pyrolysis gas inlet 55 which is in communication with the pyrolysis gas exit and which introduces the pyrolysis gas into the reforming area, a mixed gas inlet 54 introducing mixed gas of steam and air into the reforming area, a reformed gas effluent passage 70 for conducting reformed gas of the reforming area out of the reformer, and a permeable heat-barrier 60 positioned between the reforming area and the reformed gas effluent passage. The barrier is made by a layered stack of many spherical heat-resistant materials 62 which form a number of narrow gaps for draft of the pyrolysis gas and the mixed gas.
Description
- The present invention relates to an apparatus for gasifiying solid fuel, and more specifically, to such an apparatus producing pyrolysis gas by a thermal-decomposition reaction and reforming the pyrolysis gas to crude fuel gas.
- An apparatus for gasifiying solid fuel is known in the art, which has a pyrolyzer or thermal-decomposition furnace charged with solid fuel, such as waste, e.g., waste plastic, sludge, shredder dust, or municipal refuse, or coal or the like. The solid fuel is thermally decomposed to produce pyrolysis gas in reducing atmosphere of a non or less oxygen condition at a high temperature. A variety of combustion furnaces or incinerators may be generally used as the pyrolyzer, such as a waste gasification melting furnace, a coal gasifier, a rotary kiln type of pyrolyzer (an external heating type of pyrolyzer), a batch type of pyrolyzer (a self-burning type of pyrolyzer) and so forth.
- These kinds of solid fuel gasification apparatuses have been developed as being relatively large scale equipment which are continuously operated. Therefore, those apparatuses have constructions which are difficult to be applied to solid fuel gasification equipment of middle scale or small scale facilities, from a viewpoint of the volume of solid fuel, maintenance fees of equipment and so forth.
- The present inventor et al. have recently developed a waste gasification melting system which comprises a high-temperature air generator for continuously supplying an amount of hot air at a high temperature exceeding 800° C., and a waste gasification melting furnace (pebble furnace) containing a number of spherical ceramics (pebbles).
- The high temperature air is introduced from a top of the waste gasification melting furnace to the inner area of the furnace downwardly, so that the waste on the spherical ceramics (pebbles) is melted and slagged. The molten slag flows downwardly through the gaps of the pebbles to be discharged out of the furnace from the furnace bed part. The pyrolysis gas produced by the thermal-decomposition of waste is conducted out of the furnace and introduced into a cleaning-up means or purification means. This type of waste gasification melting system can be designed to be relatively small scale equipment and therefore, it has a construction applicable to waste gasification equipment for middle or small scale facilities.
- However, the waste of a middle or small scale facility usually includes a wide variety of wastes, such as synthetic resin, kitchen refuse, biological waste, fibrous material, inorganic material and so forth. In a case where waste includes a relatively large amount of waste plastics to be incinerated in a waste gasification furnace as generally in use, the molten plastic material clings to its furnace bed part. It is apprehensive of condition that the combustion air is prevented from flowing through the furnace bed part into the furnace. In addition, unburned residue is apt to clingingly deposit on the furnace bed part, which residue is difficult to be removed therefrom. On the other hand, in a case where such waste is incinerated by the aforementioned pebble furnace, the molten plastic materials and so forth tend to block the gaps among the pebbles. Such blockage of the gaps among the pebbles gives an undesirable result in that fluid passages of high temperature air and molten slag are narrowed or restricted.
- Further, in the conventional solid fuel gasification apparatuses, a large amount of sensible heat of pyrolysis gas produced in the gasification furnace is lost in the steps of cleaning-up and purifying the gas in cleaning-up and purifying equipment or a gas scrubbing equipment, and therefore, the thermal efficiency of the whole system is lowered. In order to overcome such a drawback of heat loss and to produce high-quality fuel gas, application of steam reforming process has been studied in which hydrocarbon in the pyrolysis gas is reformed by steam reforming action of high temperature steam above 700° C. However, constructions of reformer or reforming device for mixing the high temperature steam and the pyrolysis gas to reform the pyrolysis gas have not yet concretely studied.
- It is an object of the present invention to provide a relatively small scale apparatus for gasifying solid fuel in which pyrolysis gas produced in a pyrolyzer by a thermal-decomposition reaction of the solid fuel is successfully reformed to crude fuel gas.
- It is another object of the present invention to provide a pyrolyzer for solid fuel constituting such an apparatus for gasifying solid fuel, which can incinerate mixed waste including a relatively large amount of waste plastics and the like, and which can produce the pyrolysis gas therefrom.
- It is still another object of the present invention to provide a steam reformer constituting the aforesaid apparatus for gasifying solid fuel, which successfully reforms the pyrolysis gas to the crude fuel gas by mixing the pyrolysis gas of the pyrolyzer with steam.
- The present invention provides an apparatus for gasifying solid fuel which thermally decomposes the solid fuel by a combustion reaction of a low oxygen density so as to produce pyrolysis gas, comprising a solid fuel pyrolyzer and a steam reformer;
- wherein said pyrolyzer has an air inlet positioned at a bottom part thereof to blow combustion air into the pyrolyzer, a bed of the pyrolyzer located above the air inlet, and a pyrolysis gas exit positioned at an upper part of a body of the pyrolyzer and conducting the pyrolysis gas out of the pyrolyzer, the bed being constituted by a layered stack of many spherical heat-resistant materials which form a number of narrow gaps for draft of the combustion air over the whole bed; and
- wherein said steam reformer has a reforming area for producing crude fuel gas by a steam reforming reaction of said pyrolysis gas, a pyrolysis gas inlet which is in communication with said pyrolysis gas exit and which introduces the pyrolysis gas into the reforming area, a mixed gas inlet for introducing mixed gas of steam and air into the reforming area, a reformed gas effluent passage for conducting reformed gas of the reforming area out of the reformer, and a permeable heat-barrier positioned between the reforming area and the reformed gas effluent passage, the barrier being constituted by a layered stack of many spherical heat-resistant materials which form a number of narrow gaps for draft of said pyrolysis gas and said mixed gas.
- Further, the present invention provides a pyrolyzer of an apparatus for gasifying solid fuel which thermally decomposes the solid fuel by a combustion reaction of a low oxygen density so as to produce pyrolysis gas, comprising:
- an air inlet positioned at a bottom part of the pyrolyzer and upwardly blowing combustion air into the pyrolyzer; a bed of the pyrolyzer located above the air inlet; and a pyrolysis gas exit positioned at an upper part of a body of the pyrolyzer and conducting the pyrolysis gas out of the pyrolyzer, the bed being constituted by a layered stack of many spherical heat-resistant materials, which form a number of narrow gaps for draft of the combustion air over the whole bed.
- Furthermore, the present invention provides a steam reformer of an apparatus for gasifying solid fuel which reforms pyrolysis gas produced by a thermal-decomposition reaction of the solid fuel, comprising:
- a reforming area which produces crude fuel gas by a steam reforming reaction of said pyrolysis gas; a pyrolysis gas inlet which introduces the pyrolysis gas of the solid fuel pyrolyzer into the reforming area; a mixed gas inlet for introducing mixed gas of steam and air into the reforming area; a reformed gas effluent passage for conducting reformed gas of the reforming area out of the reformer; and a permeable heat-barrier positioned between the reforming area and the reformed gas effluent passage, the barrier being constituted by a layered stack of many spherical heat-resistant materials, which form a number of narrow gaps for draft of said pyrolysis gas and said mixed gas.
- According to the present invention, the pyrolyzer blows combustion air thereinto from the bottom part so that the combustion air is introduced into the pyrolyzer through the gaps of the layered stack of spherical heat-resistant materials. The narrow gaps of the stack disperse the combustion air uniformly over the whole bed of the pyrolyzer, and the bed blows the combustion air into the pyrolyzer substantially equally from the bottom. Therefore, the dispersibility of air in the pyrolyzer is improved. The solid fuel, such as waste lying on the bed, is subjected to complete combustion in its lowermost zone, owing to a combustion reaction of a high air ratio, and gasification in its intermediate zone, and further, carbonization in its uppermost zone, owing to reduction combustion of a low air ratio. The pyrolysis gas generated from the upper surface of the solid fuel is introduced into the reforming area of the reformer. As the combustion reaction in the pyrolyzer proceeds, the solid fuel reduces its volume and combustion residue deposits on the bed. However, the lowermost zone of the solid fuel is supplied with combustion air from the gaps of the spherical heat-resistant materials uniformly over the whole bed, and maintains the high temperature atmosphere owing to the heat accumulation effect of the spherical heat-resistant materials at a high temperature. Therefore, the combustion reaction is promoted and the molten components of the solid fuel, such as the plastic material included in the waste, take a re-combustion reaction within the gaps of the spherical heat-resistant materials. Thus, incinerated ash, which can be relatively easily discharged, deposits on the bed as the result of complete combustion, when the combustion operation of the pyrolyzer is stopped.
- The mixed gas of air and steam is introduced into the reforming area of the reformer. The heat-barrier permeably separates the reforming area and the reformed gas effluent passage. The barrier is constituted in a form of layered stack by a number of spherical heat-resistant materials, the layered stack being provided with a number of narrow gaps for draft of the reformed gas. The barrier functions as a heat-insulating partition for preventing the heat of reforming area from being released to the reformed gas effluent passage and thermally insulating the reforming area, and also acts to efficiently disperse the pyrolysis gas and the mixed gas, so as to effectively mix them with each other, thereby achieving reduction in mixing time of the pyrolysis gas and the mixed gas. As the result, the steam reforming reaction is accelerated, and its reaction time is reduced. Also, the barrier acts to trap soot, condensate of tar components and so forth, which are included in the pyrolysis gas, thereby functioning as cleanup means for cleaning-up the reformed gas.
- FIG. 1 is a system flow diagram of a waste gasification apparatus according to a preferred embodiment of the present invention;
- FIG. 2 is a vertical cross-sectional view showing constructions of a pyrolyzer and a reformer as shown in FIG. 1;
- FIG. 3 is a vertical cross-sectional view partially illustrating an arrangement of a bed of the pyrolyzer; and
- FIG. 4 is a vertical cross-sectional view partially illustrating a structure of a permeable barrier in the reformer.
- Spherical ceramics, such as alumina ceramic balls, are preferably used as the aforementioned spherical heat-resistant materials. The diameter (outer diameter) of the spherical heat-resistant material is set to be in a range of 5 mm˜10 mm, preferably in a range of 20 mm˜100 mm. The cross-section of the spherical heat-resistant material is not limited to a round, but may be designed to be an ellipse or a profile of an oblate sphere. In a case where the high temperature air can be set to have a temperature below 500° C., a metal sphere made of stainless steel can be used as the spherical heat-resistant material.
- According to a preferred embodiment of the present invention, the mixed gas of air and steam has a temperature equal to or higher than 300° C., preferably, equal to or higher than 400° C. Preferably, normal temperature steam or process steam produced in a steam boiler and normal temperature air of the ambient atmosphere are heated by a heating device or heater to the high temperature, and they are mixed with each other in a predetermined mixture ratio (weight ratio). Mixed gas of air and steam at a relatively low temperature may be heated by the heating device. The sensible heat of the crude fuel gas after reforming process or the heat of combustion obtained from the combustion reaction of the purified fuel gas may be utilized as a heat source of the heating device for heating the air, steam or mixed gas.
- According to another preferred embodiment of the present invention, the solid fuel gasification apparatus is provided with a mixing control device for controlling the mixture ratio of air and steam. The air and steam are mixed with each other under control of the mixing control device so that the mixed gas including an appropriate weight ratio of steam is fed to the reforming area. In the reforming area, the steam and air react with hydrocarbon in the pyrolysis gas, the pyrolysis gas is reformed to be a reformed gas including a relatively large quantity of hydrogen and carbon monoxide, and the reformed gas is conducted out of the reformer through the reformed gas effluent passage as being a crude or unpurified fuel gas. The crude fuel gas is introduced into a heat exchanger for heating air of an ambient condition at normal temperature and/or steam at a relatively low temperature, and the normal temperature air and/or steam are heated by the sensible heat of the crude fuel gas. The thermal efficiency of the whole system is improved by such utilization of the sensible heat of crude fuel gas.
- The temperature of air fed to the pyrolyzer is set to be preferably equal to or higher than 150° C., if desired, equal to or higher than 300° C. The temperature of high temperature air is variably set to suitably meet the operating conditions of the pyrolyzer and the sort of solid fuel, and if desired, the temperature thereof may be set to be 400° C/˜1000° C., or otherwise, a temperature above 1000° C. Similarly, the temperature of mixed gas fed to the reformer is variably set to appropriately meet the properties of pyrolysis gas, the temperature of reforming area, the components of crude fuel gas and so forth, and if desired, the temperature of mixed gas may be set to be 700° C.˜1000° C., or otherwise, a temperature above 1000° C. The air in the mixed gas takes an exothermic reaction with hydrocarbon in the pyrolysis gas so as to supplement the heat required for an endothermic reaction between the steam in the mixed gas and the hydrocarbon in the pyrolysis gas. However, exceeded inclusion of air in the mixed gas results in an relatively excessive loss of fuel components (carbon monoxide and hydrogen) by reaction thereof with the air, and therefore, it is desirable to limit the amount of air in the mixed gas to the minimum necessary for supplementing the heat of steam reforming reaction. For example, the mixture ratio of air and steam (weight ratio) is limited in a range of 2:8˜7:3.
- According to the other preferred embodiment of the present invention, the solid fuel gasification apparatus includes a dedusting device, desulfurization device, dechlorination device, denitration device and so forth, as purification means for purifying the crude fuel gas. For instance, the purified fuel gas or syngas is fed to a combustion device of combustion equipment or thermic engine as being a fuel therefor, and the heat energy of the combustion device causes a power generator to be driven so as to supply electrical energy to instruments or equipment out of the system. For example, a combined power generation system or a relatively small scale cogeneration system, in which waste is used as a fuel, can be provided by combining the gasifying apparatus of the present invention with a power generating system, such as a gas-turbine power generator system.
- FIG.1 is a system flow diagram of a waste gasification apparatus which is a preferred embodiment of the present invention. As the solid fuel, a variety of thermally decomposable fuels can be exemplified, such as waste, coal, and biomass fuel. The embodiment as described hereinafter relates to a waste gasification apparatus in which a quantity of mixed waste including waste plastics material and the like is used as the solid fuel.
- The waste gasification system comprises a pyrolyzer for thermally decomposing the waste and a reformer for reforming pyrolysis gas of the pyrolyzer to crude fuel gas or unpurified gas. The pyrolyzer is connected to a heat exchanger through an air supply passage HA and connected to the reformer through a pyrolysis gas delivery passage PG. The reformer is connected to a heat exchanger and a steam/air heating device by means of a reformed gas effluent passage HG and a mixed gas supply passage MG, respectively. An amount of waste is charged into the pyrolyzer, and a quantity of high-temperature air heated by the heat exchanger is fed to the pyrolyzer through the air supply passage HA. A part of the heated air through the passage HA is, if desired, introduced into the reformer through a branch passage SA. The waste is thermally decomposed in the pyrolyzer into pyrolysis gas and residue in the existence of combustion air. The pyrolysis gas produced in the pyrolyzer is introduced into the reformer through the pyrolysis gas delivery passage PG.
- The mixed gas of air and steam heated up to a relatively high temperature by the steam/air heating device is fed from its heat exchanger to the reformer through the mixed gas supply passage MG, and the gas is mixed with the pyrolysis gas in the reformer. Hydrocarbon contained in the pyrolysis gas reacts with the steam and air. The reaction between hydrocarbon and steam is, in general, an endothermic reaction as indicated by the following chemical formula (1), whereas the reaction between hydrocarbon and air is, in general, an exothermic reaction as indicated by the following chemical formula (2):
- CxHy+H2O→CO+H2+H2O (1)
- CxHy+O2+N2→CO+CO2+H2+H2O+N2 (2)
- The steam reacts with the pyrolysis gas produced by the thermal-decomposition of waste, so that the pyrolysis gas is reformed to a reformed gas (crude or unpurified fuel gas), which contains a relatively large quantity of carbon monoxide and hydrogen. The heat generated by the exothermic reaction between hydrocarbon and air is consumed as the heat required for the endothermic reforming reaction between hydrocarbon and steam.
- The pyrolysis gas reacts with the mixed gas, and the steam reforming reaction proceeds so that the pyrolysis gas is reformed to the crude fuel gas containing a relatively large quantity of carbon monoxide and hydrogen. The reformed gas is fed to the heat exchanger to be cooled down by heat exchange with air at a normal temperature, and then, the gas is supplied to a combustion device or internal combustion engine, such as boiler, gas turbine or the like. If desired, gas cleanup devices (not shown), such as a ceramic filter, gas scrubber, desulfurizer, dechlorination device, denitrizer or the like are installed in the fuel gas supply passage LG. The purified reformed gas is supplied to the combustion device or internal combustion engine as a relatively high-quality fuel gas or syngas, and partially supplied to the steam/air heating device. The steam/air heating device heats the steam and air by the heat of combustion of the fuel gas. On the other hand, the combustion device or internal combustion engine produces heating medium such as steam, or generates electric power by means of the heat of combustion of the fuel gas. The heating medium or electric power is supplied to facilities out of the system, as well as partially used as steam or electric power to be supplied to the respective devices within the system.
- With reference to FIGS. 2 and 3, an embodiment of the waste gasification apparatus according to the present invention is described in detail hereinafter.
- FIG. 2 is a cross-sectional view which shows the construction of a
pyrolyzer 1 and the construction of areformer 5. - The
pyrolyzer 1 comprises a body ofpyrolyzer 10 defining a thermal-decomposition area 20. Thebody 10 is provided with awaste charging port 11 at its top portion and anair inlet 18 at its bottom portion. Atop closure 13 for shutting thewaste charging port 11 closes theport 11, whereby the substantially closed thermal-decomposition area 20 is formed in thebody 10.Spherr6ical ceramics 32 is packed in a bottom section of thebody 10, so that a bed of thepyrolyzer 30 for draft of combustion air therethrough is provided at the bottom of the pyrolyzer. The diameter of thespherical ceramics 32 is, preferably, predetermined to be in a range of 20˜100 mm. For example, the diameter of thespherical ceramics 32 is set to be 50 mm. A support structure 31 (shown by a phantom line) for supporting thespherical ceramics 32 thereon, such as a mesh or bars, stretches over or bridges theair inlet 18. Thespherical ceramics 32 on thesupport structure 31 and abottom wall 17 constitute thebed 30 extending throughout the overall area of the bottom of pyrolyzer. - The
air inlet 18 is connected with the air supply passage HA, on which a forced draft blower (not shown) is installed. Combustion air introduced into theair inlet 18 under pressure of the blower upwardly blows into the thermal-decomposition area 20 through gaps among thespherical ceramics 32. constituting thebed 30. - A pyrolysis
gas delivery port 15 is formed at an upper portion of thebody 10, and an upstream end of the pyrolysis gas delivery passage PG is connected to thedelivery port 15. A downstream end of the passage PG is connected to apyrolysis gas inlet 55 of thereformer 5. Thereformer 5 comprises a reformingvessel part 50 constituting a vertical reactor vessel, and a reformedgas flowing part 70 which conducts the reformed gas to the reformed gas effluent passage HG Amixed gas inlet 54 is provided on atop wall 53 or an upper portion of awall 52 of the reformingvessel part 50, and a downstream end of the mixed gas supply passage MG is connected to theinlet 54. Thewall 52 forms an inner wall surface of the reformingarea 51. A support structure 61 (shown by a phantom line), such as a mesh or bars, is provided on thewalls 52 to bridge thewalls 52 or spread between thewalls 52. A permeable heat-barrier 60 constituted by a layered stack of thespherical ceramics 62 is formed on thesupport structure 61. - A
horizontal flow passage 71 of the reformedgas flowing part 70 extends beneath thestack 60. Thepassage 71 continues to avertical flow passage 72. A downstream side of thebarrier 60, which is the underside thereof in this embodiment, is in communication with thepassages passages passages passages - A
top wall 73 of thepassage 72 is formed with a reformedgas outlet 74, and an upstream end of the reformed gas effluent passage HG is connected to theoutlet 74. An induced draft blower (not shown) is provided on the fuel gas supply passage LG, and the reformed gas is introduced into the heat exchanger (FIG.1) from thevertical passage 72 through the reformed gas effluent passage HG under the pressure of the blower. - FIGS. 3 and 4 are vertical cross-sectional views showing constructions of the
bed 30 and the heat-barrier 60. - As shown in FIG. 3, a number of the
spherical ceramics 32 are placed on thebottom wall 17 and thesupport structure 31 in a multiple layered formation, and thebed 30 is formed by thespherical ceramics 32. The waste W charged into the thermal-decomposition area 20 through thewaste charging port 11 is supported on thebed 30. A number of gaps oropenings 35 are formed among thespherical ceramics 32. However, the stack of spherical ceramics in a multiple layered formation prevents the waste W from gravitationally falling therethrough. Also, thegaps 35 form narrow fluid passages which are disposed in a uniformly distributed condition over the whole area of thebed 30 and which irregularly continue to each other. Therefore, thebed 30 constitutes air dispersing means which blows the combustion air introduced into theair inlet 18, substantially uniformly and upwardly from the whole area of the bed. - The dynamic pressure of the combustion air introduced into the
air inlet 18 is partially converted into the static pressure by the airway resistance of thebed 30. The combustion air passes through thegaps 35 distributed over thewhole bed 30, and evenly flows from the upper surface of thebed 30 into the thermal-decomposition area 20 in a relatively slow velocity. Thespherical ceramics 32 is in a heat transfer contact with the combustion air at a high temperature passing through thegaps 35, and absorb the heat thereof to accumulate the sensible heat of the combustion air. Thespherical ceramics 32 also receive the heat of combustion of the waste and accumulate the heat thereof. - As illustrated in FIG. 4, a number of the
spherical ceramics 62, which are placed on thesupport structure 61 in a multiple layered formation, have substantially the same construction as thebed 30 has. The stack of spherical ceramics in a multiple layered formation constitutes the permeable heat-barrier 60 which partitions the reformingarea 51. Thegaps 65 of thebarrier 60 provide narrow passages which are disposed in a uniform distribution over the whole area of thebarrier 60 and which irregularly continue to each other. Therefore, the pyrolysis gas and the hot mixed gas flowing into the reformingarea 51 disperse to the respective narrow fluid passages of thebarrier 60 and effectively mix with each other in the respective narrow fluid passages. Thus, the steam reforming reaction of hydrocarbon in the pyrolysis gas and the steam proceeds effectively while the hot gases pass through thegaps 65 of thebarrier 60, and the reaction time of the steam reforming reaction is reduced. Simultaneously, thebarrier 60 acts to trap soot, condensate of tar components and so forth in the pyrolysis gas, and functions as gas cleanup means for cleaning-up the pyrolysis gas. - The hydrocarbon in the pyrolysis gas reacts with the steam and air in the high temperature atmosphere, owing to mixing of the pyrolysis gas and the high temperature mixed gas in the reforming
area 51 and thegaps 65, so that the steam reforming reaction of the hydrocarbon in the pyrolysis gas proceeds. Thespherical ceramics 62 accumulates the heat of the high temperature gases in their heat transfer contact therewith, and thegaps 65 are kept in a high temperature condition. The heat-barrier 60 prevents the heat of reformingarea 51 from radiating to thehorizontal flow passage 71, and thermally insulates the reformingarea 51 so as to keep the reformingarea 51 in the high temperature condition. - The operation of the waste gasification apparatus with the aforementioned arrangement is described hereinafter.
- The waste, which has been, if desired, prepared to be appropriate dimensions or grain sizes, is thrown into the
pyrolyzer 1 through thewaste charging port 11, so that the waste W lies on thebed 30. Theport 11 is shut by thetop cover 13, and a burner for initial combustion (not shown) is operated, which is provided on the bed portion or wall portion of the pyrolyzer. At the same time, the combustion air is fed to theair inlet 18 through the air supply passage HA. The combustion air passes through thegaps 35 among the spherical ceramics of thebed 30 and flows into the thermal-decomposition area 20, so that initial combustion of the waste starts. - Since the combustion air is introduced from the
bed 30 into the pyrolyzer, the substantially closed area above the waste W is kept in a combustion atmosphere of a low oxygen density (low air ratio). An oxidation combustion reaction in a condition of a relatively high oxygen density (high air ratio) proceeds at a lowermost portion of the waste W, whereas a reduction combustion reaction in a condition of a relatively low oxygen density proceeds at an uppermost portion of the waste W. The formations of the waste W can be classified as illustrated in FIG. 2, in accordance with the process of the combustion reaction. The process of the combustion reaction proceeds in different manners in respective layers, i.e., a combustion zone (lowermost layer) W1, a gasification zone (intermediate layer) W2 and a carbonization zone (uppermost layer) W3. The pyrolysis gas generated from an upper surface of the waste W is conducted through the pyrolysisgas delivery port 15 to the pyrolysis gas delivery passage PG, and the gas enters into the reformingarea 51 through thepyrolysis gas inlet 55. - Before the
pyrolyzer 1 starts the initial combustion step, the mixed gas of air and steam at a relatively high temperature has been introduced into the reformingarea 51 through the mixed gas supply passage MG, so that the reformingarea 51 and thebarrier 60 have been preheated to raise the temperature and accumulate the heat. - The pyrolysis gas of the
pyrolyzer 1 initially mixes with the mixed gas in the reformingarea 51 and then, mixes effectively therewith while passing through thegaps 65. The hydrocarbon contained in the pyrolysis gas reacts with the steam and air under the condition of high temperature atmosphere, whereby the pyrolysis gas is reformed into crude fuel gas containing a relatively large amount of carbon monoxide and hydrogen with the steam reforming reaction of the hydrocarbon. - The pyrolysis gas has a temperature of approximately 200˜300° C., and the mixed gas has a temperature equal to or higher than 300° C., preferably, a temperature equal to or higher than 400° C. The air in the mixed gas reacts with the hydrocarbon in the pyrolysis gas so as to supplement the heat required for reforming reaction between the steam in the mixed gas and the hydrocarbon in the pyrolysis gas. Inclusion of excessive quantity of air in the mixed gas results in greater loss of useful fuel components (carbon monoxide and hydrogen) in the reformed gas. Therefore, the quantity of air in the mixed gas is preferably limited to a minimum quantity necessary for supplementing the heat required for the steam reforming reaction. For instance, the mixing ratio of air and steam (weight ratio) is set to be a predetermined ratio in a range from 2:8 to 7:3, e.g., 5:5.
- The crude fuel gas produced by the reforming reaction flows through the
gaps 65 of the spherical ceramics of thebarrier 60 down to thehorizontal flow passage 71 and exits to the reformed gas effluent passage HG through thevertical flow passage 72. - As the combustion reaction proceeds in the pyrolyzer, the volume of the waste W is reduced and combustion residue deposits on the
bed 30. The lowermost zone of the waste W is supplied with the combustion air through thegaps 35 of the spherical ceramics and keeps its atmosphere of a high temperature by the heat accumulation effect of thespherical ceramics 30, so that the oxidizing combustion reaction of the waste is promoted. Molten waste plastics and the like in the waste W are subjected to re-combustion in thegaps 35. Therefore, incinerated ash after perfect or complete combustion lies on thebed 30, and after combustion operation of thepyrolyzer 1 is stopped, incinerated ash remaining on thebed 30 can be relatively easily discharged. - Although the present invention has been described as to specific embodiments, the present invention is not limited to such embodiments, but may be modified or changed without departing from the scope of the invention as defined in the attached claims.
- For instance, although the spherical ceramic forms are employed in the aforementioned embodiment, spherical metal forms may be used as the spherical heat-resistant materials.
- Further, any type of heat exchanger or heater may be employed as the heat exchanger and the air/steam heating device as set forth above, such as a high performance heat exchanger of a recuperator, metal coil or metal fin type; a high temperature air generator or a high temperature steam generator with use of regenerators of honeycomb structure as disclosed in Japanese patent application No. 10-189 (Japanese patent laid-open publication No. 10-246428), Japanese patent application No. 8-230682 (Japanese patent laid-open publication No. 10-73236) and so forth; or a regenerative type of heat exchanger having a number of pellets, pebbles or ball type regenerators contained therein.
- Furthermore, although waste is used as the solid fuel in the aforementioned embodiment, the gasification apparatus of the present invention can constitute a biomass fuel gasification apparatus or a coal gasification apparatus with use of biomass fuel or coal as the solid fuel.
- Industrial Applicability
- As described above, in accordance with the invention defined in
claim 1, a relatively small scale apparatus for gasifying solid fuel can be provided, in which the pyrolysis gas produced in the pyrolyzer for solid fuel is successfully reformed to the crude fuel gas. - According to the invention defined in
claim 5, a pyrolyzer for solid fuel constituting such an apparatus for gasifying solid fuel can be provided, which can effectively incinerate the waste including a relatively large amount of waste plastics and the like, and which can produce the pyrolysis gas from the waste. - According to the invention defined in claim 7, a steam reformer constituting the aforesaid apparatus for gasifying solid fuel can be provided, which can effectively reform the pyrolysis gas to the crude fuel gas by mixing the pyrolysis gas of the gasifier with the steam.
Claims (10)
1. An apparatus for gasifying solid fuel which thermally decomposes the solid fuel by a combustion reaction of a low oxygen density so as to produce pyrolysis gas, comprising a solid fuel pyrolyzer and a steam reformer;
wherein said pyrolyzer has an air inlet positioned at a bottom part thereof to blow combustion air into the pyrolyzer, a bed of the pyrolyzer located above the air inlet, and a pyrolysis gas exit positioned at an upper part of a body of the pyrolyzer and conducting the pyrolysis gas out of the pyrolyzer, the bed being constituted by a layered stack of many spherical heat-resistant materials which form a number of narrow gaps for draft of the combustion air over the whole bed; and
wherein said steam reformer has a reforming area for producing crude fuel gas by a steam reforming reaction of said pyrolysis gas, a pyrolysis gas inlet which is in communication with said pyrolysis gas exit and which introduces the pyrolysis gas into the reforming area, a mixed gas inlet for introducing mixed gas of steam and air into the reforming area, a reformed gas effluent passage for conducting reformed gas of the reforming area out of the reformer, and a permeable heat-barrier positioned between the reforming area and the reformed gas effluent passage, the barrier being constituted by a layered stack of many spherical heat-resistant materials which form a number of narrow gaps for draft of said pyrolysis gas and said mixed gas.
2. An apparatus for gasifying solid fuel as defined in claim 1 , wherein a temperature of said combustion air is set to be a temperature equal to or higher than 150° C.
3. An apparatus for gasifying solid fuel as in claim 1 or 2, wherein a temperature of said mixed gas is set to be a temperature equal to or higher than 300° C.
4. An apparatus for gasifying fixed fuel as defined in one of claims 1 to 3 , wherein said reformed gas effluent passage is connected with a heat exchanger for heating the combustion air, so that the reformed gas exchanges heat with the combustion air so as to be cooled down.
5. A pyrolyzer of an apparatus for gasifying solid fuel which thermally decomposes the solid fuel by a combustion reaction of a low oxygen density so as to produce pyrolysis gas, comprising:
an air inlet positioned at a bottom part of the pyrolyzer and upwardly blowing combustion air into the pyrolyzer; a bed of the pyrolyzer located above the air inlet; and a pyrolysis gas exit positioned at an upper part of a body of the pyrolyzer and conducting the pyrolysis gas out of the pyrolyzer, the bed being constituted by a layered stack of many spherical heat-resistant materials, which form a number of narrow gaps for draft of the combustion air over the whole bed.
6. A pyrolyzer for solid fuel as defined in claim 5 , wherein said heat-resistant material is a solid and spherical ceramic form or metallic form having a diameter ranging from 5 mm to 200 mm.
7. A steam reformer of an apparatus for gasifying solid fuel which reforms pyrolysis gas produced by a thermal-decomposition reaction of the solid fuel, comprising:
a reforming area which produces crude fuel gas by a steam reforming reaction of said pyrolysis gas; a pyrolysis gas inlet which introduces the pyrolysis gas of the solid fuel pyrolyzer into the reforming area; a mixed gas inlet for introducing mixed gas of steam and air into the reforming area; a reformed gas effluent passage for conducting reformed gas of the reforming area out of the reformer; and a permeable heat-barrier positioned between the reforming area and the reformed gas effluent passage, the barrier being constituted by a layered stack of many spherical heat-resistant materials, which form a number of narrow gaps for draft of said pyrolysis gas and said mixed gas.
8. A pyrolyzer for solid fuel as defined in claim 7 , wherein said heat-resistant material is a solid and spherical ceramic form or metallic form having a diameter ranging from 5 mm to 200 mm.
9. A steam reformer as defined in claim 7 or 8, composed of a vertical reformer vessel part (50) defining said reforming area and a reformed gas flowing part (70) for conducting said reformed gas to the reformed gas effluent passage, said mixed gas inlet (54) being formed at an upper portion of said vessel part and a downstream end of the mixed gas supply passage being connected to the mixed gas inlet.
10. A steam reformer as defined in claim 9 , wherein a support structure (61) supporting said spherical heat-resistant materials (62) is secured to a wall (52) of said vessel part, and a horizontal flow passage (71) of said reformed gas flowing part extends under said support structure, the horizontal flow passage continuing to a vertical flow passage (72) of the flowing part which is in communication with said reformed gas effluent passage.
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
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JP2001-10831 | 2001-01-18 | ||
JP2001010831A JP3973840B2 (en) | 2001-01-18 | 2001-01-18 | Solid fuel gasifier |
PCT/JP2002/000307 WO2002057395A1 (en) | 2001-01-18 | 2002-01-18 | Apparatus for gasifying solid fuel |
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US20040060236A1 true US20040060236A1 (en) | 2004-04-01 |
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ID=18878075
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US10/250,681 Abandoned US20040060236A1 (en) | 2001-01-18 | 2002-01-18 | Apparatus for gasifying solid fuel |
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US (1) | US20040060236A1 (en) |
EP (1) | EP1371713A4 (en) |
JP (1) | JP3973840B2 (en) |
KR (1) | KR100896112B1 (en) |
CN (1) | CN100506953C (en) |
AU (1) | AU2002225429B2 (en) |
WO (1) | WO2002057395A1 (en) |
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Also Published As
Publication number | Publication date |
---|---|
JP2002210444A (en) | 2002-07-30 |
AU2002225429B2 (en) | 2006-10-05 |
CN1498259A (en) | 2004-05-19 |
KR100896112B1 (en) | 2009-05-07 |
CN100506953C (en) | 2009-07-01 |
KR20030066805A (en) | 2003-08-09 |
EP1371713A4 (en) | 2007-05-02 |
JP3973840B2 (en) | 2007-09-12 |
EP1371713A1 (en) | 2003-12-17 |
WO2002057395A1 (en) | 2002-07-25 |
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