CA2574020A1 - Gasification apparatus and method - Google Patents
Gasification apparatus and method Download PDFInfo
- Publication number
- CA2574020A1 CA2574020A1 CA002574020A CA2574020A CA2574020A1 CA 2574020 A1 CA2574020 A1 CA 2574020A1 CA 002574020 A CA002574020 A CA 002574020A CA 2574020 A CA2574020 A CA 2574020A CA 2574020 A1 CA2574020 A1 CA 2574020A1
- Authority
- CA
- Canada
- Prior art keywords
- combustor
- ash
- scrubber
- finisher
- support member
- 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
- 238000002309 gasification Methods 0.000 title abstract description 24
- 238000000034 method Methods 0.000 title description 19
- 239000000446 fuel Substances 0.000 abstract description 50
- 239000002023 wood Substances 0.000 abstract description 12
- 239000002351 wastewater Substances 0.000 abstract description 11
- 238000006243 chemical reaction Methods 0.000 abstract description 7
- 239000002699 waste material Substances 0.000 abstract description 6
- 230000003197 catalytic effect Effects 0.000 abstract description 4
- 239000007789 gas Substances 0.000 description 72
- 239000007788 liquid Substances 0.000 description 30
- 239000007787 solid Substances 0.000 description 28
- 238000003756 stirring Methods 0.000 description 18
- 239000004449 solid propellant Substances 0.000 description 17
- 238000002485 combustion reaction Methods 0.000 description 12
- 238000010438 heat treatment Methods 0.000 description 12
- 239000003054 catalyst Substances 0.000 description 11
- 239000000463 material Substances 0.000 description 11
- 239000000203 mixture Substances 0.000 description 11
- ATUOYWHBWRKTHZ-UHFFFAOYSA-N Propane Chemical compound CCC ATUOYWHBWRKTHZ-UHFFFAOYSA-N 0.000 description 9
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 9
- 239000013618 particulate matter Substances 0.000 description 9
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 8
- 239000010802 sludge Substances 0.000 description 7
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 6
- 241000287828 Gallus gallus Species 0.000 description 6
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 6
- 239000000047 product Substances 0.000 description 6
- 229920001131 Pulp (paper) Polymers 0.000 description 5
- 239000002250 absorbent Substances 0.000 description 5
- 230000002745 absorbent Effects 0.000 description 5
- 229910052500 inorganic mineral Inorganic materials 0.000 description 5
- 239000011707 mineral Substances 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 238000012360 testing method Methods 0.000 description 5
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 4
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 4
- 239000005909 Kieselgur Substances 0.000 description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 4
- 239000003463 adsorbent Substances 0.000 description 4
- 239000012237 artificial material Substances 0.000 description 4
- 229910002091 carbon monoxide Inorganic materials 0.000 description 4
- 239000000919 ceramic Substances 0.000 description 4
- -1 ferrous metals Chemical class 0.000 description 4
- 239000002657 fibrous material Substances 0.000 description 4
- 229910010272 inorganic material Inorganic materials 0.000 description 4
- 239000011147 inorganic material Substances 0.000 description 4
- 239000003915 liquefied petroleum gas Substances 0.000 description 4
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- 239000003921 oil Substances 0.000 description 4
- 239000011368 organic material Substances 0.000 description 4
- 239000004033 plastic Substances 0.000 description 4
- 229920003023 plastic Polymers 0.000 description 4
- 239000011148 porous material Substances 0.000 description 4
- 239000010970 precious metal Substances 0.000 description 4
- 239000001294 propane Substances 0.000 description 4
- 239000012855 volatile organic compound Substances 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 3
- 230000005611 electricity Effects 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 3
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 3
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 3
- 239000003345 natural gas Substances 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 239000010828 animal waste Substances 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 238000013028 emission testing Methods 0.000 description 2
- 210000004907 gland Anatomy 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 238000012856 packing Methods 0.000 description 2
- 239000002910 solid waste Substances 0.000 description 2
- 239000011269 tar Substances 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 239000004606 Fillers/Extenders Substances 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- 239000002154 agricultural waste Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000003575 carbonaceous material Substances 0.000 description 1
- 230000005465 channeling Effects 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000000306 component Substances 0.000 description 1
- 239000008162 cooking oil Substances 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000010795 gaseous waste Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 239000010808 liquid waste Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 239000004570 mortar (masonry) Substances 0.000 description 1
- 239000010705 motor oil Substances 0.000 description 1
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 239000011120 plywood Substances 0.000 description 1
- 244000144977 poultry Species 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000003583 soil stabilizing agent Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 239000002916 wood waste Substances 0.000 description 1
- 239000010925 yard waste Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/02—Fixed-bed gasification of lump fuel
- C10J3/20—Apparatus; Plants
- C10J3/34—Grates; Mechanical ash-removing devices
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/02—Fixed-bed gasification of lump fuel
- C10J3/20—Apparatus; Plants
- C10J3/22—Arrangements or dispositions of valves or flues
- C10J3/24—Arrangements or dispositions of valves or flues to permit flow of gases or vapours other than upwardly through the fuel bed
- C10J3/26—Arrangements or dispositions of valves or flues to permit flow of gases or vapours other than upwardly through the fuel bed downwardly
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/02—Fixed-bed gasification of lump fuel
- C10J3/20—Apparatus; Plants
- C10J3/30—Fuel charging devices
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/02—Fixed-bed gasification of lump fuel
- C10J3/20—Apparatus; Plants
- C10J3/32—Devices for distributing fuel evenly over the bed or for stirring up the fuel bed
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/02—Fixed-bed gasification of lump fuel
- C10J3/20—Apparatus; Plants
- C10J3/34—Grates; Mechanical ash-removing devices
- C10J3/40—Movable grates
- C10J3/42—Rotary grates
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/72—Other features
- C10J3/723—Controlling or regulating the gasification process
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/08—Purifying combustible gases containing carbon monoxide by washing with liquids; Reviving the used wash liquors
- C10K1/10—Purifying combustible gases containing carbon monoxide by washing with liquids; Reviving the used wash liquors with aqueous liquids
- C10K1/101—Purifying combustible gases containing carbon monoxide by washing with liquids; Reviving the used wash liquors with aqueous liquids with water only
-
- 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
- C10J2200/158—Screws
-
- 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
-
- 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
-
- 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
- C10J2300/18—Details of the gasification process, e.g. loops, autothermal operation
- C10J2300/1807—Recycle loops, e.g. gas, solids, heating medium, water
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- General Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Processing Of Solid Wastes (AREA)
- Incineration Of Waste (AREA)
- Gasification And Melting Of Waste (AREA)
- Treatment Of Sludge (AREA)
- Industrial Gases (AREA)
- Chimneys And Flues (AREA)
Abstract
A gasification system (10) is disclosed having a combustor (12), a scrubber (14), a finisher (16), and optionally a recycler (18). A carbonaceous fuel is partially combusted in the combustor to generate a combustible gas. An improved ash support and removal system reduces clogging and other problems in the combustor (12). The combustible gas passes through the scrubber (14) to remove matter such as tar and oil and to undergo preliminary catalytic chemical reactions. The scrubbed gas passes through a hybrid blower (0) to the finisher (16). Final catalytic chemical reactions occur in the finisher (18), and wood chips or other filters may also be used in the finisher to provide a relatively clean, dry, combustible gas. Wastewater and other waste products from the scrubber and finisher are captured in the recycler (18) and returned to the combustor (12).
Description
GASIFICATION APPARATUS AND METHOD
This application claims priority from U.S. patent application serial number 10/911,386, filed on August 4, 2004.
Background of the Invention This invention relates to gasification and, more particularly, to a flexible gasification apparatus and method that provides combustible gases having high heating values wllile avoiding pitfalls of prior attempts at gasification.
Gasification has generally been known for years. In gasification, a carbonaceous fuel source is partially combusted to produce a combustible gas, synthesis gas, or syngas. The combustible gas is then combusted to produce work. The combustible gases produced by gasification may find any number of uses, including but not limited to supplying heat, powering a motor, or producing electricity. Gasification provides many advantages, such as allowing fuels having relatively low heating values to be used, allowing waste products to be used to produce work, and, similarly, reducing the amount of waste material that must be sent to landfills. Despite these obvious advantages, gasification has met with only limited success, because gasification systems have typically been plagued by a number of disadvantages or difficulties. For example, the heating values of gases produced using prior art systems have tended to fluctuate to an undesirable degree, particularly when a variety of fuel sources or fuel sources of varying compositions have been used. Similarly, it has also proven difficult to consistently produce gases having sufficiently high heating values. Separating particulate matter from the produced gas has proven problematic. Similarly, it has proven difficult to produce sufficiently clean gases having sufficiently low amounts of particulate matter as well as sufficiently low amounts of pollutants such as such as sulfur dioxide (SO2), nitrogen oxides (NO,t), carbon monoxide (CO), volatile organic compounds (VOC), ammonia (NH3), hydrogen chloride (HC1), and other chlorides. Environmentally sound disposal of wastewater generated by such systems has also presented difficulties. Further still, the presence of water or other liquids in the combustible gas has made it difficult or impossible to use blowers for moving the combustible gases without creating undesirable levels of wear and tear on the blowers.
Summary of the Invention It is therefore an object of the present invention to provide a flexible gasification apparatus and method that provides combustible gases having high heating values while avoiding pitfalls of prior attempts at gasification.
It is a further object of the present invention to provide an apparatus and method of the above type that can easily handle a wide variety of carbonaceous fuel sources or combinations of fuel sources.
It is a further object of the present invention to provide an apparatus and method of the above type that produces a high value heating gas having low amounts of particulate matter and otlzer pollutants.
It is a further object of the present invention to provide an apparatus and method of the above type that requires little or no wastewater disposal.
It is a still f-urther object of the present invention to provide an apparatus and method of the above type that captures a relatively high fraction of the potential heating value of the fuel sources.
It is a still furtlier object of the present invention to provide an apparatus and method of the above type that safely and cleanly consumes a wide variety of agricultural and industrial byproducts, including but not limited to animal waste and wood pulp sludge.
It is a still further object of the present invention to provide an apparatus and method of the above type that is less prone to clogging problems typically associated with ash removal.
It is a still further object of the present invention to provide an apparatus and method of the above type that may easily process a wide variety of combinations of solid, semi-solid, and liquid fuels.
It is a still further object of the present invention to provide an apparatus and method of the above type that can safely and efficiently handle and dry relatively wet combustible gases.
It is a still further object of the present invention to provide an apparatus and method of the above type that uses a rugged, hybrid blower that can safely and efficiently handle both dry and relatively wet combustible gases.
Toward the fulfillment of these and other objects and advantages, the system of the present invention comprises a combustor, a scrubber, a finisher, and optionally a recycler. A
This application claims priority from U.S. patent application serial number 10/911,386, filed on August 4, 2004.
Background of the Invention This invention relates to gasification and, more particularly, to a flexible gasification apparatus and method that provides combustible gases having high heating values wllile avoiding pitfalls of prior attempts at gasification.
Gasification has generally been known for years. In gasification, a carbonaceous fuel source is partially combusted to produce a combustible gas, synthesis gas, or syngas. The combustible gas is then combusted to produce work. The combustible gases produced by gasification may find any number of uses, including but not limited to supplying heat, powering a motor, or producing electricity. Gasification provides many advantages, such as allowing fuels having relatively low heating values to be used, allowing waste products to be used to produce work, and, similarly, reducing the amount of waste material that must be sent to landfills. Despite these obvious advantages, gasification has met with only limited success, because gasification systems have typically been plagued by a number of disadvantages or difficulties. For example, the heating values of gases produced using prior art systems have tended to fluctuate to an undesirable degree, particularly when a variety of fuel sources or fuel sources of varying compositions have been used. Similarly, it has also proven difficult to consistently produce gases having sufficiently high heating values. Separating particulate matter from the produced gas has proven problematic. Similarly, it has proven difficult to produce sufficiently clean gases having sufficiently low amounts of particulate matter as well as sufficiently low amounts of pollutants such as such as sulfur dioxide (SO2), nitrogen oxides (NO,t), carbon monoxide (CO), volatile organic compounds (VOC), ammonia (NH3), hydrogen chloride (HC1), and other chlorides. Environmentally sound disposal of wastewater generated by such systems has also presented difficulties. Further still, the presence of water or other liquids in the combustible gas has made it difficult or impossible to use blowers for moving the combustible gases without creating undesirable levels of wear and tear on the blowers.
Summary of the Invention It is therefore an object of the present invention to provide a flexible gasification apparatus and method that provides combustible gases having high heating values while avoiding pitfalls of prior attempts at gasification.
It is a further object of the present invention to provide an apparatus and method of the above type that can easily handle a wide variety of carbonaceous fuel sources or combinations of fuel sources.
It is a further object of the present invention to provide an apparatus and method of the above type that produces a high value heating gas having low amounts of particulate matter and otlzer pollutants.
It is a further object of the present invention to provide an apparatus and method of the above type that requires little or no wastewater disposal.
It is a still f-urther object of the present invention to provide an apparatus and method of the above type that captures a relatively high fraction of the potential heating value of the fuel sources.
It is a still furtlier object of the present invention to provide an apparatus and method of the above type that safely and cleanly consumes a wide variety of agricultural and industrial byproducts, including but not limited to animal waste and wood pulp sludge.
It is a still further object of the present invention to provide an apparatus and method of the above type that is less prone to clogging problems typically associated with ash removal.
It is a still further object of the present invention to provide an apparatus and method of the above type that may easily process a wide variety of combinations of solid, semi-solid, and liquid fuels.
It is a still further object of the present invention to provide an apparatus and method of the above type that can safely and efficiently handle and dry relatively wet combustible gases.
It is a still further object of the present invention to provide an apparatus and method of the above type that uses a rugged, hybrid blower that can safely and efficiently handle both dry and relatively wet combustible gases.
Toward the fulfillment of these and other objects and advantages, the system of the present invention comprises a combustor, a scrubber, a finisher, and optionally a recycler. A
carbonaceous fuel is partially combusted in the combustor to generate a combustible gas. An improved ash support and removal system reduces clogging and other problems in the combustor. The combustible gas passes through the scrubber to remove matter such as tar and oil and/or to undergo preliminary catalytic chemical reactions. The scrubbed gas passes through a hybrid blower to the finisher. Final catalytic chemical reactions occur in the finisher, and wood chips or other filters may also be used in the finisher to provide a relatively clean, diy, combustible gas. Wastewater and other waste products from the scrubber and finisher may be captured in the recycler and returned to the combustor.
Brief Description of the Drawings The above brief description, as well as further objects, features and advantages of the present invention will be more fully appreciated by reference to the following detailed description of the presently preferred but nonetheless illustrative embodiments in accordance with the present invention when taken in conjunction with the accompanying drawings, wlierein:
FIG. 1 is a flow diagram of a system for practicing the present invention;
FIG 2 is a side elevation, schematic view of a combustor for practicing the present invention;
FIG. 3 is an overhead, schematic view of a blower for practicing the present invention;
and FIG. 4 is a side elevation view of an impeller for practicing the present invention.
Detailed Description of the Preferred Embodiment Referring to Fig. 1, the reference numeral 10 refers in general to a gasification system for practicing the present invention. The system 10 will typically coinprise a combustor 12, a sciubber 14, and a finisher 16, and may also include a recycler 18. The system 10 principally consists of preferably a combustor 12 and a finisher 16, more preferably a combustor 12, a scrubber 14, and a finisher 16, and most preferably a combustor 12, a scrubber 14, a finisher 16, and a recycler 18. The combustor 12, scrubber 14, finisher 16, and recycler 18 may include any type of reaction vessel.
Brief Description of the Drawings The above brief description, as well as further objects, features and advantages of the present invention will be more fully appreciated by reference to the following detailed description of the presently preferred but nonetheless illustrative embodiments in accordance with the present invention when taken in conjunction with the accompanying drawings, wlierein:
FIG. 1 is a flow diagram of a system for practicing the present invention;
FIG 2 is a side elevation, schematic view of a combustor for practicing the present invention;
FIG. 3 is an overhead, schematic view of a blower for practicing the present invention;
and FIG. 4 is a side elevation view of an impeller for practicing the present invention.
Detailed Description of the Preferred Embodiment Referring to Fig. 1, the reference numeral 10 refers in general to a gasification system for practicing the present invention. The system 10 will typically coinprise a combustor 12, a sciubber 14, and a finisher 16, and may also include a recycler 18. The system 10 principally consists of preferably a combustor 12 and a finisher 16, more preferably a combustor 12, a scrubber 14, and a finisher 16, and most preferably a combustor 12, a scrubber 14, a finisher 16, and a recycler 18. The combustor 12, scrubber 14, finisher 16, and recycler 18 may include any type of reaction vessel.
Referring to Fig. 2, the combustor 12 has an upper, outer wall portion 20 and a lower base portion 22. The combustor 12 is preferably open, more preferably closed, at the top and is preferably configured as a downdraft combustor, more preferably as an updraft combustor.
A feed line, conduit, or fuel auger 24 is disposed above the combustor 12 to provide a carbonaceous fuel source. Another feed line 26 may also be provided to recycle material from other portions of the system 10 as discussed in more detail below.
Additional feed lines may also be used, for example, to provide different types of solid, semi-solid, and liquid fuel sources. An inner wall 28 is disposed within the combustor 12 and is connected to the combustor 12 to form an inner chamber 30 and an outer chamber 32. A lower portion of the inner wall 28 defines an opening 34. An ash support member 36 is affixed to a lower portion of the inner wall 28 by rigid members 38 so that the ash support member 36 is disposed a distance below the opening 34. The outer periphery of the ash support member 36 is relatively free from obstructions about the vast majority of the outer periphery, providing relatively open side passageways between the inner wall 28 and the ash support member 36.
This allows ash to spill from the ash support member 36 preferably over at least approximately 80 percent of the outer periphery of the ash support member 36, more preferably over at least approximately 90 percent of the outer periphery of the ash support member 36, and most preferably over at least approximately 95 percent of the outer periphery of the ash support member 36.
A gas injection ring 40 is affixed to the inner wall 28 and is disposed at a medial point of the inner chamber 30. Openings 42 in the inner wall 28 provide a flow path for gas, such as air or an air and fuel mixture, to pass from a plenum 44 forined by the ring 40 into the inner chamber 30. A conduit or gas manifold 46 extends througli the outer wall 20 of the combustor 12 and is operably connected to the ring 40. The conduit or gas manifold 46 is connected to an air source and is preferably connected to a fuel source, such as a source of natural gas, liquefied petroleum gas (LPG or LP gas), or propane (C3H8). As seen in Fig. 1, a recycle line 48 may also be provided to return a portion of the combustible gas generated by the system 10. An igniter 50, such as a spark plug igniter, is preferably disposed in the conduit or gas manifold 46 adjacent to the combustor 12, more preferably disposed inside a partial shield to prevent particles from bridging the spark plug gap, with said shield disposed in the conduit or gas manifold 46 adjacent to the combustor 12. One additional igniter, partial shield, and branch of gas manifold 46 may be optionally (and is preferably) disposed diametrically opposite igniter 50 to improve combustion uniformity within combustor 12.
A feed line, conduit, or fuel auger 24 is disposed above the combustor 12 to provide a carbonaceous fuel source. Another feed line 26 may also be provided to recycle material from other portions of the system 10 as discussed in more detail below.
Additional feed lines may also be used, for example, to provide different types of solid, semi-solid, and liquid fuel sources. An inner wall 28 is disposed within the combustor 12 and is connected to the combustor 12 to form an inner chamber 30 and an outer chamber 32. A lower portion of the inner wall 28 defines an opening 34. An ash support member 36 is affixed to a lower portion of the inner wall 28 by rigid members 38 so that the ash support member 36 is disposed a distance below the opening 34. The outer periphery of the ash support member 36 is relatively free from obstructions about the vast majority of the outer periphery, providing relatively open side passageways between the inner wall 28 and the ash support member 36.
This allows ash to spill from the ash support member 36 preferably over at least approximately 80 percent of the outer periphery of the ash support member 36, more preferably over at least approximately 90 percent of the outer periphery of the ash support member 36, and most preferably over at least approximately 95 percent of the outer periphery of the ash support member 36.
A gas injection ring 40 is affixed to the inner wall 28 and is disposed at a medial point of the inner chamber 30. Openings 42 in the inner wall 28 provide a flow path for gas, such as air or an air and fuel mixture, to pass from a plenum 44 forined by the ring 40 into the inner chamber 30. A conduit or gas manifold 46 extends througli the outer wall 20 of the combustor 12 and is operably connected to the ring 40. The conduit or gas manifold 46 is connected to an air source and is preferably connected to a fuel source, such as a source of natural gas, liquefied petroleum gas (LPG or LP gas), or propane (C3H8). As seen in Fig. 1, a recycle line 48 may also be provided to return a portion of the combustible gas generated by the system 10. An igniter 50, such as a spark plug igniter, is preferably disposed in the conduit or gas manifold 46 adjacent to the combustor 12, more preferably disposed inside a partial shield to prevent particles from bridging the spark plug gap, with said shield disposed in the conduit or gas manifold 46 adjacent to the combustor 12. One additional igniter, partial shield, and branch of gas manifold 46 may be optionally (and is preferably) disposed diametrically opposite igniter 50 to improve combustion uniformity within combustor 12.
As seen in Fig. 2, a fuel agitator, such as fuel stirring member 52, is provided in the inner chamber 30. The fuel stirring member 52 is preferably disposed above the opening 34 and is more preferably disposed above the ring 40. Similarly, an ash agitator or combustion bed stirrer such as ash stirring member or combustion bed stirrer 54 is provided inside the combustor 12, below the ring 40 and above the ash support member 36. Another ash agitator such as ash stirring member 55 is provided inside the combustor 12 below the ash support member 36. Coaxial shafts 56 and 58 extend upward from the stirring members 52, 54, and 55 to or above an upper portion of the combustor 12. Motors 60 and 62 are operably connected to the shafts 56 and 58 for rotating the shafts and stirring members 52, 54, and 55.
Hollow shaft 58 is rotated by motor 60 and is preferably connected to both stirring members 52 and 54, and more preferably connected to stirring member 52 but not to stirring member 54. Solid shaft 56 is rotated by motor 62 and is preferably comlected to stirring member 55 but not to stiiTing member 54, but more preferably connected to both stirring member 54 and stirring member 55. Stirring members 52, 54, and 55 are most preferably attached individually to separate coaxial shafts that are individually rotated by separate motors.
The fi-ustoconical, lower base portion 22 of the combustor 12 extends below the ash support member 36. An opening is provided at the bottom of the lower base portion 22 to allow ash to pass from the combustor 12 to an ash removal system 64, such as an auger drive for solids transfer. A conduit 66 is provided through the outer wall of the combustor 12 in an upper portion of preferably the outer chamber 32, more preferably the inner chamber 30 to provide a path for combustible gases generated within the combustor 12 to pass from the combustor 12.
A fuel level sensor 68 is provided in the inner chamber 30, preferably above the opening 34, more preferably above the ring 40, and most preferably above the fuel agitator 52. The fuel level sensor 68 is operably coupled with the feed line or fuel auger 24 to automate the process of maintaining fuel at a desired level within the inner chamber 30. An ash level sensor 70 is disposed within the combustor 12, preferably below the opening 34, more preferably below the ash agitator or combustion bed stirrer 54, and most preferably below the ash support member 36. The ash level sensor 70 is operably coupled with the ash removal system 64 to automate the process of maintaining ash at a desired level within the combustor 12. It is of course understood that the combustor 12 may take any number of sizes, shapes, and configurations. It is also understood that the combustor 12 need not be closed at the top and need not be an updraft combustor 12.
Referring to Fig. 1, conduit 66 connects the combustor 12 with the scrubber 14, providing a flow path into preferably an upper portion, more preferably a lower portion of the scrubber 14. The scrubber 14 preferably contains one or more filters (including, but not limited to, ferrous or non-feiTous metals, precious metals, ceramics, minerals, liquids, plastics, fibrous or non-fibrous materials, wood chips, organic or inorganic materials, porous or non-porous materials, natural or artificial materials, absorbents or adsorbents, diatomaceous earth, mixtures or combinations of these and other materials, or any other filter known to those skilled in the art). The scrubber 14 more preferably contains one or more filters and one or more catalysts (including, but not limited to, ferrous or non-ferrous metals, precious metals, ceramics, minerals, liquids, plastics, fibrous or non-fibrous materials, wood chips, organic or inorganic materials, porous or non-porous materials, natural or artificial materials, absorbents or adsorbents, diatomaceous earth, mixtures or combinations of these and other materials, or any other catalyst known to those skilled in the art).
A pump 72 is preferably provided to pass liquid, for example water with impurities therein, through a feed line 74 into a preferably upper portion, more preferably lower portion, of the scrubber 14 and preferably through sprayers. A liquid return line 76 is preferably connected to a lower portion of the scrubber 14 for returning liquid to the pump 72 for reuse within the scrubber 14. A
feed line or conduit 78 may also be provided for providing preferably gas from combustor 12, more preferably gas and liquids from combustor 12, most preferably gas and liquids from combustor 12 and recirculated liquid to scrubber 14. Wash or recirculation lines 80 may be provided for intermittent use as described below. Scrubbed gas exits through conduit 82 that is disposed at a preferably lower, more preferably upper portion of the scrubber 14. A skim line 84 is preferably provided at a lower portion of the scrubber 14, and a blow down line or conduit 86 is provided at the bottom of the scrubber 14. A level sensor 88, such as a float switch, is preferably disposed in the scrubber 14 for maintaining liquid levels within the scrubber 14 at desired levels. It is of course understood that the scrubber 14 may take any number of shapes, sizes, and configurations, and that any number of different filter media or catalysts or different combinations of filter media and catalysts may be used in scrubber 14.
Conduit 82 passes fiom the scrubber 14 to blowers 90. As best seen in Fig. 3, the blowers 90 are heavy duty hybrids that combine desirable features of blowers designed for moving gases and pumps designed for moving liquids. Walls fonning the impeller housing 92 have a wall thickness of preferably approximately 3/4 inch, more preferably approximately 5/8 inch. A sealing member 94, such as a gasket, is used to create an airtight and watertight seal between the walls forming the impeller housing 92. Referring to Fig. 4, the impeller blades 96 are preferably straight, but are more preferably curved, and are thicker than impeller blades of common blowers designed for moving gases, preferably approximately 50 percent thicker. Referring back to Fig. 3, a packing gland 98, similar to a packing gland used in a water pump, is used to provide a shaft 100 seal. Additional sets of bearings 102 are also preferably used in connection with the impeller shaft 100. It is preferred to use at least two sets of bearings 102. Referring to Fig. 1, conduit 104 passes from the blowers 90 to the finisher 16, providing a flow path into preferably a lower portion, but more preferably an upper portion, of the finisher 16. It is of course understood that the blowers 90 may be disposed at any number of locations in the system 10 and that the blowers 90 may take any number of different sizes, shapes, and configurations. It is also understood that, although not preferred, conventional blowers may be used.
The finisher 16 preferably contains one or more filters (including, but not limited to, ferrous or non-ferrous metals, precious metals, ceramics, minerals, liquids, plastics, fibrous or non-fibrous materials, wood chips, organic or inorganic materials, porous or non-porous materials, natural or artificial materials, absorbents or adsorbents, diatomaceous earth, mixtures or combinations of these and other materials, or any other filter known to those skilled in the art). The finisher 16 more preferably contains one or more filters and one or more catalysts (including, but not limited to, ferrous or non-ferrous metals, precious metals, ceramics, minerals, liquids, plastics, fibrous or non-fibrous materials, wood chips, organic or inorganic materials, porous or non-porous materials, natural or artificial materials, absorbents or adsorbents, diatomaceous earth, mixtures or combinations of these and other materials, or any other catalyst known to those skilled in the art). Conduit 106 passes from preferably an upper portion, more preferably a lower portion, of the finisher 16 to provide a flow path for the scrubbed and finished combustible gas. Additional conduits 108, 48, and 110 are also provided for passing the scrubbed, finished combustible gas to flare, to recycle, and for further uses. A conduit 112 passes from a lower portion of the finisher 16 for removing wastewater and other matter that condenses or is removed from the gas as it passes through the finisher 16. It is understood that the finisher 16 may take any number of shapes, sizes, and configurations and that any number of different filter media or catalysts or different combinations of filter media and catalysts may be used in finisher 16.
Hollow shaft 58 is rotated by motor 60 and is preferably connected to both stirring members 52 and 54, and more preferably connected to stirring member 52 but not to stirring member 54. Solid shaft 56 is rotated by motor 62 and is preferably comlected to stirring member 55 but not to stiiTing member 54, but more preferably connected to both stirring member 54 and stirring member 55. Stirring members 52, 54, and 55 are most preferably attached individually to separate coaxial shafts that are individually rotated by separate motors.
The fi-ustoconical, lower base portion 22 of the combustor 12 extends below the ash support member 36. An opening is provided at the bottom of the lower base portion 22 to allow ash to pass from the combustor 12 to an ash removal system 64, such as an auger drive for solids transfer. A conduit 66 is provided through the outer wall of the combustor 12 in an upper portion of preferably the outer chamber 32, more preferably the inner chamber 30 to provide a path for combustible gases generated within the combustor 12 to pass from the combustor 12.
A fuel level sensor 68 is provided in the inner chamber 30, preferably above the opening 34, more preferably above the ring 40, and most preferably above the fuel agitator 52. The fuel level sensor 68 is operably coupled with the feed line or fuel auger 24 to automate the process of maintaining fuel at a desired level within the inner chamber 30. An ash level sensor 70 is disposed within the combustor 12, preferably below the opening 34, more preferably below the ash agitator or combustion bed stirrer 54, and most preferably below the ash support member 36. The ash level sensor 70 is operably coupled with the ash removal system 64 to automate the process of maintaining ash at a desired level within the combustor 12. It is of course understood that the combustor 12 may take any number of sizes, shapes, and configurations. It is also understood that the combustor 12 need not be closed at the top and need not be an updraft combustor 12.
Referring to Fig. 1, conduit 66 connects the combustor 12 with the scrubber 14, providing a flow path into preferably an upper portion, more preferably a lower portion of the scrubber 14. The scrubber 14 preferably contains one or more filters (including, but not limited to, ferrous or non-feiTous metals, precious metals, ceramics, minerals, liquids, plastics, fibrous or non-fibrous materials, wood chips, organic or inorganic materials, porous or non-porous materials, natural or artificial materials, absorbents or adsorbents, diatomaceous earth, mixtures or combinations of these and other materials, or any other filter known to those skilled in the art). The scrubber 14 more preferably contains one or more filters and one or more catalysts (including, but not limited to, ferrous or non-ferrous metals, precious metals, ceramics, minerals, liquids, plastics, fibrous or non-fibrous materials, wood chips, organic or inorganic materials, porous or non-porous materials, natural or artificial materials, absorbents or adsorbents, diatomaceous earth, mixtures or combinations of these and other materials, or any other catalyst known to those skilled in the art).
A pump 72 is preferably provided to pass liquid, for example water with impurities therein, through a feed line 74 into a preferably upper portion, more preferably lower portion, of the scrubber 14 and preferably through sprayers. A liquid return line 76 is preferably connected to a lower portion of the scrubber 14 for returning liquid to the pump 72 for reuse within the scrubber 14. A
feed line or conduit 78 may also be provided for providing preferably gas from combustor 12, more preferably gas and liquids from combustor 12, most preferably gas and liquids from combustor 12 and recirculated liquid to scrubber 14. Wash or recirculation lines 80 may be provided for intermittent use as described below. Scrubbed gas exits through conduit 82 that is disposed at a preferably lower, more preferably upper portion of the scrubber 14. A skim line 84 is preferably provided at a lower portion of the scrubber 14, and a blow down line or conduit 86 is provided at the bottom of the scrubber 14. A level sensor 88, such as a float switch, is preferably disposed in the scrubber 14 for maintaining liquid levels within the scrubber 14 at desired levels. It is of course understood that the scrubber 14 may take any number of shapes, sizes, and configurations, and that any number of different filter media or catalysts or different combinations of filter media and catalysts may be used in scrubber 14.
Conduit 82 passes fiom the scrubber 14 to blowers 90. As best seen in Fig. 3, the blowers 90 are heavy duty hybrids that combine desirable features of blowers designed for moving gases and pumps designed for moving liquids. Walls fonning the impeller housing 92 have a wall thickness of preferably approximately 3/4 inch, more preferably approximately 5/8 inch. A sealing member 94, such as a gasket, is used to create an airtight and watertight seal between the walls forming the impeller housing 92. Referring to Fig. 4, the impeller blades 96 are preferably straight, but are more preferably curved, and are thicker than impeller blades of common blowers designed for moving gases, preferably approximately 50 percent thicker. Referring back to Fig. 3, a packing gland 98, similar to a packing gland used in a water pump, is used to provide a shaft 100 seal. Additional sets of bearings 102 are also preferably used in connection with the impeller shaft 100. It is preferred to use at least two sets of bearings 102. Referring to Fig. 1, conduit 104 passes from the blowers 90 to the finisher 16, providing a flow path into preferably a lower portion, but more preferably an upper portion, of the finisher 16. It is of course understood that the blowers 90 may be disposed at any number of locations in the system 10 and that the blowers 90 may take any number of different sizes, shapes, and configurations. It is also understood that, although not preferred, conventional blowers may be used.
The finisher 16 preferably contains one or more filters (including, but not limited to, ferrous or non-ferrous metals, precious metals, ceramics, minerals, liquids, plastics, fibrous or non-fibrous materials, wood chips, organic or inorganic materials, porous or non-porous materials, natural or artificial materials, absorbents or adsorbents, diatomaceous earth, mixtures or combinations of these and other materials, or any other filter known to those skilled in the art). The finisher 16 more preferably contains one or more filters and one or more catalysts (including, but not limited to, ferrous or non-ferrous metals, precious metals, ceramics, minerals, liquids, plastics, fibrous or non-fibrous materials, wood chips, organic or inorganic materials, porous or non-porous materials, natural or artificial materials, absorbents or adsorbents, diatomaceous earth, mixtures or combinations of these and other materials, or any other catalyst known to those skilled in the art). Conduit 106 passes from preferably an upper portion, more preferably a lower portion, of the finisher 16 to provide a flow path for the scrubbed and finished combustible gas. Additional conduits 108, 48, and 110 are also provided for passing the scrubbed, finished combustible gas to flare, to recycle, and for further uses. A conduit 112 passes from a lower portion of the finisher 16 for removing wastewater and other matter that condenses or is removed from the gas as it passes through the finisher 16. It is understood that the finisher 16 may take any number of shapes, sizes, and configurations and that any number of different filter media or catalysts or different combinations of filter media and catalysts may be used in finisher 16.
Conduits 84, 86, 112, and 114 preferably connect the scrubber 14 and finisher 16 to a recycler 18, providing a flow path into an upper portion of the recycler 18.
Return line or conduit 116 preferably passes from a lower portion of the recycler 18 to pump 118, and line 26 preferably passes from pump 118 to combustor 12. A recirculation line 120 is preferably provided for diverting a portion of the liquid from the return line 26 back to the recycler 18.
A level sensor 122, such as a float switch, is preferably disposed in the recycler 18 for maintaining liquid levels within the recycler 18 at desired levels. It is understood that the recycler 18 may take any number of different shapes, sizes, and configurations.
In operation, feed line or fuel auger 24 provides a solid or semi-solid carbonaceous fuel to the combustor 12. As seen in Fig. 2, the solid or semi-solid fuel drops through the inner chamber 30, accumulates on the ash support member 36, and builds up within the inner chamber 30 to a level above the ring 40 and then above the fuel stirring member 52. As seen in Fig. 1, an oxygen source, such as air, is provided preferably via conduit 124, more preferably via conduit 126 instead, and an alternate fuel source is provided preferably via conduit 126, more preferably via conduit 124 instead. Referring to Fig. 2, the air and alternate fuel are mixed inside conduit or gas manifold 46, ignited by igniter 50, and pass through the ring 40 and into the inner chamber 30. The burning air and alternate fuel mixture ignites the carbonaceous fuel within the inner chamber 30. As the carbonaceous fuel sources pass downward within the inner chainber 30, the carbonaceous fuel sources are at least partially combusted to produce, among other materials, ash and a combustible gas. Fuel stirring member 52 keeps the different fuel sources blended and reduces or prevents channeling, bridging, clumping, voids, and similar problems.
Ash passes through opening 34 and collects on ash support member 36. The ash stirring member or combustion bed stirrer 54 prevents ash build up by moving the collecting ash preferably outward so that the ash spills or passes from the outer periphery of the ash support member 36, more preferably moving the collecting ash downward so that the ash spills or passes through perforations in ash support member 36, or most preferably moving the collecting ash both outward from the outer periphery of ash support member 36 and downward through perforations in ash support member 36 to fall down to the lower base portion 22 of the combustor 12. Other than the ash stirring member or combustion bed stirrer 54 and support members 38, the area between the opening 34 of the inner wal128 and the top surface of ash support member 36 is substantially unobstructed to provide a ready path for ash removal, free from obstructions and sources of clogging such as grates or mesh materials. In that regard, the support members 38 connect the ash support member 36 to the inner wa1128 in a manner that allows ash to spill from the ash support member 36 preferably over at least approximately 70 percent of the outer periphery of the ash support member 36, more preferably over at least approximately 80 percent of the outer periphery of the ash support member 36, and most preferably over at least approximately 90 percent of the outer periphery of the ash support member 36.
Ash that accumulates in the lower base portion 22 of the combustor 12 passes through an opening in the bottom of the combustor 12 and is removed by an ash removal system 64, such as by an auger or screw drive. The ash auger drive 64 is operably coupled with ash level sensor 70 to maintain the ash in the combustor 12 below a desired amount. The ash removed from the combustor 12 will typically be a salable product. For example, the ash might be suitable for sale as fertilizer, soil stabilizer, filter material, and/or as an extender for mortar, concrete, or road material, among other uses.
The fuel level sensor 68 is operably coupled with the solid or semi-solid fuel feed line or fuel auger 24 to maintain solid or semi-solid fuel within a desired height range within the inner chainber 30. The desired heigl7t range will vary depending upon a number of factors, including but not limited to the properties of the solid or semi-solid fuel.
It is typically desirable to maintain the solid or semi-solid fuel level within the inner chamber 30 at the lowest possible level while still maintaining an adequate seal, preferably to prevent products of combustion from escaping through the top of the combustor 12 and/or to help control the degree of partial combustion within inner chamber 30. The level desired will vary with factors such as the density and moisture content of the solid or semi-solid fuel. For example, the desired level for a solid or semi-solid fuel comprised primarily of chicken litter (including, but not limited to, chicken waste products, absorbents such as rice hulls or wood chips, or any combination of these and similar or related materials) will tend to be higher than the desired level for a solid or semi-solid fuel comprised primarily of wood pulp or paper mill sludge, and the desired level for a solid or semi-solid fuel comprised primarily of wood pulp sludge will tend to be higher than the desired level for a solid or semi-solid fuel comprised primarily of sanding or wood dust. In a typical operation in which the solid or semi-solid fuel is comprised primarily of chicken litter, the level of solid or semi-solid fuel within the inner chamber 30 is preferably maintained at a heiglit of approximately 8 inches to approximately 10 inches above the ring 40. Similarly, in an operation in which the solid or semi-solid fuel is comprised primarily of wood pulp sludge, the level of solid or semi-solid fuel within the inner chamber 30 is preferably maintained at a height that is only slightly above the ring 40. Also, in an operation in which the solid or semi-solid fuel is comprised primarily of sanding or wood dust, the level of solid or semi-solid fuel within the inner chamber 30 is preferably maintained at a height that is approximately even with or slightly below the ring 40.
The blowers 90 draw gaseous products of combustion preferably downward, more preferably upward, through the combustor 12 so that they pass through the opening 34 in the inner wall 28 and upwardly through preferably the outer chamber 32, more preferably the inner chamber 30 before passing tlirough conduit 66. Referring to Fig. 1, combustible gas from the combustor 12 enters preferably an upper portion, more preferably a lower portion, of the scrubber 14 and passes upward toward conduit 82. Pump 72 circulates liquid, for example water with impurities therein, to the scrubber 14. Liquid enters the scrubber 14 through conduit 74, passes preferably through sprayers, and contacts the combustible gas.
The liquid cools and scrubs the combustible gas, removing matter from the combustible gas including tar, oil, and particulate matter. The liquid level in the scrubber 14 is maintained at a desired level so that tar, oil, and similar matter may be removed from the scrubber 14 preferably via the skimmer line 84. Particulate matter and other components that settle to the bottom of the scr=ubber 14 are periodically removed via blow down line or conduit 86. Valves 128 are also opened preferably periodically so that the puinp 72 may circulate liquid through wash lines 80 and through conduits 66, 82, and 104 for cleaning. From time to time, valve 130 may be opened so that the liquid in scrubber 14 may also be drained through line 86 and preferably replaced with liquid from line 78. Filters in scrubber 14 primarily remove liquids from the gas. Catalysts in scrubber 14 primarily improve the chemical composition of the gas.
The scrubbed combustible gas exits the scrubber 14 through line 82, passes through blowers 90, and is driven through fmisher 16. As it exits the scrubber 14, the gas may also be passed through a filter/knock-out pot, before being passed to the blowers 90.
Wood chips or other filters in the finisher 16 diy the gas and remove additional amounts of particulate matter and other pollutants. Wastewater and other matter that are removed from the combustible gas and that are not absorbed by the wood chips or other filters fall to the bottom of the finisher 16 and are removed via line 112. Filters in finisher 16 primarily remove liquids from the gas.
Catalysts in finisher 16 primarily improve the chemical composition of the gas. Scrubbed, finished combustible gas exits the fmisher 16 via line 106. From there the combustible gas is flared via line 108, returned to the reaction chamber via line 48, or sent to other uses via line 110. During the initial start-up phase, the combustible gas is flared until it is determined that gas is being produced at a desired quantity and quality. Once the start-up phase is complete, the combustible gas will primarily be passed via line 110 to produce work or for further uses elsewhere. For example, the combustible gas might be combusted to supply heat to a process or might be combusted within a motor or turbine to produce work or to generate electricity.
As additional examples, the combustible gas produced by the system 10 may be used in brooder heaters in poultry houses, in internal combustion engines, and in boilers. In fact, the combustible gas generated by the present system 10 compares quite favorably with natural gas, often being cleaner while having comparable or higher heating values. The heating values of the combustible gas produced will vary depending upon a number of factors, such as the type, composition, and moisture content of the carbonaceous fuel provided, but the heating values of the combustible gas produced will typically be at or near 550 British Thermal Units (BTUs) per cubic foot. Accordingly, combustible gas produced using the present system 10 is a good candidate for use in any situation that currently uses natural gas, liquefied petroleum gas (LPG or LP gas), or propane.
Depending upon the properties of the carbonaceous fuels being supplied to the combustor 12, such as the moisture content, a portion of the combustible gas may be returned to the combustor 12 via line 48 to supply additional fuel to aid in the partial combustion of the carbonaceous fuel. The combustible gas supplied via line 48 may serve as a complete or partial replacement for the alternate fuel source supplied to the combustor 12, preferably via line 126, more preferably via line 124. Returning the combustible gas to the reaction chamber 12 offers a number of advantages. For example, it saves on alternate fuel costs that might otherwise be required to maintain the desired combustion in the combustor 12.
Lines 86, 84, 112, and 114 pass from the scrubber 14 and the finisher 16 to recycler 18. These lines 86, 84, 112, and 114 pass wastewater, excess liquid from wet fuel components, tar, oil, particulate matter, and other removed substances to an upper portion of the recycler 18. These components pass from the recycler 18, preferably via line 116 and pump 118, via line 26 back to the combustor 12, where they are fed into an upper portion of the combustor 12. A portion of these components is preferably diverted via line 120 and returned to the recycler 18 to help stir or agitate the contents of the recycler 18. Returning the wastewater and other components to the combustor 12 provides a number of advantages. For example, the wastewater scavenges additional, residual carbon from the ash as the liquid is broken down. This provides for better recovery of the heating value from the carbonaceous fuel and eliminates or drastically reduces the need to dispose of wastewater.
The system 10 may be used to process a wide variety of carbonaceous fuels, as well as combinations thereof. The spacing between the ash support member 36 and the opening 34 of the inner wa1128, as well as the relatively unobstructed side openings there, allow a wide assortment of solid or semi-solid fuels to be used without fear of clogging.
Possible carbonaceous fuels include, but are not limited to, materials such as chicken litter, other animal waste, municipal solid or semi-solid waste, glued woods (such as plywood and press board), paper mill or wood pulp sludge (including sludge with a moisture content of 65% or higher), wood or yard waste, agricultural waste, shredded tires, and mixtures or combinations of these and other carbonaceous materials. Liquid carbonaceous fuels may also be added, including but not limited to waste motor oil and cooking oil. Adding these liquid carbonaceous fuels can markedly increase the heating value of the combustible gas produced.
In one particular embodiment, the system 10 is approximately 6 feet wide, approximately 10 feet long, and approximately 7.5 feet tall. This particular embodiment of system 10 gasifies approximately eighty (80) pounds of chicken litter per hour, requires no auxiliary fuel after startup, uses only about three (3) kilowatt-hours of electricity, produces over 3.5 million BTUs per hour of combustible gas, and produces only about four (4) pounds per hour of mineral ash, generating no other solid waste, no liquid waste, and no gaseous waste.
The following emissions test examples illustrate that the gasification system 10 of the present invention can produce combustible gas that is environmentally friendly while processing solid or semi-solid carbonaceous fuels that previously posed serious landfill issues.
Example 1 An emissions test was conducted on combustible gas generated by the system 10 while combusting chicken litter. A sample run of 60 minutes in duration was performed.
Testing was performed in accordance with the methods detailed in 40 Code of Federal Regulations (CFR), Part 60, Appendix A. The flow, based on the lowest recordable flow, had a velocity of 6.77 feet per second, and the sample collected had a voluine of 41.42 dry standard cubic feet. The results of the emissions testing are summarized in Table 1 below.
Table 1 Substance Emissions lbs/hr Particulate Matter (based on lowest detectable flow rate) 0.003 VOC as Propane (corrected for moisture) 0.137 Nitrogen Oxides as NOZ 0.001 Carbon Monoxide 0.003 Sulfur Dioxide 0.096 Ammonia 0.033 HCl 0.008 Chloride 0.005 Example 2 An emissions test was conducted on combustible gas generated by the system 10 while combusting paper mill sludge. A sample run of 60 minutes in duration was performed.
Testing was performed in accordance with the metliods detailed in 40 CFR, Part 60, Appendix A. The flow, based on the lowest recordable flow, had a velocity of 6.53 feet per second, and the sample collected had a volume of 40.60 dry standard cubic feet. The results of the emissions testing are summarized in Table 2 below.
Table 2 Substance Emissions (lbs/hr) Particulate Matter (based on lowest detectable flow rate) 0.0014 VOC as Propane (corrected for moisture) 0.014 Nitrogen Oxides as NO2 0.013 Carbon Monoxide 0.051 Sulfur Dioxide 0.017 Other modifications, changes and substitutions are intended in the foregoing, and in some instances, some features of the invention will be employed without a corresponding use of other features. For example, the configuration of the ash support member 36 may be used in combination with any number of different gasification systems, regardless of whether such systems also use other features of the present invention, and may also find uses in systems other than gasification systems. Similarly, the wastewater return features of the present invention may be used in combination with any number of different gasification systems, regardless of whether such systems also use other features of the present invention, and may also find uses in systems other than gasification systems. Further, the wood chip filtering or other filters or catalysts of the present invention may be used in combination with any number of different gasification systems, regardless of whether such systems also use other features of the present invention, and may also find uses in systems other than gasification systems.
Further still, the hybrid blower 90 design of the present invention may be used in combination with any number of different gasification systems, regardless of whether such systems also use other features of the present invention, and may also find uses in systems other than gasification systems. Of course, quantitative information is included by way of exainple only and is not intended as a limitation as to the scope of the invention.
Accordingly, it is appropriate that the invention be construed broadly and in a manner consistent with the scope of the invention disclosed.
Return line or conduit 116 preferably passes from a lower portion of the recycler 18 to pump 118, and line 26 preferably passes from pump 118 to combustor 12. A recirculation line 120 is preferably provided for diverting a portion of the liquid from the return line 26 back to the recycler 18.
A level sensor 122, such as a float switch, is preferably disposed in the recycler 18 for maintaining liquid levels within the recycler 18 at desired levels. It is understood that the recycler 18 may take any number of different shapes, sizes, and configurations.
In operation, feed line or fuel auger 24 provides a solid or semi-solid carbonaceous fuel to the combustor 12. As seen in Fig. 2, the solid or semi-solid fuel drops through the inner chamber 30, accumulates on the ash support member 36, and builds up within the inner chamber 30 to a level above the ring 40 and then above the fuel stirring member 52. As seen in Fig. 1, an oxygen source, such as air, is provided preferably via conduit 124, more preferably via conduit 126 instead, and an alternate fuel source is provided preferably via conduit 126, more preferably via conduit 124 instead. Referring to Fig. 2, the air and alternate fuel are mixed inside conduit or gas manifold 46, ignited by igniter 50, and pass through the ring 40 and into the inner chamber 30. The burning air and alternate fuel mixture ignites the carbonaceous fuel within the inner chamber 30. As the carbonaceous fuel sources pass downward within the inner chainber 30, the carbonaceous fuel sources are at least partially combusted to produce, among other materials, ash and a combustible gas. Fuel stirring member 52 keeps the different fuel sources blended and reduces or prevents channeling, bridging, clumping, voids, and similar problems.
Ash passes through opening 34 and collects on ash support member 36. The ash stirring member or combustion bed stirrer 54 prevents ash build up by moving the collecting ash preferably outward so that the ash spills or passes from the outer periphery of the ash support member 36, more preferably moving the collecting ash downward so that the ash spills or passes through perforations in ash support member 36, or most preferably moving the collecting ash both outward from the outer periphery of ash support member 36 and downward through perforations in ash support member 36 to fall down to the lower base portion 22 of the combustor 12. Other than the ash stirring member or combustion bed stirrer 54 and support members 38, the area between the opening 34 of the inner wal128 and the top surface of ash support member 36 is substantially unobstructed to provide a ready path for ash removal, free from obstructions and sources of clogging such as grates or mesh materials. In that regard, the support members 38 connect the ash support member 36 to the inner wa1128 in a manner that allows ash to spill from the ash support member 36 preferably over at least approximately 70 percent of the outer periphery of the ash support member 36, more preferably over at least approximately 80 percent of the outer periphery of the ash support member 36, and most preferably over at least approximately 90 percent of the outer periphery of the ash support member 36.
Ash that accumulates in the lower base portion 22 of the combustor 12 passes through an opening in the bottom of the combustor 12 and is removed by an ash removal system 64, such as by an auger or screw drive. The ash auger drive 64 is operably coupled with ash level sensor 70 to maintain the ash in the combustor 12 below a desired amount. The ash removed from the combustor 12 will typically be a salable product. For example, the ash might be suitable for sale as fertilizer, soil stabilizer, filter material, and/or as an extender for mortar, concrete, or road material, among other uses.
The fuel level sensor 68 is operably coupled with the solid or semi-solid fuel feed line or fuel auger 24 to maintain solid or semi-solid fuel within a desired height range within the inner chainber 30. The desired heigl7t range will vary depending upon a number of factors, including but not limited to the properties of the solid or semi-solid fuel.
It is typically desirable to maintain the solid or semi-solid fuel level within the inner chamber 30 at the lowest possible level while still maintaining an adequate seal, preferably to prevent products of combustion from escaping through the top of the combustor 12 and/or to help control the degree of partial combustion within inner chamber 30. The level desired will vary with factors such as the density and moisture content of the solid or semi-solid fuel. For example, the desired level for a solid or semi-solid fuel comprised primarily of chicken litter (including, but not limited to, chicken waste products, absorbents such as rice hulls or wood chips, or any combination of these and similar or related materials) will tend to be higher than the desired level for a solid or semi-solid fuel comprised primarily of wood pulp or paper mill sludge, and the desired level for a solid or semi-solid fuel comprised primarily of wood pulp sludge will tend to be higher than the desired level for a solid or semi-solid fuel comprised primarily of sanding or wood dust. In a typical operation in which the solid or semi-solid fuel is comprised primarily of chicken litter, the level of solid or semi-solid fuel within the inner chamber 30 is preferably maintained at a heiglit of approximately 8 inches to approximately 10 inches above the ring 40. Similarly, in an operation in which the solid or semi-solid fuel is comprised primarily of wood pulp sludge, the level of solid or semi-solid fuel within the inner chamber 30 is preferably maintained at a height that is only slightly above the ring 40. Also, in an operation in which the solid or semi-solid fuel is comprised primarily of sanding or wood dust, the level of solid or semi-solid fuel within the inner chamber 30 is preferably maintained at a height that is approximately even with or slightly below the ring 40.
The blowers 90 draw gaseous products of combustion preferably downward, more preferably upward, through the combustor 12 so that they pass through the opening 34 in the inner wall 28 and upwardly through preferably the outer chamber 32, more preferably the inner chamber 30 before passing tlirough conduit 66. Referring to Fig. 1, combustible gas from the combustor 12 enters preferably an upper portion, more preferably a lower portion, of the scrubber 14 and passes upward toward conduit 82. Pump 72 circulates liquid, for example water with impurities therein, to the scrubber 14. Liquid enters the scrubber 14 through conduit 74, passes preferably through sprayers, and contacts the combustible gas.
The liquid cools and scrubs the combustible gas, removing matter from the combustible gas including tar, oil, and particulate matter. The liquid level in the scrubber 14 is maintained at a desired level so that tar, oil, and similar matter may be removed from the scrubber 14 preferably via the skimmer line 84. Particulate matter and other components that settle to the bottom of the scr=ubber 14 are periodically removed via blow down line or conduit 86. Valves 128 are also opened preferably periodically so that the puinp 72 may circulate liquid through wash lines 80 and through conduits 66, 82, and 104 for cleaning. From time to time, valve 130 may be opened so that the liquid in scrubber 14 may also be drained through line 86 and preferably replaced with liquid from line 78. Filters in scrubber 14 primarily remove liquids from the gas. Catalysts in scrubber 14 primarily improve the chemical composition of the gas.
The scrubbed combustible gas exits the scrubber 14 through line 82, passes through blowers 90, and is driven through fmisher 16. As it exits the scrubber 14, the gas may also be passed through a filter/knock-out pot, before being passed to the blowers 90.
Wood chips or other filters in the finisher 16 diy the gas and remove additional amounts of particulate matter and other pollutants. Wastewater and other matter that are removed from the combustible gas and that are not absorbed by the wood chips or other filters fall to the bottom of the finisher 16 and are removed via line 112. Filters in finisher 16 primarily remove liquids from the gas.
Catalysts in finisher 16 primarily improve the chemical composition of the gas. Scrubbed, finished combustible gas exits the fmisher 16 via line 106. From there the combustible gas is flared via line 108, returned to the reaction chamber via line 48, or sent to other uses via line 110. During the initial start-up phase, the combustible gas is flared until it is determined that gas is being produced at a desired quantity and quality. Once the start-up phase is complete, the combustible gas will primarily be passed via line 110 to produce work or for further uses elsewhere. For example, the combustible gas might be combusted to supply heat to a process or might be combusted within a motor or turbine to produce work or to generate electricity.
As additional examples, the combustible gas produced by the system 10 may be used in brooder heaters in poultry houses, in internal combustion engines, and in boilers. In fact, the combustible gas generated by the present system 10 compares quite favorably with natural gas, often being cleaner while having comparable or higher heating values. The heating values of the combustible gas produced will vary depending upon a number of factors, such as the type, composition, and moisture content of the carbonaceous fuel provided, but the heating values of the combustible gas produced will typically be at or near 550 British Thermal Units (BTUs) per cubic foot. Accordingly, combustible gas produced using the present system 10 is a good candidate for use in any situation that currently uses natural gas, liquefied petroleum gas (LPG or LP gas), or propane.
Depending upon the properties of the carbonaceous fuels being supplied to the combustor 12, such as the moisture content, a portion of the combustible gas may be returned to the combustor 12 via line 48 to supply additional fuel to aid in the partial combustion of the carbonaceous fuel. The combustible gas supplied via line 48 may serve as a complete or partial replacement for the alternate fuel source supplied to the combustor 12, preferably via line 126, more preferably via line 124. Returning the combustible gas to the reaction chamber 12 offers a number of advantages. For example, it saves on alternate fuel costs that might otherwise be required to maintain the desired combustion in the combustor 12.
Lines 86, 84, 112, and 114 pass from the scrubber 14 and the finisher 16 to recycler 18. These lines 86, 84, 112, and 114 pass wastewater, excess liquid from wet fuel components, tar, oil, particulate matter, and other removed substances to an upper portion of the recycler 18. These components pass from the recycler 18, preferably via line 116 and pump 118, via line 26 back to the combustor 12, where they are fed into an upper portion of the combustor 12. A portion of these components is preferably diverted via line 120 and returned to the recycler 18 to help stir or agitate the contents of the recycler 18. Returning the wastewater and other components to the combustor 12 provides a number of advantages. For example, the wastewater scavenges additional, residual carbon from the ash as the liquid is broken down. This provides for better recovery of the heating value from the carbonaceous fuel and eliminates or drastically reduces the need to dispose of wastewater.
The system 10 may be used to process a wide variety of carbonaceous fuels, as well as combinations thereof. The spacing between the ash support member 36 and the opening 34 of the inner wa1128, as well as the relatively unobstructed side openings there, allow a wide assortment of solid or semi-solid fuels to be used without fear of clogging.
Possible carbonaceous fuels include, but are not limited to, materials such as chicken litter, other animal waste, municipal solid or semi-solid waste, glued woods (such as plywood and press board), paper mill or wood pulp sludge (including sludge with a moisture content of 65% or higher), wood or yard waste, agricultural waste, shredded tires, and mixtures or combinations of these and other carbonaceous materials. Liquid carbonaceous fuels may also be added, including but not limited to waste motor oil and cooking oil. Adding these liquid carbonaceous fuels can markedly increase the heating value of the combustible gas produced.
In one particular embodiment, the system 10 is approximately 6 feet wide, approximately 10 feet long, and approximately 7.5 feet tall. This particular embodiment of system 10 gasifies approximately eighty (80) pounds of chicken litter per hour, requires no auxiliary fuel after startup, uses only about three (3) kilowatt-hours of electricity, produces over 3.5 million BTUs per hour of combustible gas, and produces only about four (4) pounds per hour of mineral ash, generating no other solid waste, no liquid waste, and no gaseous waste.
The following emissions test examples illustrate that the gasification system 10 of the present invention can produce combustible gas that is environmentally friendly while processing solid or semi-solid carbonaceous fuels that previously posed serious landfill issues.
Example 1 An emissions test was conducted on combustible gas generated by the system 10 while combusting chicken litter. A sample run of 60 minutes in duration was performed.
Testing was performed in accordance with the methods detailed in 40 Code of Federal Regulations (CFR), Part 60, Appendix A. The flow, based on the lowest recordable flow, had a velocity of 6.77 feet per second, and the sample collected had a voluine of 41.42 dry standard cubic feet. The results of the emissions testing are summarized in Table 1 below.
Table 1 Substance Emissions lbs/hr Particulate Matter (based on lowest detectable flow rate) 0.003 VOC as Propane (corrected for moisture) 0.137 Nitrogen Oxides as NOZ 0.001 Carbon Monoxide 0.003 Sulfur Dioxide 0.096 Ammonia 0.033 HCl 0.008 Chloride 0.005 Example 2 An emissions test was conducted on combustible gas generated by the system 10 while combusting paper mill sludge. A sample run of 60 minutes in duration was performed.
Testing was performed in accordance with the metliods detailed in 40 CFR, Part 60, Appendix A. The flow, based on the lowest recordable flow, had a velocity of 6.53 feet per second, and the sample collected had a volume of 40.60 dry standard cubic feet. The results of the emissions testing are summarized in Table 2 below.
Table 2 Substance Emissions (lbs/hr) Particulate Matter (based on lowest detectable flow rate) 0.0014 VOC as Propane (corrected for moisture) 0.014 Nitrogen Oxides as NO2 0.013 Carbon Monoxide 0.051 Sulfur Dioxide 0.017 Other modifications, changes and substitutions are intended in the foregoing, and in some instances, some features of the invention will be employed without a corresponding use of other features. For example, the configuration of the ash support member 36 may be used in combination with any number of different gasification systems, regardless of whether such systems also use other features of the present invention, and may also find uses in systems other than gasification systems. Similarly, the wastewater return features of the present invention may be used in combination with any number of different gasification systems, regardless of whether such systems also use other features of the present invention, and may also find uses in systems other than gasification systems. Further, the wood chip filtering or other filters or catalysts of the present invention may be used in combination with any number of different gasification systems, regardless of whether such systems also use other features of the present invention, and may also find uses in systems other than gasification systems.
Further still, the hybrid blower 90 design of the present invention may be used in combination with any number of different gasification systems, regardless of whether such systems also use other features of the present invention, and may also find uses in systems other than gasification systems. Of course, quantitative information is included by way of exainple only and is not intended as a limitation as to the scope of the invention.
Accordingly, it is appropriate that the invention be construed broadly and in a manner consistent with the scope of the invention disclosed.
Claims
What is claimed is:
19. A combination, comprising:
a combustor having an upper outer wall portion and a lower base portion;
an inner wall disposed within said combustor, an upper portion of said inner wall being connected to said combustor to form an inner chamber and an outer chamber, a lower portion of said inner wall defining a first opening within said combustor;
an ash support member disposed within said combustor below said first opening, said ash support member being affixed within said combustor so that ash may spill from said ash support member over at least approximately 80 percent of an outer periphery of said ash support member.
20. The combination of claim 19, wherein said ash support member is affixed within said combustor so that ash may spill from said ash support member over at least approximately 90 percent of said outer periphery of said ash support member.
21. The combination of claim 19, further comprising:
a first agitating member disposed within said combustor above said opening;
and a second agitating member disposed within said combustor below said opening.
22. The combination of claim 21, further comprising a third agitating member disposed within said combustor above said opening.
23. The combination of claim 19, further comprising:
a scrubber, said scrubber being operably connected to said combustor to provide a flow path from said outer chamber of said combustor to said scrubber, a finisher, said finisher being operably connected to said scrubber; and one or more filters disposed in said finisher.
24. The combination of claim 19, further comprising:
a blower disposed downstream from said combustor and operably connected to said combustor for withdrawing a combustible gas from said combustor, said blower comprising:
an impeller housing;
an impeller disposed within said impeller housing; and a seal between portions of said impeller housing.
25. The combination of claim 24, wherein said blower further comprises:
a shaft affixed to said impeller; and at least two sets of bearings operably connected to said shaft.
19. A combination, comprising:
a combustor having an upper outer wall portion and a lower base portion;
an inner wall disposed within said combustor, an upper portion of said inner wall being connected to said combustor to form an inner chamber and an outer chamber, a lower portion of said inner wall defining a first opening within said combustor;
an ash support member disposed within said combustor below said first opening, said ash support member being affixed within said combustor so that ash may spill from said ash support member over at least approximately 80 percent of an outer periphery of said ash support member.
20. The combination of claim 19, wherein said ash support member is affixed within said combustor so that ash may spill from said ash support member over at least approximately 90 percent of said outer periphery of said ash support member.
21. The combination of claim 19, further comprising:
a first agitating member disposed within said combustor above said opening;
and a second agitating member disposed within said combustor below said opening.
22. The combination of claim 21, further comprising a third agitating member disposed within said combustor above said opening.
23. The combination of claim 19, further comprising:
a scrubber, said scrubber being operably connected to said combustor to provide a flow path from said outer chamber of said combustor to said scrubber, a finisher, said finisher being operably connected to said scrubber; and one or more filters disposed in said finisher.
24. The combination of claim 19, further comprising:
a blower disposed downstream from said combustor and operably connected to said combustor for withdrawing a combustible gas from said combustor, said blower comprising:
an impeller housing;
an impeller disposed within said impeller housing; and a seal between portions of said impeller housing.
25. The combination of claim 24, wherein said blower further comprises:
a shaft affixed to said impeller; and at least two sets of bearings operably connected to said shaft.
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US10/911,386 US20050155288A1 (en) | 2003-08-04 | 2004-08-04 | Gasification apparatus and method |
US10/911,386 | 2004-08-04 | ||
PCT/US2005/027682 WO2006017636A1 (en) | 2004-08-04 | 2005-08-04 | Gasification apparatus and method |
Publications (1)
Publication Number | Publication Date |
---|---|
CA2574020A1 true CA2574020A1 (en) | 2006-02-16 |
Family
ID=35839614
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CA002574020A Abandoned CA2574020A1 (en) | 2004-08-04 | 2005-08-04 | Gasification apparatus and method |
Country Status (8)
Country | Link |
---|---|
US (1) | US20050155288A1 (en) |
EP (1) | EP1799326A1 (en) |
JP (1) | JP2008509373A (en) |
CN (1) | CN101035604A (en) |
AU (1) | AU2005271442A1 (en) |
CA (1) | CA2574020A1 (en) |
MX (1) | MX2007001350A (en) |
WO (1) | WO2006017636A1 (en) |
Families Citing this family (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US7964026B2 (en) * | 2003-08-04 | 2011-06-21 | Power Reclamation, Inc. | Gasification apparatus |
US20050268556A1 (en) * | 2003-08-04 | 2005-12-08 | Power Reclamation, Inc. | Gasification apparatus and method |
US20080098653A1 (en) * | 2006-07-06 | 2008-05-01 | The Board Of Regents For Oklahoma State University | Downdraft gasifier with internal cyclonic combustion chamber |
US8657892B2 (en) * | 2007-07-05 | 2014-02-25 | The Board Of Regents For Oklahoma State University | Downdraft gasifier with internal cyclonic combustion chamber |
CN102192514B (en) * | 2011-06-30 | 2012-08-15 | 天津市碧奥达思科技有限公司 | Oxygen-deficiency pyrolyzing circular sludge incinerator |
AT513407B1 (en) * | 2011-07-14 | 2014-06-15 | Rep Renewable Energy Products Gmbh | Process for purifying a product gas and fine filter therefor |
US9096807B2 (en) * | 2012-03-09 | 2015-08-04 | General Electric Company | Biomass gasifier with disruption device |
US11242494B2 (en) | 2013-01-28 | 2022-02-08 | Aries Clean Technologies Llc | System and process for continuous production of contaminate free, size specific biochar following gasification |
US8721748B1 (en) * | 2013-01-28 | 2014-05-13 | PHG Energy, LLC | Device with dilated oxidation zone for gasifying feedstock |
EP3950606A1 (en) * | 2020-08-07 | 2022-02-09 | HBI S.r.l. | Biomass treatment process and plant |
Family Cites Families (48)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US360945A (en) * | 1887-04-12 | John d | ||
US2168652A (en) * | 1937-07-09 | 1939-08-08 | John U Mcdonald | Apparatus for producing gas |
US2240462A (en) * | 1939-12-23 | 1941-04-29 | Leah M Johnston | Illuminated signaling mailbox |
US2464473A (en) * | 1947-04-28 | 1949-03-15 | Utility Appliance Corp | Blower installation |
US2864677A (en) * | 1955-02-24 | 1958-12-16 | Texas Co | Gasification of solid carbonaceous materials |
NL300131A (en) * | 1962-11-15 | |||
US3361644A (en) * | 1965-05-13 | 1968-01-02 | Union Oil Co | Shale retorting process |
US3639261A (en) * | 1968-03-27 | 1972-02-01 | Texaco Inc | Process for the generation of synthesis gas from oil |
US3907519A (en) * | 1972-05-11 | 1975-09-23 | Chevron Res | Gasification of solid carbonaceous materials to obtain high BTU product gas |
US3817724A (en) * | 1972-05-11 | 1974-06-18 | Chevron Res | Gasification of solid carbonaceous waste material |
JPS49110164A (en) * | 1973-02-21 | 1974-10-19 | ||
US3971637A (en) * | 1974-12-23 | 1976-07-27 | Gulf Oil Corporation | Coal gasification process utilizing waste water from an external process |
US4087258A (en) * | 1975-02-05 | 1978-05-02 | Metallgesellschaft Aktiengesellschaft | Process for purifying raw gas from the gasification of solid fuels |
GB1544002A (en) * | 1976-10-21 | 1979-04-11 | Shell Int Research | Process for the separation of dry particulate matter from a hot gas |
US4117786A (en) * | 1977-05-24 | 1978-10-03 | United Technologies Corporation | Inlet air preheating for pyrolysis system |
US4233024A (en) * | 1978-11-20 | 1980-11-11 | Plass Vernon F | Apparatus for destructive distillation of cellulosic materials |
US4279234A (en) * | 1979-01-12 | 1981-07-21 | Texas Instruments Incorporated | Early fuel evaporation of carburetion system |
US4237780A (en) * | 1979-01-30 | 1980-12-09 | Andrew Truhan | Hydrocarbon fume disposal system particularly for use in paint spray booths |
FR2469447A1 (en) * | 1979-11-16 | 1981-05-22 | Pillard Chauffage | FIXED BED AND REVERSE DRAFT SOLID FUEL GASIFIER |
JPS56173830U (en) * | 1980-05-21 | 1981-12-22 | ||
US4306506A (en) * | 1980-06-02 | 1981-12-22 | Energy Recovery Research Group, Inc. | Gasification apparatus |
US4391205A (en) * | 1981-02-06 | 1983-07-05 | Morey Norval K | Method and apparatus for burning green wood chips |
US4428308A (en) * | 1981-11-30 | 1984-01-31 | Georgia Tech Research Institute | Linear down-draft biomass gasifier |
US4431405A (en) * | 1982-02-23 | 1984-02-14 | Down River International, Inc. | Gas pollution control apparatus and method and wood drying system employing same |
US4452611A (en) * | 1982-05-24 | 1984-06-05 | Richey Clarence B | Downdraft channel biomass gasifier |
US4659340A (en) * | 1985-06-24 | 1987-04-21 | Weaver Lloyd E | Pressurized downdraft gasifier |
US4584947A (en) * | 1985-07-01 | 1986-04-29 | Chittick Donald E | Fuel gas-producing pyrolysis reactors |
US5137702A (en) * | 1988-12-22 | 1992-08-11 | Mobil Oil Corporation | Regeneration of used alkanolamine solutions |
JPH04203496A (en) * | 1990-11-30 | 1992-07-24 | Nkk Corp | Seal device of centrifugal form blower |
US5101739A (en) * | 1991-01-04 | 1992-04-07 | Utah Environmental Energy, Inc. | Tire gassification and combustion system |
US5221484A (en) * | 1991-01-10 | 1993-06-22 | Ceramem Separations Limited Partnership | Catalytic filtration device and method |
US5226927A (en) * | 1991-02-13 | 1993-07-13 | Southern California Edison | Wood gasifier |
US5230716A (en) * | 1992-07-14 | 1993-07-27 | The United States Of America As Represented By The United States Department Of Energy | Grate assembly for fixed-bed coal gasifier |
US5922090A (en) * | 1994-03-10 | 1999-07-13 | Ebara Corporation | Method and apparatus for treating wastes by gasification |
US5407647A (en) * | 1994-05-27 | 1995-04-18 | Florida Scientific Laboratories Inc. | Gas-scrubber apparatus for the chemical conversion of toxic gaseous compounds into non-hazardous inert solids |
US5666890A (en) * | 1994-06-22 | 1997-09-16 | Craig; Joe D. | Biomass gasification system and method |
US5678494A (en) * | 1995-03-22 | 1997-10-21 | Ulrich; Gael | Biomass-fueled furnace |
US5799591A (en) * | 1997-02-14 | 1998-09-01 | Anderson; Berris M. | Incinerator for medical waste |
US6074623A (en) * | 1997-10-14 | 2000-06-13 | Vick; Steven C. | Process for thermal destruction of spent potliners |
JP4154029B2 (en) * | 1998-04-07 | 2008-09-24 | 株式会社東芝 | Waste treatment method and waste treatment apparatus |
GB9925199D0 (en) * | 1999-10-25 | 1999-12-22 | Mortimer Tech Holdings | Process for the production of gaseous fuel |
US20020146362A1 (en) * | 2001-04-09 | 2002-10-10 | Mcquigg Kevin | Method of filtration and cleansing of high temperature combustible gases |
US6863878B2 (en) * | 2001-07-05 | 2005-03-08 | Robert E. Klepper | Method and apparatus for producing synthesis gas from carbonaceous materials |
US20040006917A1 (en) * | 2002-07-09 | 2004-01-15 | Wakefield David W. | Clean fuel gas made by the gasification of coal |
US7301060B2 (en) * | 2003-03-28 | 2007-11-27 | Ab-Cwt, Llc | Process for conversion of organic, waste, or low-value materials into useful products |
US6769370B1 (en) * | 2003-06-17 | 2004-08-03 | Ming-Chuo Lee | Incinerator with a bowl-shaped grate |
US20050268556A1 (en) * | 2003-08-04 | 2005-12-08 | Power Reclamation, Inc. | Gasification apparatus and method |
US7964026B2 (en) * | 2003-08-04 | 2011-06-21 | Power Reclamation, Inc. | Gasification apparatus |
-
2004
- 2004-08-04 US US10/911,386 patent/US20050155288A1/en not_active Abandoned
-
2005
- 2005-08-04 EP EP05779367A patent/EP1799326A1/en not_active Withdrawn
- 2005-08-04 JP JP2007524973A patent/JP2008509373A/en active Pending
- 2005-08-04 CN CN200580033589.4A patent/CN101035604A/en active Pending
- 2005-08-04 AU AU2005271442A patent/AU2005271442A1/en not_active Abandoned
- 2005-08-04 CA CA002574020A patent/CA2574020A1/en not_active Abandoned
- 2005-08-04 WO PCT/US2005/027682 patent/WO2006017636A1/en active Application Filing
- 2005-08-04 MX MX2007001350A patent/MX2007001350A/en not_active Application Discontinuation
Also Published As
Publication number | Publication date |
---|---|
JP2008509373A (en) | 2008-03-27 |
AU2005271442A1 (en) | 2006-02-16 |
EP1799326A1 (en) | 2007-06-27 |
MX2007001350A (en) | 2007-04-02 |
CN101035604A (en) | 2007-09-12 |
US20050155288A1 (en) | 2005-07-21 |
WO2006017636A1 (en) | 2006-02-16 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US7964026B2 (en) | Gasification apparatus | |
CA2574020A1 (en) | Gasification apparatus and method | |
US4123332A (en) | Process and apparatus for carbonizing a comminuted solid carbonizable material | |
TWI687511B (en) | Solid fuel composition formed from mixed solid waste | |
US4344770A (en) | Method and apparatus for converting solid organic material to fuel oil and gas | |
US20050268556A1 (en) | Gasification apparatus and method | |
US3746521A (en) | Gasification method and apparatus | |
US20020046686A1 (en) | Gasifier | |
JP5938788B2 (en) | Method for thermochemical carbonization and gasification of wet biomass | |
CN103468319A (en) | Gasification of | |
JP2010533769A (en) | Steam hydrogenation gasification method and apparatus with increased conversion time | |
US8372166B2 (en) | Plasma assisted gasification system | |
US20110308157A1 (en) | Biomass gasification device and process | |
FI112798B (en) | Process and plant for gasification of a carbonaceous fuel in a fixed bed gasifier | |
US20120117875A1 (en) | Plasma assisted gasification system with agitator drive assembly in reactor vessel | |
US20120117877A1 (en) | Plasma assisted gasification system with internal syngas heater | |
WO2008010789A1 (en) | Gasification apparatus | |
JP4200255B2 (en) | Power generation apparatus and method using hydrocarbon as raw material | |
KR101205962B1 (en) | Method and a device to synthesis gas production from high moisturized organic waste over the course of the synthetic coal | |
CN206666457U (en) | The system that a kind of plastics pyrolytic gasification prepares oil product | |
EP3592830A1 (en) | Method and combined solid fuel gasifier for gasification of solid fuel | |
JPH09316464A (en) | Improvement of solid waste material slurry | |
JP2023116154A (en) | Fuel composition production method, waste gasification facility and operating method thereof | |
CN111690440A (en) | Pyrolysis vaporization treatment device for household garbage | |
US20100215551A1 (en) | Tyer hot gas filter and fluidized bed media cleaner |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
FZDE | Discontinued |