US20080127867A1 - Production of Synthetic Gas From Organic Waste - Google Patents
Production of Synthetic Gas From Organic Waste Download PDFInfo
- Publication number
- US20080127867A1 US20080127867A1 US11/757,189 US75718907A US2008127867A1 US 20080127867 A1 US20080127867 A1 US 20080127867A1 US 75718907 A US75718907 A US 75718907A US 2008127867 A1 US2008127867 A1 US 2008127867A1
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- United States
- Prior art keywords
- gas
- thermal oxidizer
- pyrolyzer
- heat
- burner
- 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.)
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Links
- 238000004519 manufacturing process Methods 0.000 title description 3
- 239000010815 organic waste Substances 0.000 title 1
- 239000007800 oxidant agent Substances 0.000 claims abstract description 34
- 239000002699 waste material Substances 0.000 claims abstract description 18
- 238000012546 transfer Methods 0.000 claims description 2
- 238000000197 pyrolysis Methods 0.000 abstract description 9
- 230000001105 regulatory effect Effects 0.000 abstract description 3
- 239000007789 gas Substances 0.000 description 29
- 238000000034 method Methods 0.000 description 5
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- 238000013461 design Methods 0.000 description 3
- 238000010438 heat treatment Methods 0.000 description 3
- 239000000567 combustion gas Substances 0.000 description 2
- 230000005611 electricity Effects 0.000 description 2
- 239000003345 natural gas Substances 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
Images
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/027—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
- F23G5/12—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating using gaseous or liquid fuel
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
- F23G5/14—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion
- F23G5/16—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion in a separate combustion chamber
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/30—Pyrolysing
- F23G2201/303—Burning pyrogases
Definitions
- the field of the invention is pyrolysis.
- both Walker '213 and Cole '069 patents contemplate that all of the heat used to pyrolyze the waste comes from the thermal oxidizer. There is no separate burner to provide heat directly to the pyrolyzer.
- the Walker '213 design splits the thermal oxidizer into two sections, each with its own burners. The burners of the first section are used to heat up the pyrolyzer upon cold start, and then to assist in burning the syn gas once pyrolysis is underway.
- the Cole '069 design shunts the combustion gasses from the thermal oxidizer into the outer chambers of dual pyrolyzers. Both designs turn out to be problematic because of difficulties in implementation.
- the pyrolyzer has its own burner(s), which can be controlled independently of the thermal oxidizer, but which can be down-regulated as heat from the thermal oxidizer is used to hear the pyrolyzer.
- the present invention provides systems, methods and devices in which a pyrolyzer has its own burner(s), which can be controlled independently of the thermal oxidizer, but which can be down-regulated as heat from the thermal oxidizer is used to hear the pyrolyzer.
- a device for pyrolytically treating a waste comprises a pyrolyzer and a thermal oxidizer, a first burner that primarily heats the pyrolyzer to produce a synthetic gas from the waste, a second burner that primarily assists in combusting the synthetic gas in the thermal oxidizer; and a heat transfer component that carries heat from the thermal oxidizer to the pyrolyzer.
- the first and second burners can advantageously receive a supply of extrinsic gas, such as from a natural gas line.
- One or more automatic controllers preferably adjust a burn rate of the extrinsic gas by the first burner as a function of a rate at which heat is transferred from the thermal oxidizer to the pyrolyzer.
- the burn rate of the extrinsic gas can be adjusted to ⁇ 50%, ⁇ 30% or even lower relative to a base rate that would be required to pyrolyze the waste without the heat thermal oxidizer.
- a line can carry a portion of the un-combusted or partially combusted syn gas to be burned along with the extrinsic gas at the first burner, which process can also be under the control of an automatic controller.
- FIG. 1 is a perspective view of a prior art pyrolysis system including a retort and a thermal oxidizer.
- FIG. 2 is a perspective view of a novel pyrolysis system in which combustion gas from the thermal oxidizer is used to assist in heating the pyrolyzer.
- FIG. 3 is a perspective view of a novel pyrolysis system in which syn gas is being fed to the burner of the pyrolyzer.
- FIG. 4 is a perspective view of a novel two level pyrolysis system in which combustion gas from the thermal oxidizer is used to assist in heating the pyrolyzer.
- a prior art pyrolytic device 100 includes an inner chamber 112 and an outer chamber 113 .
- a rotating drive 114 carries waste 111 through the inner chamber 112 , where the waste is subjected to heat to produce a combustible synthetic (“syn”) gas 116 and pyrolyzed solids 119 .
- the pyrolyzing heat is provided by a burner 120 , which burns natural or other extrinsic gas 117 and releases the exhaust into outer chamber 113 .
- Syn gas 116 generated by the process travels to the thermal oxidizer (“after burner”) 120 , where it is combined with air, and combusted along with additional extrinsic gas 127 .
- Combusted gas exhaust from the thermal oxidizer 120 is sent to the boiler of a power plant 130 to produce steam and ultimately, electricity. Details are provided in the patents and applications incorporated herein by reference.
- a novel pyrolytic device 200 includes all the listed components discussed above for device 100 .
- device 200 includes line 142 that carries combusted or semi-combusted gasses from the thermal oxidizer 120 to the outer chamber 113 of the pyrolyzer 110 , where they provide heat to pyrolyze the waste 111 .
- Exhaust from the pyrolyzer 110 can be used to dry waste 111 before it is fed into the pyrolyzer, utilized in operating the power plant, or utilized for any other purpose. Although not preferred, the exhaust could also be vented. Lines carrying the exhaust are not shown.
- the heat provided via line 142 can provide a majority or even all of the heat needed to pyrolyze the waste 111 .
- the balance of heat provided by combusting the extrinsic gas and the heat being provided via line 142 is automatically controlled by controller 150 . For example, if the natural gas or other extrinsic gas is being procured at very low cost, or if energy production is being maximized, the amount of heat being siphoned off via line 142 could be low or even zero.
- the controller could automatically adjust a burn rate of the extrinsic gas to below 50% of a base rate that would be required to pyrolyze the waste without the heat thermal oxidizer. That percentage could be cut further to below 30%, below 25%, below 20% and even down to zero for a period of time.
- controller could automatically adjusts relative amounts of the extrinsic and syn gasses as a function of a characteristic of the syn gas being produced. Suitable characteristics upon which to base the adjustments include quantity of syn gas, and relative amounts of combustible and non-combustible constituents of the syn gas.
- device 300 is similar to device 200 except that here some of the syn gas is ported to the burner 116 of the pyrolyzer 110 via line 144 . At present is a less preferred embodiment, and would generally make sense where the syn gas being ported has not yet been fully combusted.
- device 400 is again similar to device 200 .
- the pyrolyzer 110 and thermal oxidizer 120 are vertically disposed relative to one another rather than horizontally disposed.
- this configuration can provide much greater efficiency in terms of land usage.
- heat in the form of hot combusted or semi-combusted gasses
- line 146 heat (in the form of hot combusted or semi-combusted gasses) are ported from the thermal oxidizer 120 to the pyrolyzer 110 via line 146 .
- burner 116 is used primarily to heat the pyrolyzer 110 , to produce a synthetic gas from the waste 111 .
- the second burner 126 primarily assists in combusting the synthetic gas in the thermal oxidizer 120 .
- the term “primarily” refers to functions during normal steady-state operation, as opposed for example to start-up or shutdown procedures.
- the primary function of burner 66 in U.S. Pat. No. 6,619,214 is to provide heat to the thermal oxidizer 26 , not to heat the pyrolytic converter 24 .
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Processing Of Solid Wastes (AREA)
- Incineration Of Waste (AREA)
Abstract
A pyrolysis device has a pyrolyzer (retort) and a thermal oxidizer, each with its own burner, but coupled so that the burner of the pyrolyzer can be down-regulated as heat from the thermal oxidizer is used to hear the pyrolyzer. One or more automatic controllers preferably adjust a burn rate of the extrinsic gas by the first burner as a function of a rate at which heat is transferred from the thermal oxidizer to the pyrolyzer. In preferred embodiments, the burn rate of the extrinsic gas can be adjusted to ≦50%, ≦30% or even lower relative to a base rate that would be required to pyrolyze the waste without the heat thermal oxidizer.
Description
- This application claims priority to provisional application Ser. No. 60/810382 filed Jun. 1, 2006.
- The field of the invention is pyrolysis.
- Pyrolysis of wastes often produces combustible gases (i.e., synthetic or syn gases) that can be burned in a thermal oxidizer to produce heat, and ultimately to generate electricity. US619214 to Walker et al. (September '03) and U.S. Pat. No. 7,044,069 to Cole et al. May 2006) teach that some of the heat produced by oxidation of the syn gas can also be used for other purposes, including heating of the reaction chamber of the pyrolytic converter (also referred to herein as the pyrolyzer), and drying of the waste prior to pyrolysis.
- Various other improvements are described in patents and applications of the same family, including US700551 (February '06), U.S. Pat. No. 6,988,453 (January 2006), US2005/0039651 (February 2005), U.S. Pat. No. 7,191,714 (March 2007), and US 11/286552 (filed Nov. 22, 2005). These and all other extrinsic materials referenced herein are incorporated by reference in their entirety. Where a definition or use of a term in an incorporated reference is inconsistent or contrary to the definition of that term provided herein, the definition of that term provided herein applies and the definition of that term in the reference does not apply.
- Significantly, both Walker '213 and Cole '069 patents contemplate that all of the heat used to pyrolyze the waste comes from the thermal oxidizer. There is no separate burner to provide heat directly to the pyrolyzer. The Walker '213 design splits the thermal oxidizer into two sections, each with its own burners. The burners of the first section are used to heat up the pyrolyzer upon cold start, and then to assist in burning the syn gas once pyrolysis is underway. The Cole '069 design shunts the combustion gasses from the thermal oxidizer into the outer chambers of dual pyrolyzers. Both designs turn out to be problematic because of difficulties in implementation.
- What is needed are systems and methods in which the pyrolyzer has its own burner(s), which can be controlled independently of the thermal oxidizer, but which can be down-regulated as heat from the thermal oxidizer is used to hear the pyrolyzer.
- The present invention provides systems, methods and devices in which a pyrolyzer has its own burner(s), which can be controlled independently of the thermal oxidizer, but which can be down-regulated as heat from the thermal oxidizer is used to hear the pyrolyzer.
- In preferred embodiments of the apparatus, a device for pyrolytically treating a waste comprises a pyrolyzer and a thermal oxidizer, a first burner that primarily heats the pyrolyzer to produce a synthetic gas from the waste, a second burner that primarily assists in combusting the synthetic gas in the thermal oxidizer; and a heat transfer component that carries heat from the thermal oxidizer to the pyrolyzer. The first and second burners can advantageously receive a supply of extrinsic gas, such as from a natural gas line.
- One or more automatic controllers preferably adjust a burn rate of the extrinsic gas by the first burner as a function of a rate at which heat is transferred from the thermal oxidizer to the pyrolyzer. In preferred embodiments, the burn rate of the extrinsic gas can be adjusted to ≦50%, ≦30% or even lower relative to a base rate that would be required to pyrolyze the waste without the heat thermal oxidizer.
- It is also contemplated that a line can carry a portion of the un-combusted or partially combusted syn gas to be burned along with the extrinsic gas at the first burner, which process can also be under the control of an automatic controller.
- Various objects, features, aspects and advantages of the present invention will become more apparent from the following detailed description of preferred embodiments of the invention, along with the accompanying drawings in which like numerals represent like components.
-
FIG. 1 is a perspective view of a prior art pyrolysis system including a retort and a thermal oxidizer. -
FIG. 2 is a perspective view of a novel pyrolysis system in which combustion gas from the thermal oxidizer is used to assist in heating the pyrolyzer. -
FIG. 3 is a perspective view of a novel pyrolysis system in which syn gas is being fed to the burner of the pyrolyzer. -
FIG. 4 is a perspective view of a novel two level pyrolysis system in which combustion gas from the thermal oxidizer is used to assist in heating the pyrolyzer. - In
FIG. 1 , a prior artpyrolytic device 100 includes aninner chamber 112 and anouter chamber 113. A rotatingdrive 114 carrieswaste 111 through theinner chamber 112, where the waste is subjected to heat to produce a combustible synthetic (“syn”)gas 116 and pyrolyzedsolids 119. The pyrolyzing heat is provided by aburner 120, which burns natural or otherextrinsic gas 117 and releases the exhaust intoouter chamber 113.Syn gas 116 generated by the process travels to the thermal oxidizer (“after burner”) 120, where it is combined with air, and combusted along with additionalextrinsic gas 127. Combusted gas exhaust from thethermal oxidizer 120 is sent to the boiler of apower plant 130 to produce steam and ultimately, electricity. Details are provided in the patents and applications incorporated herein by reference. - In
FIG. 2 , a novelpyrolytic device 200 includes all the listed components discussed above fordevice 100. In addition,device 200 includesline 142 that carries combusted or semi-combusted gasses from thethermal oxidizer 120 to theouter chamber 113 of thepyrolyzer 110, where they provide heat to pyrolyze thewaste 111. Exhaust from thepyrolyzer 110 can be used to drywaste 111 before it is fed into the pyrolyzer, utilized in operating the power plant, or utilized for any other purpose. Although not preferred, the exhaust could also be vented. Lines carrying the exhaust are not shown. - Once syn gas is being produced in good quantity, and depending upon selected operating parameters, the heat provided via
line 142 can provide a majority or even all of the heat needed to pyrolyze thewaste 111. In especially preferred embodiments, the balance of heat provided by combusting the extrinsic gas and the heat being provided vialine 142 is automatically controlled bycontroller 150. For example, if the natural gas or other extrinsic gas is being procured at very low cost, or if energy production is being maximized, the amount of heat being siphoned off vialine 142 could be low or even zero. On the other hand, if the extrinsic gas is relatively expensive, or if energy production is not being maximized, or perhaps more heat is being generated that can be effectively used in the power plant, relatively more heat could be siphoned off vialine 142. It is contemplated that the controller could automatically adjust a burn rate of the extrinsic gas to below 50% of a base rate that would be required to pyrolyze the waste without the heat thermal oxidizer. That percentage could be cut further to below 30%, below 25%, below 20% and even down to zero for a period of time. - It is also contemplated that the controller could automatically adjusts relative amounts of the extrinsic and syn gasses as a function of a characteristic of the syn gas being produced. Suitable characteristics upon which to base the adjustments include quantity of syn gas, and relative amounts of combustible and non-combustible constituents of the syn gas.
- Given this disclosure, development and appreciation of contemplated electronic and other controls are well within the skill of those in the art, including for example Johnson Controls™.
- In
FIG. 3 ,device 300 is similar todevice 200 except that here some of the syn gas is ported to theburner 116 of thepyrolyzer 110 vialine 144. At present is a less preferred embodiment, and would generally make sense where the syn gas being ported has not yet been fully combusted. - In
FIG. 4 ,device 400 is again similar todevice 200. One major difference is that here thepyrolyzer 110 andthermal oxidizer 120 are vertically disposed relative to one another rather than horizontally disposed. Among other things, this configuration can provide much greater efficiency in terms of land usage. In this particular instance, heat (in the form of hot combusted or semi-combusted gasses) are ported from thethermal oxidizer 120 to thepyrolyzer 110 vialine 146. - It should be appreciated that in each of
FIGS. 2-4 ,burner 116 is used primarily to heat thepyrolyzer 110, to produce a synthetic gas from thewaste 111. Similarly, in each ofFIGS. 2-4 , thesecond burner 126 primarily assists in combusting the synthetic gas in thethermal oxidizer 120. As used herein, the term “primarily” refers to functions during normal steady-state operation, as opposed for example to start-up or shutdown procedures. In contrast, the primary function of burner 66 in U.S. Pat. No. 6,619,214 is to provide heat to the thermal oxidizer 26, not to heat the pyrolytic converter 24. - It should also be apparent to those skilled in the art that many more modifications besides those already described are possible without departing from the inventive concepts herein. Moreover, in interpreting the disclosure, all terms should be interpreted in the broadest possible manner consistent with the context. In particular, the terms “comprises” and “comprising” should be interpreted as referring to elements, components, or steps in a non-exclusive manner, indicating that the referenced elements, components, or steps could be present, or utilized, or combined with other elements, components, or steps that are not expressly referenced. Where the specification claims refers to at least one of something selected from the group consisting of A, B, C . . . and N, the text should be interpreted as requiring only one element from the group, not A plus N, or B plus N, etc.
Claims (7)
1. A device for pyrolytically treating a waste, comprising:
a pyrolyzer and a thermal oxidizer;
a first burner that primarily heats the pyrolyzer to produce a synthetic gas from the waste;
a second burner that primarily assists in combusting the synthetic gas in the thermal oxidizer; and
a heat transfer component that carries heat from the thermal oxidizer to the pyrolyzer.
2. The device of claim 1 , wherein the first burner receives a supply of extrinsic gas.
3. The device of claim 2 , further comprising a controller that automatically adjusts a burn rate of the extrinsic gas by the first burner as a function of a rate at which heat is transferred from the thermal oxidizer to the pyrolyzer.
4. The device of claim 2 , further comprising a controller that automatically adjusts a burn rate of the extrinsic gas to below 50% of a base rate that would be required to pyrolyze the waste without the heat thermal oxidizer.
5. The device of claim 2 , further comprising a controller that automatically adjusts a burn rate of the extrinsic gas to below 30% of a base rate that would be required to pyrolyze the waste without the heat thermal oxidizer.
6. The device of claim 2 , further comprising a controller that automatically adjusts relative amounts of the extrinsic and syn gasses combusted by the first burner as a function of a characteristic of the syn gas.
7. The device of claim 1 , further comprising a line that carries a portion of the syn gas to the first burner.
Priority Applications (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US11/757,189 US20080127867A1 (en) | 2006-06-01 | 2007-06-01 | Production of Synthetic Gas From Organic Waste |
US11/862,378 US20080072805A1 (en) | 2006-06-01 | 2007-09-27 | Piggybacked Pyrolyzer and Thermal Oxidizer |
PCT/US2008/001020 WO2008153607A2 (en) | 2007-06-01 | 2008-01-23 | Piggybacked pyrolizer and thermal oxidizer |
US13/081,749 US20110271882A1 (en) | 2006-06-01 | 2011-04-07 | Piggybacked Pyrolyzer and Thermal Oxidizer With Enhanced Exhaust Gas Transfer |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US81038206P | 2006-06-01 | 2006-06-01 | |
US11/757,189 US20080127867A1 (en) | 2006-06-01 | 2007-06-01 | Production of Synthetic Gas From Organic Waste |
Related Child Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
US11/862,378 Continuation-In-Part US20080072805A1 (en) | 2006-06-01 | 2007-09-27 | Piggybacked Pyrolyzer and Thermal Oxidizer |
Publications (1)
Publication Number | Publication Date |
---|---|
US20080127867A1 true US20080127867A1 (en) | 2008-06-05 |
Family
ID=40130610
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
US11/757,189 Abandoned US20080127867A1 (en) | 2006-06-01 | 2007-06-01 | Production of Synthetic Gas From Organic Waste |
Country Status (2)
Country | Link |
---|---|
US (1) | US20080127867A1 (en) |
WO (1) | WO2008153607A2 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2010011137A2 (en) * | 2008-07-19 | 2010-01-28 | Btg Biomass Technology Group B.V. | Device for treating organic material |
US20100326338A1 (en) * | 2009-06-24 | 2010-12-30 | Kimmo Ahola | Device for Gasification and Combustion of Solid Fuel |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US9534510B2 (en) | 2011-03-07 | 2017-01-03 | Dynamis Energy, Llc | System and method for thermal chemical conversion of waste |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4084521A (en) * | 1975-05-09 | 1978-04-18 | Helma Lampl | Method and apparatus for the pyrolysis of waste products |
US4517906A (en) * | 1983-08-30 | 1985-05-21 | Zimpro Inc. | Method and apparatus for controlling auxiliary fuel addition to a pyrolysis furnace |
US5411714A (en) * | 1992-04-06 | 1995-05-02 | Wu; Arthur C. | Thermal conversion pyrolysis reactor system |
US6619214B2 (en) * | 2001-06-20 | 2003-09-16 | Karen Meyer Bertram | Method and apparatus for treatment of waste |
US6988453B2 (en) * | 2003-08-21 | 2006-01-24 | International Environmental Solutions Corporation | Outlets for a pyrolytic waste treatment system |
US7191714B2 (en) * | 2003-08-21 | 2007-03-20 | International Enviornmental Solutions Corporation | Shaft seal for a pyrolytic waste treatment system |
US20070113761A1 (en) * | 2005-11-22 | 2007-05-24 | Cameron Cole | Pyrolytic waste treatment system having dual knife gate valves |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR960700328A (en) * | 1992-12-30 | 1996-01-19 | 아더 이. 푸니어 2세 | High performance coal gasifier system |
US5826520A (en) * | 1996-07-30 | 1998-10-27 | Tempyrox Company, Inc. | Apparatus and process for high temperature cleaning of organic contaminants from fragile parts in a self-inerting atmosphere at below the temperature of combustion |
US6758150B2 (en) * | 2001-07-16 | 2004-07-06 | Energy Associates International, Llc | System and method for thermally reducing solid and liquid waste and for recovering waste heat |
KR100677727B1 (en) * | 2002-06-03 | 2007-02-02 | 호누아 테크놀로지즈 인코포레이티드 | Pyrolysis methods for medical and other wastes |
-
2007
- 2007-06-01 US US11/757,189 patent/US20080127867A1/en not_active Abandoned
-
2008
- 2008-01-23 WO PCT/US2008/001020 patent/WO2008153607A2/en active Application Filing
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4084521A (en) * | 1975-05-09 | 1978-04-18 | Helma Lampl | Method and apparatus for the pyrolysis of waste products |
US4517906A (en) * | 1983-08-30 | 1985-05-21 | Zimpro Inc. | Method and apparatus for controlling auxiliary fuel addition to a pyrolysis furnace |
US5411714A (en) * | 1992-04-06 | 1995-05-02 | Wu; Arthur C. | Thermal conversion pyrolysis reactor system |
US6619214B2 (en) * | 2001-06-20 | 2003-09-16 | Karen Meyer Bertram | Method and apparatus for treatment of waste |
US6988453B2 (en) * | 2003-08-21 | 2006-01-24 | International Environmental Solutions Corporation | Outlets for a pyrolytic waste treatment system |
US7000551B2 (en) * | 2003-08-21 | 2006-02-21 | International Environmental Solutions Corporation | Chamber support for pyrolytic waste treatment system |
US7044069B2 (en) * | 2003-08-21 | 2006-05-16 | International Environmental Solutions Corporation | Multi retort pyrolytic waste treatment system |
US7191714B2 (en) * | 2003-08-21 | 2007-03-20 | International Enviornmental Solutions Corporation | Shaft seal for a pyrolytic waste treatment system |
US20070113761A1 (en) * | 2005-11-22 | 2007-05-24 | Cameron Cole | Pyrolytic waste treatment system having dual knife gate valves |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2010011137A2 (en) * | 2008-07-19 | 2010-01-28 | Btg Biomass Technology Group B.V. | Device for treating organic material |
WO2010011137A3 (en) * | 2008-07-19 | 2010-06-24 | Btg Biomass Technology Group B.V. | Device for treating organic material |
NL2003238C2 (en) * | 2008-07-19 | 2010-07-13 | Btg Biomass Technology Group B V | DEVICE FOR TREATING ORGANIC MATERIAL. |
US20100326338A1 (en) * | 2009-06-24 | 2010-12-30 | Kimmo Ahola | Device for Gasification and Combustion of Solid Fuel |
US8459192B2 (en) * | 2009-06-24 | 2013-06-11 | Kimmo Ahola | Device for gasification and combustion of solid fuel |
Also Published As
Publication number | Publication date |
---|---|
WO2008153607A2 (en) | 2008-12-18 |
WO2008153607A3 (en) | 2009-12-30 |
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