US20070012233A1 - Incineration methods and apparatus for enhanced destruction of volatile organic compounds - Google Patents

Incineration methods and apparatus for enhanced destruction of volatile organic compounds Download PDF

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Publication number
US20070012233A1
US20070012233A1 US11/444,536 US44453606A US2007012233A1 US 20070012233 A1 US20070012233 A1 US 20070012233A1 US 44453606 A US44453606 A US 44453606A US 2007012233 A1 US2007012233 A1 US 2007012233A1
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Prior art keywords
incinerator
destruction
emissivity
rating
voc
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US11/444,536
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Naiping Zhu
Louis Karambis
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Fosbel Intellectual Ltd
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Fosbel Intellectual Ltd
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Priority to US11/444,536 priority Critical patent/US20070012233A1/en
Assigned to FOSBEL INTELLECTUAL LIMITED reassignment FOSBEL INTELLECTUAL LIMITED ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: KARAMBIS, LOUIS A., ZHU, NAIPING
Publication of US20070012233A1 publication Critical patent/US20070012233A1/en
Assigned to GENERAL ELECTRIC CAPITAL CORPORATION, AS AGENT reassignment GENERAL ELECTRIC CAPITAL CORPORATION, AS AGENT SECURITY AGREEMENT Assignors: FOSBEL INTELLECTUAL LIMITED
Assigned to FOSBEL INTELLECTUAL LIMITED, FOSBEL, INC. reassignment FOSBEL INTELLECTUAL LIMITED RELEASE BY SECURED PARTY (SEE DOCUMENT FOR DETAILS). Assignors: GENERAL ELECTRIC CAPITAL CORPORATION, AS AGENT
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    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23MCASINGS, LININGS, WALLS OR DOORS SPECIALLY ADAPTED FOR COMBUSTION CHAMBERS, e.g. FIREBRIDGES; DEVICES FOR DEFLECTING AIR, FLAMES OR COMBUSTION PRODUCTS IN COMBUSTION CHAMBERS; SAFETY ARRANGEMENTS SPECIALLY ADAPTED FOR COMBUSTION APPARATUS; DETAILS OF COMBUSTION CHAMBERS, NOT OTHERWISE PROVIDED FOR
    • F23M5/00Casings; Linings; Walls
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/061Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
    • F23G7/065Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating using gaseous or liquid fuel
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23MCASINGS, LININGS, WALLS OR DOORS SPECIALLY ADAPTED FOR COMBUSTION CHAMBERS, e.g. FIREBRIDGES; DEVICES FOR DEFLECTING AIR, FLAMES OR COMBUSTION PRODUCTS IN COMBUSTION CHAMBERS; SAFETY ARRANGEMENTS SPECIALLY ADAPTED FOR COMBUSTION APPARATUS; DETAILS OF COMBUSTION CHAMBERS, NOT OTHERWISE PROVIDED FOR
    • F23M2900/00Special features of, or arrangements for combustion chambers
    • F23M2900/05004Special materials for walls or lining

Definitions

  • the present invention relates generally to the incineration of industrial waste gases and, in one aspect, to methods and systems for the enhanced incineration of industrial waste gases containing volatile organic compounds (VOCs).
  • VOCs volatile organic compounds
  • VOCs volatile organic compounds
  • VOCs in the plant air system are typically collected and fed into a mixing chamber of a thermal oxidizer where they are mixed in a burner flame zone with sufficient natural gas to sustain combustion.
  • the combustion chamber may also be provided with stream so as to prolong the residence time therewithin so as to achieve higher conversation rate.
  • thermal oxidizers are typically classified as having a so-called “two-nine” or better destruction capability, meaning that at least 99.0% or greater of the VOCs are incinerated.
  • the present invention is directed to methods and systems for enhanced destruction of industrial waste gases.
  • the present invention is directed to methods and systems whereby a high emissivity coating is applied to at least portions of the vessel walls of a direct fired incinerator, such as a thermal oxidizer, in order to enhance its incineration efficiencies, particularly for the incineration of VOCs.
  • a direct fired incinerator such as a thermal oxidizer
  • FIGURE is a schematic cross-sectional elevation view of an exemplary direct fired incinerator to incinerate VOC's in accordance with the present invention.
  • FIGURE depicts schematically an exemplary direct fired incinerator 10 that may be employed to incinerate VOC's in accordance with the present invention.
  • the incinerator 10 is provided with vessel walls 10 - 1 and a burner 10 - 2 which is supplied via line 10 - 3 with a combustible fuel (e.g., natural gas).
  • the incinerator 10 is also supplied with VOCs to be incinerated via line 104 .
  • the products of combustion namely carbon dioxide and water vapor, are removed from the incinerator 10 via flue 10 - 5 .
  • a coating layer 12 formed of a high emissivity (high-E) coating material is applied to the interior walls of a heated process vessel so as to enhance its thermal characteristics.
  • FIG. 1 schematically depicts the coating layer 12 is formed entirely on the inside of the incinerator walls 10 - 1 , it will be understood by those skilled in this art that the high-E coating material may be applied to one or both of the interior walls associated with the residence chamber or mixing/combustion chamber associated with a conventional thermal oxidizer.
  • the high-E coating material therefore allows the incinerator 10 (e.g., a thermal oxidizer) to achieve a higher degree of conversion and a higher VOC destruction rate.
  • the high-E coatings will have a higher surface temperature and a higher heat flux that will therefore result in more complete destruction of the VOCs.
  • a thermal oxidizer having a conventional two-nine (i.e., 99.0%) VOC destruction rating may have its capabilities increased to at least a three-nine (i.e., 99.9%) VOC destruction rating by employing a coating layer 12 formed of a high-E coating material according to the present invention.
  • industrial sites may improve substantially the VOC destruction capabilities without the significant added capitol costs associated with installation of thermal oxidizers having a greater initial VOC destruction rating.
  • the emissivity (E) of a material is meant to refer to a unitless number measured on a scale between zero (total energy reflection) and 1.0 (a perfect “black body” capable of total energy absorption and re-radiation).
  • a relatively high emissivity (high-E) is meant to refer to coating materials having an emissivity at 2000° F. of greater than about 0.70 to about 0.99, and usually between about 0.90 to about 0.99.
  • any commercially available high-E coating material may be employed satisfactorily in the practice of the present invention.
  • the CERAKTM ceramic coating materials commercially available from Cetek Ltd. of Berea, Ohio may be employed, with CERAKTM R371, R360 and R370 each having an emissivity of about 0.92 at 2000° F. being especially preferred.
  • Coating thicknesses on the walls 10 - 1 of the incinerator 10 are not critical but will vary in dependence upon the desired resulting thermal flux and/or the particular material forming the coating. Thus, coating thicknesses of from about 1 to about 60 mils may be appropriate for a given process vessel application, with coating densities typically being greater than about 65%, more specifically 80% or greater.
  • the high-E coating material may be applied to process vessel walls in any conventional manner during thermal oxidizer shutdown.
  • the high-E coating material may be applied to the process vessel walls via any pressurized spray system while the process vessel is off-line (i.e., is not at its operational temperatures).

Abstract

Methods and apparatus for enhanced destruction of industrial waste gases include coating a high emissivity material onto to at least portions of the vessel walls of a direct fired incinerator, such as a thermal oxidizer, in order to enhance its incineration efficiencies, particularly for the incineration of volatile organic compounds (VOCs).

Description

    CROSS-REFERENCE TO RELATED APPLICATION
  • This application is based on and claims domestic priority benefits under 35 USC §119(e) from, U.S. Provisional Application Ser. No. 60/686,428 filed on Jun. 2, 2005, the entire content of which is expressly incorporated hereinto by reference.
  • FIELD OF THE INVENTION
  • The present invention relates generally to the incineration of industrial waste gases and, in one aspect, to methods and systems for the enhanced incineration of industrial waste gases containing volatile organic compounds (VOCs).
  • BACKGROUND AND SUMMARY OF THE INVENTION
  • Air quality has increasingly become an issue of public concern. As a result of this public concern and governmental regulation, the scientific community has endeavored to reduce the amounts of environmentally toxic industrial waste materials. In this regard, a large part of air pollution is attributable to the release of volatile organic compounds (VOCs) into the atmosphere. As a result, the reduction of the release of VOCs has become an increasingly important part of the overall strategy to improve air quality.
  • The most common technique currently in use to control VOC emissions is to incinerate the VOCs in a thermal oxidizer. See in this regard, U.S. Pat. Nos. 5,832,713, 5,527,984 and 6,450,800, the entire content of each being expressly incorporated hereinto by reference. In this regard, the VOCs in the plant air system are typically collected and fed into a mixing chamber of a thermal oxidizer where they are mixed in a burner flame zone with sufficient natural gas to sustain combustion. The combustion chamber may also be provided with stream so as to prolong the residence time therewithin so as to achieve higher conversation rate. Therefore, according to prior proposals in this art, a large combustion and residence chamber is typically required so as to incinerate the VOCs as well as the fuel thereby producing carbon dioxide and water vapor as the primary combustion products. The incineration of the VOCs in a thermal oxidizer is not, however, entirely complete. Thus, thermal oxidizers are typically classified as having a so-called “two-nine” or better destruction capability, meaning that at least 99.0% or greater of the VOCs are incinerated.
  • While conventional thermal oxidizers do in fact destroy very substantial amounts of VOCs, there is a constant need to improve the efficiencies of such incineration so as to drive the amount of VOCs that are destroyed even higher than conventionally available. It is towards fulfilling such a need that the present invention is directed.
  • Broadly, the present invention is directed to methods and systems for enhanced destruction of industrial waste gases. In especially preferred embodiments, the present invention is directed to methods and systems whereby a high emissivity coating is applied to at least portions of the vessel walls of a direct fired incinerator, such as a thermal oxidizer, in order to enhance its incineration efficiencies, particularly for the incineration of VOCs.
  • These and other aspects and advantages will become more apparent after careful consideration is given to the following detailed description of the preferred exemplary embodiments thereof.
  • BRIEF DESCRIPTION OF THE ACCOMPANYING DRAWING
  • Reference will hereinafter be made to the accompanying drawing FIGURE which is a schematic cross-sectional elevation view of an exemplary direct fired incinerator to incinerate VOC's in accordance with the present invention.
  • DETAILED DESCRIPTION OF THE INVENTION
  • The accompanying FIGURE depicts schematically an exemplary direct fired incinerator 10 that may be employed to incinerate VOC's in accordance with the present invention. In this regard, the incinerator 10 is provided with vessel walls 10-1 and a burner 10-2 which is supplied via line 10-3 with a combustible fuel (e.g., natural gas). The incinerator 10 is also supplied with VOCs to be incinerated via line 104. The products of combustion, namely carbon dioxide and water vapor, are removed from the incinerator 10 via flue 10-5.
  • According to the present invention, a coating layer 12 formed of a high emissivity (high-E) coating material is applied to the interior walls of a heated process vessel so as to enhance its thermal characteristics. Although accompanying FIG. 1 schematically depicts the coating layer 12 is formed entirely on the inside of the incinerator walls 10-1, it will be understood by those skilled in this art that the high-E coating material may be applied to one or both of the interior walls associated with the residence chamber or mixing/combustion chamber associated with a conventional thermal oxidizer. The high-E coating material therefore allows the incinerator 10 (e.g., a thermal oxidizer) to achieve a higher degree of conversion and a higher VOC destruction rate. Specifically, the high-E coatings will have a higher surface temperature and a higher heat flux that will therefore result in more complete destruction of the VOCs.
  • By way of example, a thermal oxidizer having a conventional two-nine (i.e., 99.0%) VOC destruction rating may have its capabilities increased to at least a three-nine (i.e., 99.9%) VOC destruction rating by employing a coating layer 12 formed of a high-E coating material according to the present invention. As a result, by use of the present invention, industrial sites may improve substantially the VOC destruction capabilities without the significant added capitol costs associated with installation of thermal oxidizers having a greater initial VOC destruction rating.
  • As used herein, the emissivity (E) of a material is meant to refer to a unitless number measured on a scale between zero (total energy reflection) and 1.0 (a perfect “black body” capable of total energy absorption and re-radiation). According to the present invention, a relatively high emissivity (high-E) is meant to refer to coating materials having an emissivity at 2000° F. of greater than about 0.70 to about 0.99, and usually between about 0.90 to about 0.99.
  • Virtually any commercially available high-E coating material may be employed satisfactorily in the practice of the present invention. For example, the CERAK™ ceramic coating materials commercially available from Cetek Ltd. of Berea, Ohio may be employed, with CERAK™ R371, R360 and R370 each having an emissivity of about 0.92 at 2000° F. being especially preferred.
  • Coating thicknesses on the walls 10-1 of the incinerator 10 are not critical but will vary in dependence upon the desired resulting thermal flux and/or the particular material forming the coating. Thus, coating thicknesses of from about 1 to about 60 mils may be appropriate for a given process vessel application, with coating densities typically being greater than about 65%, more specifically 80% or greater.
  • The high-E coating material may be applied to process vessel walls in any conventional manner during thermal oxidizer shutdown. The high-E coating material may be applied to the process vessel walls via any pressurized spray system while the process vessel is off-line (i.e., is not at its operational temperatures).
  • While the invention has been described in connection with what is presently considered to be the most practical and preferred embodiment, it is to be understood that the invention is not to be limited to the disclosed embodiment, but on the contrary, is intended to cover various modifications and equivalent arrangements included within the spirit and scope of the appended claims.

Claims (18)

1. A method of increasing a volatile organic compound (VOC) destruction rating of a direct-fired incinerator comprising coating a layer of a high-emissivity (high-E) material on an interior wall of the incinerator in an amount sufficient to increase the VOC destruction rating of the incinerator as compared to the VOC destruction rating of the incinerator without the high-E coating layer.
2. The method of claim 1, wherein the incinerator has a VOC destruction rating of two-nine without the high-E coating on an interior wall thereof, and wherein the method comprises coating the high-E material on an interior wall of the incinerator sufficient to increase the VOC destruction rating to at least three-nine or greater.
3. The method of claim 1, wherein the high-E material is a ceramic material.
4. The method of claim 3, wherein the high-E ceramic material has an emissivity at 2000° F. of greater than about 0.70.
5. The method of claim 4, wherein the high-E ceramic material has an emissivity of between about 0.70 to about 0.99.
6. The method of claim 4, wherein the high-E ceramic material has an emissivity of between about 0.90 to about 0.99.
7. The method of claim 4, wherein the high-E ceramic material has an emissivity of about 0.92.
8. The method of claim 3, wherein the high-E coating layer has a thickness of between about 1 mil to about 60 mils.
9. The method of claim 8, wherein the high-E coating layer has a density of greater than about 65%.
10. In a direct-fired incinerator having a volatile organic compound (VOC) destruction rating for the incinerated destruction of volatile organic compounds, the incinerator including incinerator walls, a burner for incinerating the VOCs within an interior of the incinerator, and a supply of combustible fuel to the burner, the improvement comprising a coating a layer of a high-emissivity (high-E) material on an interior portion of the incinerator walls in an amount sufficient to increase the VOC destruction rating of the incinerator as compared to the VOC destruction rating of the incinerator without the high-E coating layer.
11. The incinerator of claim 10, wherein the incinerator has a VOC destruction rating of two-nine without the high-E coating on an interior portion of the incinerator walls thereof, and coating layer of the high-E material is sufficient to increase the VOC destruction rating to at least three-nine or greater.
12. The incinerator of claim 10, wherein the high-E material is a ceramic material.
13. The incinerator of claim 12, wherein the high-E ceramic material has an emissivity at 2000° F. of greater than about 0.70.
14. The incinerator of claim 13, wherein the high-E ceramic material has an emissivity of between about 0.70 to about 0.99.
15. The incinerator of claim 13, wherein the high-E ceramic material has an emissivity of between about 0.90 to about 0.99.
16. The incinerator of claim 15, wherein the high-E ceramic material has an emissivity of about 0.92.
17. The incinerator of claim 13, wherein the high-E coating layer has a thickness of between about 1 mil to about 60 mils.
18. The incinerator of claim 17, wherein the high-E coating layer has a density of greater than about 65%.
US11/444,536 2005-06-02 2006-06-01 Incineration methods and apparatus for enhanced destruction of volatile organic compounds Abandoned US20070012233A1 (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20070238058A1 (en) * 2006-01-27 2007-10-11 Fosbel Intellectual Limited Longevity and performance improvements to flare tips
US20110212010A1 (en) * 2009-09-02 2011-09-01 Despatch Industries Limited Partnership Apparatus and Method for Thermal Destruction of Volatile Organic Compounds
US8779208B2 (en) 2012-05-18 2014-07-15 Eastman Chemical Company Process for reducing emissions of volatile organic compounds from the ketonization of carboxylic acids
US10391470B2 (en) 2005-09-30 2019-08-27 Abs Materials, Inc. Sol-gel derived compositions

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2007091011A1 (en) * 2006-02-09 2007-08-16 Fosbel Intellectual Limited Refractory burner tiles having improved emissivity and combustion apparatus employing the same
CN106442856A (en) * 2016-10-13 2017-02-22 福建农林大学 Staying room device for simulating biomass burning in field

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US3195608A (en) * 1963-04-08 1965-07-20 Coen Co Volatile waste incinerator
US3933420A (en) * 1974-08-19 1976-01-20 Zink John S Vertically fired burner for waste combustible gases
US4828481A (en) * 1987-10-05 1989-05-09 Institute Of Gas Technology Process and apparatus for high temperature combustion
US5527984A (en) * 1993-04-29 1996-06-18 The Dow Chemical Company Waste gas incineration
US5832713A (en) * 1995-10-03 1998-11-10 Alliedsignal Inc. Method and apparatus for the destruction of volatile organic compounds
US6007873A (en) * 1996-05-09 1999-12-28 Equity Enterprises High emissivity coating composition and method of use
US6152050A (en) * 1995-12-14 2000-11-28 Pyrogenesis Inc. Lightweight compact waste treatment furnace
US6183707B1 (en) * 1992-06-08 2001-02-06 Biothermica International Inc. Incineration of waste gases containing contaminant aerosols
US6450800B1 (en) * 2000-04-05 2002-09-17 Megtec Systems Inc. Regenerative thermal oxidizer incorporating a venturi style burner
US6666911B2 (en) * 2001-10-16 2003-12-23 Zhong Huan Environment Advisor Corp. Treatment system for waste gas containing volatile organic compounds

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US3195608A (en) * 1963-04-08 1965-07-20 Coen Co Volatile waste incinerator
US3933420A (en) * 1974-08-19 1976-01-20 Zink John S Vertically fired burner for waste combustible gases
US4828481A (en) * 1987-10-05 1989-05-09 Institute Of Gas Technology Process and apparatus for high temperature combustion
US6183707B1 (en) * 1992-06-08 2001-02-06 Biothermica International Inc. Incineration of waste gases containing contaminant aerosols
US5527984A (en) * 1993-04-29 1996-06-18 The Dow Chemical Company Waste gas incineration
US5832713A (en) * 1995-10-03 1998-11-10 Alliedsignal Inc. Method and apparatus for the destruction of volatile organic compounds
US6152050A (en) * 1995-12-14 2000-11-28 Pyrogenesis Inc. Lightweight compact waste treatment furnace
US6007873A (en) * 1996-05-09 1999-12-28 Equity Enterprises High emissivity coating composition and method of use
US6450800B1 (en) * 2000-04-05 2002-09-17 Megtec Systems Inc. Regenerative thermal oxidizer incorporating a venturi style burner
US6666911B2 (en) * 2001-10-16 2003-12-23 Zhong Huan Environment Advisor Corp. Treatment system for waste gas containing volatile organic compounds

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10391470B2 (en) 2005-09-30 2019-08-27 Abs Materials, Inc. Sol-gel derived compositions
US20070238058A1 (en) * 2006-01-27 2007-10-11 Fosbel Intellectual Limited Longevity and performance improvements to flare tips
US20110212010A1 (en) * 2009-09-02 2011-09-01 Despatch Industries Limited Partnership Apparatus and Method for Thermal Destruction of Volatile Organic Compounds
US8779208B2 (en) 2012-05-18 2014-07-15 Eastman Chemical Company Process for reducing emissions of volatile organic compounds from the ketonization of carboxylic acids

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WO2006129063A1 (en) 2006-12-07

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