WO2009070563A1 - Flameless thermal oxidation apparatus and methods - Google Patents
Flameless thermal oxidation apparatus and methods Download PDFInfo
- Publication number
- WO2009070563A1 WO2009070563A1 PCT/US2008/084637 US2008084637W WO2009070563A1 WO 2009070563 A1 WO2009070563 A1 WO 2009070563A1 US 2008084637 W US2008084637 W US 2008084637W WO 2009070563 A1 WO2009070563 A1 WO 2009070563A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- fluid stream
- fuels
- oxidation chamber
- oxidation
- components
- Prior art date
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/06—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
- F23G7/061—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
- F23G7/065—Incinerators 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
- F23G7/066—Incinerators 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 preheating the waste gas by the heat of the combustion, e.g. recuperation type incinerator
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C2900/00—Special features of, or arrangements for combustion apparatus using fluid fuels or solid fuels suspended in air; Combustion processes therefor
- F23C2900/99001—Cold flame combustion or flameless oxidation processes
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
Definitions
- This invention relates generally to thermal oxidizers used to oxidize organic compounds in process streams and, more particularly, to apparatus and methods of operating such thermal oxidizers using flameless thermal oxidation to decompose the organic compounds.
- Thermal oxidizers are commonly used to oxidize one or more gases or vapors in a process stream by subjecting them to high temperatures before the process stream is released to the atmosphere.
- the gases in the process stream are commonly referred to as off-gases and typically consist of volatile organic compounds (VOCs), semi-volatile organic compounds (SVOCs), and/or hazardous air pollutants (HAPs).
- VOCs volatile organic compounds
- SVOCs semi-volatile organic compounds
- HAPs hazardous air pollutants
- the process stream containing the off-gases is frequently a byproduct of an industrial, manufacturing, or power generating process.
- the off-gases are oxidized to form carbon dioxide and water by combining the process stream with a gas stream that contains oxygen and then passing the combined stream through a flame or combustion gases produced by burning a fuel source such as natural gas.
- a fuel source such as natural gas.
- a mixture of gases or vapors with air and/or oxygen flows into a bed matrix of solid heat-resistant material which has been preheated to a temperature above the autoignition temperature of the mixture.
- the mixture ignites and reacts exothermally in the bed matrix to form a self-sustaining reaction wave within the bed matrix.
- the process is used to minimize production of NOx, CO, and other products of incomplete combustion during destruction of a particular gas or vapor in a process stream prior to release of the process stream to the atmosphere.
- Emission levels of thermal-NOx of less than 0.007 Ib of NOx (as NO 2 ) per million BTU and CO levels below 10 ppm are said to be obtainable using the described method.
- Patent No. 5,165,884 is advantageous in that it anchors and stabilizes the reaction wave during the combustion process.
- the bed matrix occupies a substantial portion of the internal volume of the process reactor, thereby reducing the open volume available for the flow of the process stream.
- the reduction in open volume in the reactor reduces the available residence time for a given reactor size at a given throughput of the process stream, thus reducing the time available for destruction of hazardous wastes, hi addition, the bed matrix creates a substantial pressure drop that adds to the operating costs of the process because the process stream must be subjected to an increased pressure before it enters the process reactor. This pressure drop tends to increase over time as particulate matter from the process stream accumulates in the bed matrix or the bed material degrades due to thermal shock. Eventually, the increase in pressure drop across the bed matrix may require replacement of the bed material. [0007] A need has thus developed for a thermal oxidizer that generates low levels of NOx and CO without the disadvantages described above.
- the present invention provides a method for thermally oxidizing components, such as those contained in a fluid stream, in an oxidation chamber having an internal lining which transfers sufficient heat for causing the thermal oxidation of the components in the fluid stream.
- the method comprises initially heating the oxidation chamber lining and then delivering the components to the oxidation chamber under conditions to initiate thermal oxidation of the components as a result of heat transfer from the oxidation chamber lining.
- the step of initially heating the oxidation chamber lining comprises heating the lining to a preselected temperature which is sufficient to radiate or otherwise transfer enough heat to initiate the thermal oxidation of the components in the fluid stream.
- the components which may include one or more fuels, are delivered to the oxidation chamber in a fluid stream.
- the conditions in the fluid stream are controlled to cause the flameless thermal oxidation of the components in the fluid stream as a result of heat transfer from the refractory lining.
- the present method thus relies on heat transfer from the refractory lim ' ng to initiate and sustain the flameless thermal oxidation and does not require a bed matrix, preheating of the fuel stream and/or combustion air stream, or flue gas recirculation as required by conventional flameless oxidation processes.
- one or more fuel components in the fluid stream are combusted in a visible flame to cause the initial heating of the refractory lining to the preselected temperature.
- the overall concentration of the fuel components in the fluid stream can be within the flammability range during this startup mode. Alternatively, the overall concentration of the fuel components is outside of the flammability range, but a flammable mixture results by not completely mixing the fuel components with the combustion air which is present in the fluid stream so that a diffusion or partially premixed flame results.
- the flame in the fluid stream is extinguished, such as by increasing the mixing of the fuel and combustion air to move the localized concentrations of the fuel components outside of the flammability range to prevent combustion of the mixture in a visible flame within the burner.
- Other methods for changing the localized concentrations of the fuel components outside of the flammability range can be used.
- Volatile organic compounds, semi -volatile organic compounds, and/or hazardous air pollutants may be present as additional components in the fluid stream and are thermally oxidized during the flameless thermal oxidation mode. These additional components typically originate in a process stream from an industrial, manufacturing, or power generating process and must be removed prior to release of the process stream to the atmosphere. The process stream can supply some, all, or none of the combustion air required in the process.
- supplemental heat can be added to the oxidation chamber to offset thermal losses through an external shell of the oxidation chamber or the cooling effect of the fluid stream.
- the supplemental heat can be added continuously, such as by burning one or more fuels in another fluid stream in the oxidation chamber in a visible flame. Alternatively, the supplemental heat can be added intermittently, such as by periodically operating the thermal oxidizer in the initial heating mode.
- FIG. 1 is a top elevation view of a thermal oxidizer in accordance with one embodiment of the present invention with portions of the thermal oxidizer broken away to show details of construction;
- FIG. 2 is an enlarged side elevation view, taken in vertical section, of a burner portion of the thermal oxidizer with certain portions shown schematically.
- FIG. 1 one embodiment of a thermal oxidizer useful in the flameless thermal oxidation of components in a fluid stream is broadly represented by the numeral 10.
- the fluid stream is designated by an arrow 11 and typically is a gas or vapor stream which flows in a continuous or intermittent fashion within the thermal oxidizer 10.
- the oxidizable components in the fluid stream 1 1 can be in gas, liquid, and/or solid particulate form. Examples of these components include fuels, waste products, organic compounds, including volatile organic compounds and semi- volatile organic compounds, and/or hazardous air pollutants.
- Thermal oxidizer 10 comprises a thermal oxidation chamber 12 having an exterior shell 14 lined with one or more layers of a refractory lining 16 formed of a material, such as any of various refractory materials, having the chemical and physical properties necessary to withstand the high operating temperatures and other conditions present within the thermal oxidation chamber 12.
- the refractory lining 16 may be in castable, plastic, brick, blanket, fibrous, or any other suitable form and typically comprises primarily ceramic materials made from combinations of high-melting oxides such as aluminum oxide, silicon dioxide, or magnesium oxide.
- the refractory lining 16 may also be formed of other materials such as refractory metals.
- Suitable refractory metals include molybdenum, tungsten, tantalum, rhenium, and niobium, as well as alloys of these metals.
- the innermost or "hot face" refractory lining 16 is preferably backed with a lower thermal conductivity lining 17 to further reduce thermal losses through the exterior shell 14.
- the internal area within the lined shell 14 defines an open interior volume 18 within which the flameless thermal oxidation occurs, as more fully described below.
- the open interior volume 1 S is sized so that the desired residence time is obtained for the fluid stream 11 flowing through the thermal oxidation chamber 12 at the intended volumetric flow rate for the specific process applications being performed. Normally, the residence time is selected so that complete combustion and/or the desired destruction removal efficiency is obtained for the oxidizable components in the process stream.
- the shell 14 is preferably cylindrical and horizontally oriented, but it may alternatively have a cross section which is of a polygonal or other configuration and/or it may be oriented vertically or at an intermediate angle.
- the shell 14 has an at least partially open upstream end 20 and an opposite, at least partially open, downstream end 22.
- upstream and downstream are used with reference to the intended direction of flow of the fluid stream 11 through the oxidation chamber 12 during operation of the thermal oxidizer 10.
- Thermal oxidizer 10 further includes a burner 24 connected to the upstream end 20 of the thermal oxidation chamber 12 by an optional transition 26.
- the downstream end 22 of chamber 12 is connected by a similar optional transition 28 to an exhaust stack 30 through which the flue gas reaction products resulting from the thermal oxidation process are released to the atmosphere.
- the downstream end of the chamber 12 may be in fluid flow communication with downstream equipment 31 that would benefit from a low NOx, low CO, high temperature fluid stream.
- downstream equipment 31 include but are not limited to process heaters, boilers, reactor furnaces such as those of ethylene cracking units, hydrogen reformers and the like, air heaters, dryers, gas turbines, and heat exchangers.
- the thermal oxidizer 10 can thus be used to provide a hot flue gas stream, which is low in NOx and CO levels, in lieu of all or a portion of the traditional method for firing the downstream equipment.
- Burner 24 is a forced draft burner that generates a strong vortex to insure thorough premixing of combustion air and fuel gas.
- Burner 24 is preferably fueled by a gas, typically natural gas or a refinery fuel gas, but other fuel gases such as hydrogen, methane, ethane, propane, butane, other hydrocarbons, carbon monoxide, and various blends thereof, can be used.
- a gas typically natural gas or a refinery fuel gas
- other fuel gases such as hydrogen, methane, ethane, propane, butane, other hydrocarbons, carbon monoxide, and various blends thereof, can be used.
- Various additives and diluents, such as nitrogen, carbon dioxide, and/or water vapor can also be added to or are present in the gas.
- Some or all of the fuel may be in liquid or solid particulate form.
- Other types of burners such as an induced draft burner, natural draft burner, premixed burner, and partial premised burner, can also be used.
- burner 24 comprises an exterior housing 32 which is lined with one or more layers of a refractory lining 34 of the type previously described.
- An insulating lining 35 may also be placed between the hot face refractory lining 34 and the inner surface of the exterior housing 32.
- the housing 32 is preferably cylindrical, but can have a cross section which is of polygonal or other configuration.
- the housing 32 has a side wall 36 and opposed upstream and downstream ends 38 and 40, respectively.
- the lined housing 32 defines an open interior antechamber 42 which is in fluid- flow communication with the oxidation chamber 12 positioned downstream from the burner 24.
- a choke 44 formed of refractory material may be positioned at the downstream end 40 of the burner housing 32 to provide a reduced diameter passageway 45 from the antechamber 42 to the downstream oxidation chamber 12.
- the choke 44 may have the rectangular cross section as illustrated in the drawings or it may be formed with inwardly sloping inlet and outlet ends to form a more aerodynamic structure. The choke 44 may be omitted in certain applications.
- a nozzle assembly 46 is positioned at the upstream end 38 of the burner housing 32 for delivery of a combustible fuel and air mixture into the antechamber 42.
- nozzle assembly 46 comprises an elongated, centrally-positioned fuel gun 48 which is supplied with fuel from a fuel source 50 by a conduit 52.
- a suitable flow regulator 54 regulates the volumetric flow rate of fuel to the fuel gun 48.
- the fuel gun 48 terminates in a fuel tip 56 having orifices (not shown) through which a fuel stream designated by arrow 57 is discharged into the antechamber 42.
- the fuel gun 48 may be moveable in an axial direction so that the positioning of the fuel tip 56 may be varied in relation to a surrounding throat structure 58 which has a reduced cross-sectional area, as more fully described below.
- a second fuel tip associated with the fuel gun 48 or another fuel gun may be displaced from the first fuel tip 56 so that fuel may be injected at different positions in relation to the throat structure 58.
- the fuel gun 48 is surrounded by a canister 59 in which a plurality of swirl vanes 60 are positioned in a ring-shaped opening that extends around the circumference of the canister 59.
- the swirl vanes 60 are mounted to spaced apart rings 63a and 63b which are secured to the canister 59 adjacent the ring-shaped opening.
- the ring 63a positioned closest to the fuel tip 56 has an inner diameter which is substantially the same as the inner diameter of the canister 59 so that it does not impede the flow of fluid within the canister 59 in a direction toward the fuel tip 56.
- the other ring 63b has an inner diameter less than the inner diameter of the canister 59 so that it operates to impede the flow of fluid within the canister 59 in a direction away from the fuel tip 56.
- An oxygen-containing combustion air stream or other oxidant designated by arrow 61 flows through the swirl vanes 60 into the canister 59 and subsequently into the antechamber 42.
- the swirl vanes 60 impart an intense rotary motion to the combustion air stream to aid mixing of the combustion air with the fuel stream discharged from the fuel tip 56.
- Combustion air is supplied to the canister 59 by a conduit 62 from a combustion air source 64 and the volumetric flow rate is regulated by a flow regulator 65, Other mechanisms may be used to impart the desired mixing of the fuel stream 57 with the combustion air stream 61.
- the combustion air stream 61 may be delivered into the canister 59 through one or more angled discharge nozzles which impart a rotary motion to the combustion air. It is to be understood that a swirling motion need not be imparted to the fuel stream 57 or combustion air stream 61 so long as sufficient turbulence is otherwise created to cause intimate mixing of the fuel stream 57 and combustion air stream 61.
- the combustion air stream 61 and/or the fuel stream 57 may be supplied to the burner 24 at ambient temperatures.
- the combustion air stream 61 and/or the fuel stream 57 may be preheated by a heat exchanger 66 in which heat is supplied by the combustion process occurring within the thermal oxidizer 10 or from other suitable sources.
- the combustion air stream 61 and the fuel stream 57 are preferably supplied to the burner 24 at sufficient pressure to force the fluid stream 11 to flow forwardly through the oxidation chamber 12 without recirculating.
- the source 64 of the combustion air stream 61 may comprise a portion, or all, of a process stream 68 containing waste products, organic compounds, including volatile organic compounds and semi-volatile organic compounds, and/or hazardous air pollutants.
- these compounds and pollutants include hydrocarbons, sulfur compounds, chlorinated solvents, halogenated hydrocarbon liquids, dioxins, and polychlorinated biphenyls.
- the process stream 68 may thus be an off-gas or byproduct of an industrial, manufacturing, or power generating process.
- the source 64 of the combustion air stream may also comprise atmospheric air or some additional source of oxygen
- one or more portions, or all, of the process stream 68 may bypass the combustion air plenum 59 and may be delivered to the antechamber 42 and/or the oxidation chamber 12 at one or more downstream locations, such as through injection ports 70, 71 and/or 72.
- the number and location of injection ports 70, 71, and 72 can be varied to suit particular applications.
- Flow regulators 73a-c are positioned to permit regulation of the flow rate of the various portions of the process stream 68.
- Suitable process controls 74 are used to monitor and regulate the volumetric flow rates of the various fuel, combustion air, and process streams 57, 61, and 68.
- the process controls 74 can regulate the flow rates by controlling one or more of the flow regulators 54, 65, and 73a-c in an automated fashion. Alternatively, one or more of the flow regulators 54, 65, and 73a-c can be adjusted manually.
- the throat structure 58 is positioned at the upstream end 38 of the antechamber 42 and, in one embodiment, comprises an annular wall 76 that converges or tapers inwardly from both ends to a throat 78 of reduced cross-sectional area.
- the throat structure 58 is positioned downstream from the swirl vanes 60 so that the combustion air stream 61 discharged through the swirl vanes 60 must pass through the throat structure 58 before entering the antechamber 42.
- An inner diameter of the throat 78 may be generally the same as the inner diameter of the ring 63b which mounts the swirl vanes 60.
- the fuel tip 56 is positioned so that the fuel stream 57 is discharged from the fuel tip 56 at a first location downstream from a centerline of the throat 78.
- the combustion air stream 61 is discharged from the swirl vanes 60 at a second location which is a preselected distance upstream from the first discharge location of the fuel stream 57 so that the two streams are first mixed together at or downstream from the throat 78.
- positioning of the fuel tip 56 downstream from the throat 78 limits complete mixing of the fuel and combustion air and allows local fuel concentrations to be within the flammability range so that the fuel is combusted in a flame within the antechamber 42.
- the flame may extend from the antechamber 42 into an upstream portion of the oxidation chamber 12.
- the refractory lining 16 of the oxidation chamber 12 is heated to a preselected temperature which is capable of sustaining flameless thermal oxidation of the specific fuel and air mixture flowing through the oxidation chamber 12.
- the present method has been demonstrated to operate successfully within the preselected temperature range of about 1,900 0 F to about 2,400 0 F. With further optimization of the equipment and method, it is believed that the preselected temperature range can be extended to from about 1,700 0 F to about 3,000 0 F.
- the process switches from the startup mode to a flameless thermal oxidation mode in which components of the fluid stream 11 delivered to the oxidation chamber 12 are thermally oxidized.
- Various methods may be used to extinguish the flame in the fluid stream 11 during the transition from the startup mode to the flameless thermal oxidation mode.
- the switch from startup to flameless thermal oxidation mode is achieved by moving the fuel tip 56 upstream from the throat 78. This movement of the fuel tip 56 causes the fuel stream 57 to be discharged from the fuel tip 56 at a second location which causes the fuel exiting the fuel tip 56 to impinge on the burner throat 78.
- the fuel stream 57 and swirling combustion air stream 61 are thus brought into contact with each other at a location upstream from the throat 78 to allow more complete mixing of the fuel stream 57 and combustion air stream 61 before the mixture passes through the throat 78.
- the air-to-fuel ratio throughout the mixture is below the lower fiammability limit and the visible flame is extinguished in the antechamber 42.
- fuel delivered through injection port 70 can be used for the startup mode, hi this embodiment, the fuel tip 56 is fixed in a position upstream of the throat 78 and a fuel valve (not shown) switches the fuel from the injection port 70 to the fuel tip 56 after a preselected temperature is reached.
- the fuel and combustion air mixture nonetheless continues to thermally oxidize without a flame within the oxidation chamber 12 as a result of the heat transferred from the refractory lining 16 in the oxidation chamber 12 and without the need for flue gas recirculation, preheating of the fuel, combustion air, and/or process streams 57, 61, or 68, and/or the use of a bed matrix within the oxidation chamber 12 as required in prior art processes.
- the NOx level in the flue gas drops dramatically, including to a level of less than 5, less than 2, and even less than 1 ppm dry, without an increase in CO levels.
- the localized combustion air-to-fuel ratios can be changed during transition from the startup mode to the flameless thermal oxidation mode by simply varying the relative flow rate of the fuel stream 57 in relation to the combustion air stream 61.
- the local combustion air-to-fuel ratios are within the flammability range.
- the combustion air-to-fuel ratio can be adjusted so that the localized ratios are sufficiently outside of the flammability range to extinguish the visible flame used during the startup mode.
- Exceeding the turbulent flame speed is a general method for extinguishing the visible flame during transition to the flameless thermal oxidation mode.
- the flow rates of the fuel stream 57 and combustion air stream 61 are maintained below the upper limit of the turbulent flame speed.
- the flow rate of one or both of the fuel stream 57 and combustion air stream 61 are increased so that the mixture is flowing at a flow rate above the turbulent flame speed, thereby extinguishing the flame and causing thermal oxidation of the fuel and combustion air mixture in the oxidation chamber 12 as a result of heat transfer from the refractory lining 16.
- the turbulent flame speed can be lowered to a rate below that of the fuel and combustion air mixture.
- the internal flow geometry of the burner 24 can be changed, such as by moving the location of the fuel injection during the transition from startup to flameless thermal oxidation mode in the manners previously described.
- a flame holding structure (not shown) may be provided within the antechamber 42 to anchor the flame during the startup mode. The flame holding structure can then be moved or altered to lower the turbulent flame speed during the transition to flameless oxidation mode so that it no longer anchors the flame.
- the process may also cycle between the startup and flameless oxidation modes at preselected intervals, such as when additional heat is required in the oxidation chamber 12 in situations where the refractory lining 16 cools below the temperature required to sustain flameless thermal oxidation of the components in the fluid stream 11.
- This cooling can result from thermal loses through the exterior shell 14 of the oxidation chamber 12 or from the cooling effect of the fuel, combustion air, and/or process streams 57, 61, and 68.
- the flameless thermal oxidation can be self-sustaining for a period of time, such as one hour or longer, including indefinitely.
- supplemental heat may need to be added to the oxidation chamber 12 to offset thermal losses through the exterior shell 14 and the cooling effect of one or more of the fuel, combustion air, and/or process streams 57, 61, and 68 which are delivered to the burner 24 or oxidation chamber 12 at temperatures below that at which flameless oxidation is occurring.
- the supplemental heat could be added, for example, by continuously or intermittently preheating the fuel, combustion air, and/or process streams, introducing supplemental fuel into the oxidation chamber 12 through one or more injection ports, such as injection port(s) 71 with or without a portion of the process stream 68 and/or injection port(s) 72, by burning the supplemental fuel in a flame mode, by using electrical resistance heating elements, and/or by intermittently operating the burner 24 in the initial heating mode. Adding this supplemental heat by burning fuel with a visible flame may cause an increase in the NOx and CO levels, but the overall levels will remain significantly below those that would result from operating the thermal oxidizer 10 by continual burning all of the fuel in a visible flame.
- the fluid stream 11 comprising the fuel and combustion air streams 57 and 61 and, optionally, the process stream 68, is delivered to oxidation chamber 12 as a premixed mixture with a combustion air-to- fuel ratio selected for the desired operating conditions in the specific application being conducted.
- the combustion air-to-fuel ratio and the respective flow rates of combustion air stream 61 and fuel stream 57 are generally regulated to supply sufficient heat as a result of thermal oxidation of the fuel and other components of the fluid stream 11 to sustain the thermal oxidation process for the desired length of time.
- the localized combustion air-to-fuel ratios or the localized fuel concentrations in fluid stream 11 should be below the lower flammability limit for the specific fuel or mixture of fuels being utilized or the flow rate of one or more of the fluid stream 11, combustion air stream 61, and fuel stream 57 is regulated so that the flow rate of the fluid stream 11 is above the turbulent flame speed for the fuel and other combustible components in the fluid stream 11.
- a combustion air-to-fuel ratio of approximately 20:1 or greater can be used.
- the choke 44 if present, further reduces the opportunity for flashback by increasing the velocity of the fluid stream 11 flowing from the antechamber 42 into the oxidation chamber 12 and shielding the antechamber 42 from radiation emanating from the oxidation chamber 12.
- the presence of diluents may improve fuel efficiency since the flameless process is able to operate with lower oxygen content in the combustion air stream.
- the components of the fluid stream 11 which are thermally oxidized in the flameless process described above can be any compounds capable of undergoing thermal oxidation, such as fuels, waste materials, organic compounds, including volatile organic compounds and semi- volatile organic compounds, and various types of hazardous air pollutants.
- the thermal oxidizer 10 In situations where it is desired for the thermal oxidizer 10 to operate merely as a burner, one or more fuels would be the components in the fluid stream 11 which undergo thermal oxidation.
- the present invention encompasses processes where the thermal oxidizer 10 is not acting to remove pollutants from a process stream, but is instead serving as a low NOx and low CO burner which provides hot flue gases for other uses, such as in downstream equipment 31.
- the burner 24 provides a convenient mechanism for preheating the oxidation chamber 12 and for subsequently premixing the fuel and combustion gas prior to delivery to the oxidation chamber 12. It is to be understood, however, that the oxidation chamber 12 can be preheated by other heat sources in place of or in addition to the burner 24. In addition, the fuel and combustion air can be premixed by other mechanisms prior to entry into, or as they enter, the oxidation chamber 12. Thus, the present invention encompasses processes where the burner 24 need not be used and the heat is supplied in other ways, or where the burner 24 is an induced draft burner, natural draft burner, premixed burner, or partial premixed burner.
- the process of the present invention does not require the use of a bed matrix of the type used in U.S. Patent No. 5,165,884.
- a bed matrix of the type used in U.S. Patent No. 5,165,884.
- all or substantially all of the open internal volume 18 of the oxidation chamber 12 is available for the flow of the fluid stream 11 undergoing fiameless thermal oxidation.
- the previously discussed disadvantages of the bed matrix are avoided in the present process, which nonetheless is capable of achieving very low NOx and CO levels.
- a bed matrix is not necessary in the fiameless thermal oxidation process of the present invention, it may be desirable in certain applications to include a bluff body or other mixing device within the oxidation chamber 12 to facilitate the mixing of the fluid stream 1 1 and/or to anchor the flame, if used, which supplies supplemental heat.
- a bluff body or other mixing device may also be used as a flame holding structure in the antechamber 42.
- altering or moving the flame holding structure may change the turbulent flame speed of the fuel in the fluid stream 1 1 to facilitate the transition between the modes where the fuel is combusted in a visible flame to initially heat or reheat the oxidation chamber refractory lining 16 and the mode where the fuel is thermally oxidized without a flame by heat transfer from the refractory lining 16.
- the flue gas reaction products exiting the oxidation chamber 12 may be delivered to the exhaust stack 30 for venting to the atmosphere.
- the flue gas may also be used as a heat exchange medium to preheat one or more components of the fluid stream 11 prior to delivery to the oxidation chamber 12.
- the hot flue gas may be used in the downstream equipment 31 such as process heaters, boilers, reactor furnaces such as ethylene cracking units, hydrogen reformers and the like.
- Example 1 is provided by way of illustration and are not to be taken as a limitation on the overall scope of the present invention.
- Combustion air in the form of air at room temperature was delivered into the antechamber 42 through swirl vanes 60 at a flow rate of 114,000 scf/hr.
- Fuel in the form of natural gas at room temperature was injected into the antechamber 42 through the fuel tip 56 at a flow rate of 5,550 scf/hr.
- the fuel and combustion air mixture was ignited and burned with a visible flame until the oxidation chamber 12 reached a temperature of 1,880 G F. Once the oxidation chamber 12 was preheated in this manner, the burner flame was extinguished by pulling the fuel tip 56 back from the centerline of the burner throat 78 approximately 3.5 inches to cause more complete mixing of the fuel and combustion air prior to passage of the mixture through the burner throat 78.
- the fuel and combustion air flow rates remained nearly unchanged and the premix stream of fuel and combustion air passed into the antechamber 42 through the burner throat 78 without a visible flame being present and the combustion roar that had accompanied the burning of the fuel in the flame mode disappeared.
- the fuel continued to oxidize in a stable flameless oxidation process as a result of heat transfer from the preheated refractory lining 16 of the oxidation chamber 12.
- the flameless oxidation process was substantially in equilibrium and NOx levels of less than 1 ppm dry and CO levels of less than 1 ppm dry were measured.
- the process ran for 8.5 hours and was shut down when the temperature in the oxidation chamber 12 just downstream from the burner 24 cooled to a temperature of 1 ,500 0 F as a result of thermal losses through the exterior shell 14 of the oxidation chamber 12 and the cooling effect of the fuel and combustion air being delivered to the burner 24 at ambient temperatures.
- the outlet temperature of the oxidation chamber 12 was still at 1,880 0 F when the process was shut down.
- Example 1 The test of Example 1 was repeated with the following changes in parameters: (1) the combustion air flow rate was reduced to 100,200 scf/hr., and (2) the fuel flow rate through the antechamber 42 was reduced by staging the fuel. The total fuel flow was 5,500 scf/hr. and was split with 85.6% of the fuel being premixed with all of the combustion air stream prior to injection into the antechamber 42 and the remaining 14.4% of the fuel being injected through two fuel gas tips 72 positioned in the oxidation chamber 12 just downstream from the burner 24.
- the fuel injected through the fuel gas tips into the oxidation chamber 12 was combusted with a visible flame and provided direct heating of the refractory lining 16 to stabilize the flameless oxidation process in the oxidation chamber 12.
- the outlet temperature of the oxidation chamber 12 was 1,990 °F. Because a portion of the fuel was combusted with a visible flame, the NOx levels increased and varied from 6 to 12 ppm dry. The CO levels remained below 1 ppm dry. The test was intentionally terminated at 44.5 hours of operation as it appeared that the process was self-sustaining.
- Example 3 The test conditions presented for Example 3 demonstrate a case where, after sufficient preheating of the refractory lining 16, the turbulent flame speed was exceeded to allow for flameless operation above the lower flammability limit of the air/fuel mixture in the antechamber 42.
- the combustion air flow rate was 245,640 scf/hr.
- the natural gas flow rate was 18,357 scf/hr.
- the thermal oxidizer operating temperature was 2,381 0 F.
- the combustion air and natural gas were premixed in the antechamber 42 to yield a 5.87 vol% premixed fuel composition, which was above the ambient temperature lower flammability limit (5 vol%).
- a blend of low 0 2 -combustion air was generated by combining 20,820 scf/hr. of CO 2 and 62,280 scf/lir. of fresh air, which resulted in a 14.5 vol% O 2 content.
- the low O 2 combustion air was delivered into the ante chamber 42 through swirl vanes 60.
- Fuel in the form of natural gas at room temperature was injected into the antechamber 42 through the fuel tip 56 at a flow rate of 5,475 scf/hr.
- the fuel and low O 2 -combustion air were mixed in the antechamber 42 and exited into the thermal oxidation chamber 12 where the fuel was oxidized fiamelessly.
- the O 2 concentration in the resulting flue gas was 2 vol% dry, CO concentrations were undetectable, the NOx concentration in the flue gas was 1.2 ppm dry, and the operating temperature was 1 ,941 0 F.
- This test example demonstrates the ability of the thermal oxidizer 10 to operate with low-O 2 combustion air streams, flue gas recycle streams, and/or low heating value waste streams. The test also showed that the flameless process will operate with lower O 2 content in the combustion air compared to a conventional flame-type burner. Thermal efficiency can be gained when low O 2 content combustion air sources are used since less fresh air needs to be added to the low O 2 content stream to maintain stability.
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Incineration Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
- Physical Or Chemical Processes And Apparatus (AREA)
- Tunnel Furnaces (AREA)
Abstract
Description
Claims
Priority Applications (6)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2008801186797A CN101874180B (en) | 2007-11-27 | 2008-11-25 | Flameless thermal oxidation apparatus and methods |
EP08853951A EP2227654A1 (en) | 2007-11-27 | 2008-11-25 | Flameless thermal oxidation apparatus and methods |
MX2010005194A MX2010005194A (en) | 2007-11-27 | 2008-11-25 | Flameless thermal oxidation apparatus and methods. |
JP2010536115A JP2011508864A (en) | 2007-11-27 | 2008-11-25 | Flameless thermal oxidation apparatus and method |
BRPI0820661-9A BRPI0820661A2 (en) | 2007-11-27 | 2008-11-25 | Flammable apparatus and processes of thermal oxidation |
CA2705773A CA2705773A1 (en) | 2007-11-27 | 2008-11-25 | Flameless thermal oxidation apparatus and methods |
Applications Claiming Priority (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US11/945,775 US20090136406A1 (en) | 2007-11-27 | 2007-11-27 | Flameless thermal oxidation method |
US11/945,775 | 2007-11-27 | ||
US12/273,367 US20090133854A1 (en) | 2007-11-27 | 2008-11-18 | Flameless thermal oxidation apparatus and methods |
US12/273,367 | 2008-11-18 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2009070563A1 true WO2009070563A1 (en) | 2009-06-04 |
Family
ID=40668727
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/US2008/084637 WO2009070563A1 (en) | 2007-11-27 | 2008-11-25 | Flameless thermal oxidation apparatus and methods |
Country Status (12)
Country | Link |
---|---|
US (1) | US20090133854A1 (en) |
EP (1) | EP2227654A1 (en) |
JP (1) | JP2011508864A (en) |
KR (1) | KR20100098632A (en) |
CN (1) | CN101874180B (en) |
AR (1) | AR069751A1 (en) |
BR (1) | BRPI0820661A2 (en) |
CA (1) | CA2705773A1 (en) |
CL (1) | CL2008003517A1 (en) |
MX (1) | MX2010005194A (en) |
TW (1) | TW200940155A (en) |
WO (1) | WO2009070563A1 (en) |
Families Citing this family (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20090136406A1 (en) * | 2007-11-27 | 2009-05-28 | John Zink Company, L.L.C | Flameless thermal oxidation method |
JP6110854B2 (en) * | 2011-08-22 | 2017-04-05 | トクァン, マジェドTOQAN, Majed | Tangential annular combustor with premixed fuel air for use in gas turbine engines |
CN102809162B (en) * | 2012-08-08 | 2016-03-30 | 陈汉笙 | The two-way thermal oxidizer of a kind of nonflame |
US9476589B2 (en) * | 2013-03-13 | 2016-10-25 | Fives North American Combustion, Inc. | Diffuse combustion method and apparatus |
US10215408B2 (en) | 2015-12-09 | 2019-02-26 | Fives North American Combustion, Inc. | Method and apparatus for diffuse combustion of premix |
EP3242080B1 (en) * | 2016-05-04 | 2019-07-10 | WS-Wärmeprozesstechnik GmbH | Apparatus and method for heating of furnaces using radiant tubes |
DE102017222517A1 (en) * | 2017-12-12 | 2019-06-13 | Dürr Systems Ag | Method for cleaning exhaust gas and exhaust gas purification device |
ES2933119T3 (en) * | 2018-11-12 | 2023-02-02 | Ws Waermeprozesstechnik Gmbh | Procedure and device for staged combustion without flame |
WO2021091768A1 (en) * | 2019-11-07 | 2021-05-14 | Exxonmobil Chemical Patents Inc. | Olefin polymerization processes |
US11898747B2 (en) * | 2020-04-30 | 2024-02-13 | Honeywell International Inc. | Burner system and process for natural gas production |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4519993A (en) * | 1982-02-16 | 1985-05-28 | Mcgill Incorporated | Process of conversion for disposal of chemically bound nitrogen in industrial waste gas streams |
US5165884A (en) * | 1991-07-05 | 1992-11-24 | Thermatrix, Inc. | Method and apparatus for controlled reaction in a reaction matrix |
Family Cites Families (62)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US2772149A (en) * | 1951-12-13 | 1956-11-27 | Hydrocarbon Research Inc | Generation of synthesis gas and apparatus therefor |
US3207201A (en) * | 1963-02-06 | 1965-09-21 | Zink Co John | Apparatus for combustion of waste gases |
US3195608A (en) * | 1963-04-08 | 1965-07-20 | Coen Co | Volatile waste incinerator |
US3320999A (en) * | 1965-03-15 | 1967-05-23 | Owens Corning Fiberglass Corp | Internal combustion burner |
US3418062A (en) * | 1966-08-08 | 1968-12-24 | Bloom Eng Co Inc | Burner structures |
US3810732A (en) * | 1971-07-01 | 1974-05-14 | Siemens Ag | Method and apparatus for flameless combustion of gaseous or vaporous fuel-air mixtures |
US4033725A (en) * | 1972-02-24 | 1977-07-05 | John Zink Company | Apparatus for NOx control using steam-hydrocarbon injection |
US3898317A (en) * | 1972-07-24 | 1975-08-05 | Midland Ross Corp | Method for incinerating flue gases |
DE2362132C2 (en) * | 1973-12-14 | 1982-03-11 | Klöckner-Humboldt-Deutz AG, 5000 Köln | Device for the thermal treatment of fine-grained material with several additional combustion devices assigned to a heat exchanger system |
US4154567A (en) * | 1977-01-07 | 1979-05-15 | Continental Carbon Company | Method and apparatus for the combustion of waste gases |
DE2801161B2 (en) * | 1978-01-12 | 1981-06-25 | Babcock Krauss-Maffei Industrieanlagen GmbH, 8000 München | Process and burning of sintered goods made from carbonate raw materials such as cement clinker |
US4784599A (en) * | 1982-05-14 | 1988-11-15 | Garbo Paul W | Liquid fuel combustion with porous fiber burner |
US4541561A (en) * | 1983-06-23 | 1985-09-17 | Smith Robert E | Heating equipment and method of operating same |
USRE34298E (en) * | 1984-08-17 | 1993-06-29 | American Combustion, Inc. | Method for waste disposal |
US4865543A (en) * | 1984-08-30 | 1989-09-12 | Garbo Paul W | Liquid fuel combustion with porous fiber burner |
US4658762A (en) * | 1986-02-10 | 1987-04-21 | Gas Research Institute | Advanced heater |
US4785768A (en) * | 1986-09-15 | 1988-11-22 | Iowa State University Research Foundation, Inc. | Means and method for controlling load turndown in a fluidized bed combustor |
IT1227318B (en) * | 1988-07-29 | 1991-04-08 | Pietro Italiano | METHANE CATALYTIC COMBUSTION BOILER FOR OBTAINING HOT WATER FOR DOMESTIC AND INDUSTRIAL USES. |
US4988287A (en) * | 1989-06-20 | 1991-01-29 | Phillips Petroleum Company | Combustion apparatus and method |
US4974530A (en) * | 1989-11-16 | 1990-12-04 | Energy And Environmental Research | Apparatus and methods for incineration of toxic organic compounds |
ES2064538T3 (en) * | 1990-06-29 | 1995-02-01 | Wuenning Joachim | PROCEDURE AND DEVICE FOR COMBUSTION OF FUEL IN A COMBUSTION ENCLOSURE. |
CN2077084U (en) * | 1990-07-14 | 1991-05-15 | 朱华 | Pipe-type nonflame burner |
US5025631A (en) * | 1990-07-16 | 1991-06-25 | Garbo Paul W | Cogeneration system with low NOx combustion of fuel gas |
US5236354A (en) * | 1991-03-18 | 1993-08-17 | Combustion Power Company, Inc. | Power plant with efficient emission control for obtaining high turbine inlet temperature |
US5249952A (en) * | 1992-04-24 | 1993-10-05 | Cosmos Ventures, Inc. | Exhaust fume energy source and waste combustion apparatus |
WO1994014008A1 (en) * | 1992-12-17 | 1994-06-23 | Thermatrix Inc. | Method and apparatus for control of fugitive voc emissions |
US5297954A (en) * | 1993-03-11 | 1994-03-29 | Haden Schweitzer Corporation | Volatile organic compound abatement system |
WO1995002450A1 (en) * | 1993-07-16 | 1995-01-26 | Thermatrix Inc. | Method and afterburner apparatus for control of highly variable flows |
US5366699A (en) * | 1993-09-22 | 1994-11-22 | Bonnie June Goodrich | Apparatus for thermal destruction of waste |
US5542840A (en) * | 1994-01-26 | 1996-08-06 | Zeeco Inc. | Burner for combusting gas and/or liquid fuel with low NOx production |
WO1996012612A1 (en) * | 1994-10-19 | 1996-05-02 | Altex Technologies Corporation | Lime mud regeneration process and apparatus |
DE69527299D1 (en) * | 1994-10-27 | 2002-08-08 | Isentropic Sys Ltd | IMPROVEMENTS IN THE COMBUSTION AND USE OF FUEL GASES |
US5690482A (en) * | 1994-11-04 | 1997-11-25 | Integrated Energy Development Corp. | Process for the combustion of sulphur containing fuels |
US5592811A (en) * | 1995-10-03 | 1997-01-14 | Alliedsignal Inc. | Method and apparatus for the destruction of volatile organic compounds |
US5823124A (en) * | 1995-11-03 | 1998-10-20 | Gas Research Institute | Method and system to reduced NOx and fuel emissions from a furnace |
US6136144A (en) * | 1996-06-06 | 2000-10-24 | Thermatrix, Inc. | Method of removing sulfur from a process gas stream using a packed bed calcinator |
US5819673A (en) * | 1996-10-15 | 1998-10-13 | Thermatrix Inc. | Systems for the treatment of chemical wastes and methods for treating chemical wastes |
US6238206B1 (en) * | 1997-05-13 | 2001-05-29 | Maxon Corporation | Low-emissions industrial burner |
US6003305A (en) * | 1997-09-02 | 1999-12-21 | Thermatrix, Inc. | Method of reducing internal combustion engine emissions, and system for same |
DK1021682T3 (en) * | 1997-10-08 | 2002-06-17 | Shell Int Research | Flame-free combustion process heater |
DE19747905C1 (en) * | 1997-10-30 | 1999-01-28 | Chemisch Thermische Prozestech | Cleaner for pollutant bearing exhaust gases |
US6146007A (en) * | 1998-03-20 | 2000-11-14 | Cedarapids Inc. | Asphalt plant having centralized media burner and low fugitive emissions |
KR19980082082A (en) * | 1998-08-21 | 1998-11-25 | 오석인 | Evaporative Regenerative Incineration System of Organic Wastewater |
US6736635B1 (en) * | 1999-11-02 | 2004-05-18 | Ebara Corporation | Combustor for exhaust gas treatment |
DE10001293B4 (en) * | 2000-01-14 | 2008-06-12 | WS-Wärmeprozeßtechnik GmbH | Tube Erhitzerofen |
US7033544B2 (en) * | 2000-12-13 | 2006-04-25 | Megtec Systems, Inc. | Determination of supplemental fuel requirement and instantaneous control thereof involving regenerative thermal oxidation |
DE10119083C1 (en) * | 2001-04-19 | 2002-11-28 | Joachim Alfred Wuenning | Compact steam reformer |
FR2825448B1 (en) * | 2001-05-30 | 2003-09-12 | Inst Francais Du Petrole | THERMAL GENERATOR FOR LIMITING EMISSIONS OF NITROGEN OXIDES BY RECOMBUSTION OF FUMES AND METHOD FOR IMPLEMENTING SUCH A GENERATOR |
US20030013053A1 (en) * | 2001-07-11 | 2003-01-16 | Cornel Dutescu | Waste and toxic gas combustion reactor |
US20030059731A1 (en) * | 2001-09-25 | 2003-03-27 | Coffey Clayton G. | Device for incinerating waste gas |
JP3864092B2 (en) * | 2002-01-10 | 2006-12-27 | 東京瓦斯株式会社 | Flame retardant decomposition burner |
DE10217524B4 (en) * | 2002-04-19 | 2005-10-13 | WS - Wärmeprozesstechnik GmbH | Burner with side outlet for flameless oxidation |
DE10217913B4 (en) * | 2002-04-23 | 2004-10-07 | WS Wärmeprozesstechnik GmbH | Gas turbine with combustion chamber for flameless oxidation |
US20040018460A1 (en) * | 2002-07-29 | 2004-01-29 | Korwin Michel J. | Apparatus and method for thermal neutralization of gaseous mixtures |
US6796789B1 (en) * | 2003-01-14 | 2004-09-28 | Petro-Chem Development Co. Inc. | Method to facilitate flameless combustion absent catalyst or high temperature oxident |
AU2003299324A1 (en) * | 2003-03-21 | 2004-10-11 | Kleen-Up S.R.L. | Method and apparatus for reducing combustion residues in exhaust gases |
US7270539B1 (en) * | 2003-10-28 | 2007-09-18 | Soil-Therm Equipment, Inc. | Method and apparatus for destruction of vapors and waste streams using flash oxidation |
US7273366B1 (en) * | 2003-10-28 | 2007-09-25 | Soil-Therm Equipment, Inc. | Method and apparatus for destruction of vapors and waste streams |
JP2007518551A (en) * | 2003-12-29 | 2007-07-12 | ナンヤン テクノロジカル ユニヴァーシティ | System and method of using a cold hydrogen flame for the decomposition of volatile organic compounds (VOCS) and odorous substances |
DE102005026764B3 (en) * | 2005-06-10 | 2007-04-05 | Ws Reformer Gmbh | Fixed bed gasifier and process for the gasification of solid fuel |
US8062027B2 (en) * | 2005-08-11 | 2011-11-22 | Elster Gmbh | Industrial burner and method for operating an industrial burner |
US20090136406A1 (en) * | 2007-11-27 | 2009-05-28 | John Zink Company, L.L.C | Flameless thermal oxidation method |
-
2008
- 2008-11-18 US US12/273,367 patent/US20090133854A1/en not_active Abandoned
- 2008-11-25 MX MX2010005194A patent/MX2010005194A/en not_active Application Discontinuation
- 2008-11-25 CN CN2008801186797A patent/CN101874180B/en not_active Expired - Fee Related
- 2008-11-25 KR KR1020107013157A patent/KR20100098632A/en active IP Right Grant
- 2008-11-25 CA CA2705773A patent/CA2705773A1/en not_active Abandoned
- 2008-11-25 JP JP2010536115A patent/JP2011508864A/en not_active Withdrawn
- 2008-11-25 WO PCT/US2008/084637 patent/WO2009070563A1/en active Application Filing
- 2008-11-25 BR BRPI0820661-9A patent/BRPI0820661A2/en not_active IP Right Cessation
- 2008-11-25 EP EP08853951A patent/EP2227654A1/en not_active Withdrawn
- 2008-11-26 TW TW097145644A patent/TW200940155A/en unknown
- 2008-11-26 CL CL2008003517A patent/CL2008003517A1/en unknown
- 2008-11-26 AR ARP080105140A patent/AR069751A1/en not_active Application Discontinuation
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4519993A (en) * | 1982-02-16 | 1985-05-28 | Mcgill Incorporated | Process of conversion for disposal of chemically bound nitrogen in industrial waste gas streams |
US5165884A (en) * | 1991-07-05 | 1992-11-24 | Thermatrix, Inc. | Method and apparatus for controlled reaction in a reaction matrix |
Also Published As
Publication number | Publication date |
---|---|
KR20100098632A (en) | 2010-09-08 |
TW200940155A (en) | 2009-10-01 |
CA2705773A1 (en) | 2009-06-04 |
EP2227654A1 (en) | 2010-09-15 |
JP2011508864A (en) | 2011-03-17 |
US20090133854A1 (en) | 2009-05-28 |
CN101874180B (en) | 2012-10-03 |
AR069751A1 (en) | 2010-02-17 |
CN101874180A (en) | 2010-10-27 |
MX2010005194A (en) | 2010-05-24 |
BRPI0820661A2 (en) | 2015-06-16 |
CL2008003517A1 (en) | 2010-01-15 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US20090136406A1 (en) | Flameless thermal oxidation method | |
US20090133854A1 (en) | Flameless thermal oxidation apparatus and methods | |
JP4309380B2 (en) | Multistage combustion system with ignition assisted fuel lance | |
TWI275414B (en) | Low NOx combustion | |
EP0416533B1 (en) | Combustion process having improved temperature distribution | |
KR950007381B1 (en) | Low nox high efficiency combustion process | |
JP2927557B2 (en) | Ultra low NOx burner | |
US7717701B2 (en) | Pulverized solid fuel burner | |
US8485813B2 (en) | Three stage low NOx burner system with controlled stage air separation | |
KR101477519B1 (en) | System apparatus and method for flameless combustion absent catalyst or high temperature oxidants | |
US6234092B1 (en) | Thermal treatment of incombustible liquids | |
EP0432153A4 (en) | Method and apparatus for generating highly luminous flame | |
KR960010601B1 (en) | Opposed fired rotary kiln | |
US5213492A (en) | Combustion method for simultaneous control of nitrogen oxides and products of incomplete combustion | |
CN107270285B (en) | Method for burning fuel and combustion device | |
JP2013181732A (en) | Waste incinerator and waste incineration method | |
JPH0579614A (en) | Burner contstruction for low calorific gas and burning method therefor | |
US5242295A (en) | Combustion method for simultaneous control of nitrogen oxides and products of incomplete combustion | |
KR20190118681A (en) | Gradual oxidation with heat transfer | |
EP0499184B1 (en) | Combustion method for simultaneous control of nitrogen oxides and products of incomplete combustion | |
JP3680659B2 (en) | Combustion apparatus and combustion method | |
JP2005003360A (en) | Tubular flame burner | |
JPH08226611A (en) | Burning method of fuel |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
WWE | Wipo information: entry into national phase |
Ref document number: 200880118679.7 Country of ref document: CN |
|
121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 08853951 Country of ref document: EP Kind code of ref document: A1 |
|
WWE | Wipo information: entry into national phase |
Ref document number: MX/A/2010/005194 Country of ref document: MX |
|
WWE | Wipo information: entry into national phase |
Ref document number: 2705773 Country of ref document: CA |
|
WWE | Wipo information: entry into national phase |
Ref document number: 2010536115 Country of ref document: JP |
|
NENP | Non-entry into the national phase |
Ref country code: DE |
|
ENP | Entry into the national phase |
Ref document number: 20107013157 Country of ref document: KR Kind code of ref document: A |
|
WWE | Wipo information: entry into national phase |
Ref document number: 3787/CHENP/2010 Country of ref document: IN Ref document number: 2008853951 Country of ref document: EP |
|
ENP | Entry into the national phase |
Ref document number: PI0820661 Country of ref document: BR Kind code of ref document: A2 Effective date: 20100527 |