According to an embodiment, a combustion system may include a burner, a nozzle or an injector that may dispense a steam of fuel or a mixture of fuel and air into a combustion volume, which is ignited to provide a flame. During combustion, the flame may include a flow of exhaust (also referred to as flue gases herein) that includes a plurality of particles including burned combustion products, unburned fuel and air. The combustion system may employ one or more methods for charging and redirecting the particles included in the exhaust or flue gases emanating from the combustion system. The particles may be recirculated into the flame, such as to improve combustion efficiency and reduce the concentration of these recirculated particles in the exhaust gases for disposal. According to various embodiments, a method for charging the exhaust gases from a combustion process may be implemented using a corona discharge device that includes two or more discharge electrodes that may create an ionic wind to charge emission particles. Other charging methods may include utilizing fluxes of x-rays, laser beams, radiation material enrichment-like processes, and various electrical discharge processes. In some embodiments, a charge electrode is disposed in contact with a conductive portion of a combustion reaction and is driven to carry a high voltage, to cause the conductive portion of the combustion reaction to carry a similar voltage.
The application of an electric field by corona discharge electrodes may be controlled by one or more control systems.
In other embodiments, particles entrained in the exhaust gases may pass through an ionic wind produced by the corona discharge where positively charged particles may be generated such that these charges may attach to all or most of the entrained particles to create charged particles. The charged particles may then be collected by an oppositely charged collector plate that may be placed above and away from the combustion volume. Larger particles may receive a lower charge to mass ratio and may be more poorly attracted to the collector plate, while smaller particles may receive a higher charge-to-mass ratio and may be more easily attracted by the collector plate. Particle size in exhaust gas has been found to be fuel dependent, but for some fuels, the desired particle size to be collected range from about 0.1 μm to about 10 μm.
In another embodiment, particles in the exhaust gases passing through an ionic wind to generate charged particles selected to be attracted by a director conduit. The director conduit may redirect or recirculate these particles back into the flame within the combustion volume where any remaining fuel contained by the redirected particles is oxidized and where the concentration of these particles is further reduced. Re-burned particles in the exhaust gases may then be charged during another cycle of corona discharge application and may be collected by a collector plate for later disposal according to an embodiment.
The structures and methods disclosed in the present disclosure may improve the efficiency of combustion processes since more energy may be produced by the same amount or quantity of reactants. Additionally, particle emissions may be decreased when being re-burned and particulate pollution thereby reduced. Furthermore, charging of exhaust particles and their collection and disposal employing the collector plate may decrease the complexity of disposal methods while reducing emission levels.
Numerous other aspects, features and benefits of the present disclosure will become apparent from the following detailed description taken together with the associated figures.
Various embodiments of the present disclosure are described by way of example with reference to the accompanying figures, which are schematic and are not intended to be drawn to scale. Unless indicated as representing the prior art, the figures represent aspects of the present disclosure.
In the following detailed description, reference is made to the accompanying drawings, which form a part hereof. In the drawings, which are not to scale or to proportion, similar symbols typically identify similar components, unless context dictates otherwise. The illustrated embodiments described in the detailed description, drawings and claims, are not meant to be limiting. Other embodiments may be used and/or other changes may be made without departing from the spirit or scope of the present disclosure.
As used herein, the following terms may have the following definitions:
“corona discharge” may refer to an electrical discharge, either positive or negative, produced by the ionization of a fluid surrounding an electrically energized conductor.
“ionic wind” may refer to a stream of ions generated from a tip electrode by a strong electric field exceeding a corona discharge voltage gradient and that may be used to charge exhaust combustion particles.
In order to accomplish a simultaneous charging and collection of exhaust particles 104, electrodes 106 may be placed at either side of a combustion volume 108 above flame 101, and charged with a sufficiently high voltage to generate a corona discharge. Voltage may be applied to electrodes 106 by a high voltage power source (HVPS) 110.
In order to generate a corona discharge one or both electrodes 106 is configured to taper to a sharp tip, which can produce a projection of ions near the end of this tip when excited by voltages above a minimum ionization limit. Corona discharge is a process by which a current flows from one electrode 106 with a high voltage potential into a zone of neutral atmospheric gas molecules such as is present in the combustion exhaust gases 103 adjacent to the tips of electrodes 106. These neutral molecules can be ionized to create a region of plasma around electrode 106. Ions generated in this manner may eventually pass charge to nearby areas of lower voltage potential, such as at collector plate 102, or they can recombine to again form neutral gas molecules.
When the voltage potential gradient, or electric field, is large enough at a point in the area where a corona discharge is established, neutral air molecules may be ionized and the area may become conductive. The air around a sharp shaped electrode 106 may include a much higher voltage potential gradient than elsewhere in the area of neutral air molecules. As such, air near electrodes 106 may become ionized, while air in more distant areas may not. When the air near the tips of sharp shaped electrodes 106 becomes conductive, it may have the effect of increasing the apparent size of the conductor. Since the new conductive region may be less sharp, the ionization may not extend past this local area. Outside this area of ionization and conductivity, positively charged air molecules may move in the direction of an oppositely charged object such as collector plate 102, where they may be neutralized and/or collected.
The movement of these ions generated by a corona discharge, therefore, may form an ionic wind 114. When exhaust particles 104 pass through ionic wind 114, ions may be attached to so or all of exhaust particles 104 such that particles 104 become positively charged to provide charged particles 112.
When the geometry and voltage potential gradient applied to a first conductor increase such that the ionized area continues to grow until it can reach another conductor at a lower potential, a low resistance conductive path between the two conductors may be formed, resulting in an electric arc.
Corona discharge, therefore, may be generally formed at the highly curved regions on electrodes 106, such as, for example, at sharp corners, projecting points, edges of metal surfaces, or small diameter wires. This high curvature may cause a high voltage potential gradient at these locations on electrodes 106 so that the surrounding air breaks down to form a plasma. The electrodes 106 are preferably driven to a voltage sufficiently high to eject ions, but sufficiently low to avoid causing dielectric breakdown and associated plasma formation. The corona discharge may be either positively or negatively charged depending on the polarity of the voltage applied to electrodes 106. If electrodes 106 are positive with respect to collector plate 102, the corona discharge will be positive and vice versa. Typically charges of either sign are deposited on molecules and/or directly onto larger particulates. Charges deposited onto molecules tend to transfer to larger particles (e.g. onto particles including carbon chains with a relatively large number of carbon atoms). Particles including carbon chains essentially constitute unburned fuel. It is desirable to recycle carbon into the combustion reaction to achieve more complete combustion.
Moreover, charges tend to collect on metals and metal-containing particulates including mercury, arsenic, and/or selenium. According to embodiments, structures and functions disclosed herein are arranged to remove metal cations from flue gas.
In some embodiments, ions in ionic wind 114 can have a constant positive polarity. Positively charged particles 112 may be attracted by collector plate 102 which may be negatively charged. Particles 104 which are larger may obtain more charge due to a larger area exposed to receive more positive ions, for example. Charged particles 112 sized between about 0.1 μm and about 10 μm may be more easily attracted and collected by collector plate 102, while charged particles 112 with size smaller than about 0.1 μm can exit combustion system 100 without being attracted by collector plate 102. Re-entrainment of charged particles 112 larger than 10 μm into combustion volume 108 or disposal within a suitable storage component of combustion system 100 (not shown) may reduce exhaust emissions, including but not limited to soot and unburned fuel that may be contained within particles 104.
In other embodiments, ions in ionic wind 114 can have a negative polarity.
In still other embodiments, charging the combustion reaction can be omitted. A collector plate 102 or director conduit 202 (see
Other charging methods can, for example, include utilizing fluxes of x-rays or laser beams, radiation material enrichment-like processes, and various electrical discharge processes. The application of an electric field by a corona discharge generated by an application of high voltage at electrodes 106 may be controlled by a combustion control system.
According to another embodiment, the collector plate 102 may include an electrical conductor coupled to receive a second polarity electrical potential from a node (not shown) operatively coupled to the HVPS 110. The collector plate 102 may be disposed above and away from the combustion volume 108 distal to the flame 101, arranged to cause at least one particle classification to flow to a collection location and to cause at least one different particle classification to flow to one or more locations different from the collection location. The main particle flow may typically be aerodynamic. The differentiation between the collected particles and uncollected particles may be based at least partly on the response of a characteristic charge-to-mass ratio (Q/m) of the collected particles.
In yet another embodiment, a director conduit may be configured to receive the flow of the selected particle classification at a first collection location and to convey the flow of at the least one particle classification to an output location. The output location may be selected to cause the output flow of the selected particle classification to flow back toward the flame 101. For example, unburned fuel particles may be relatively heavy, and have a tendency to carry positive charges on their surface. According to yet another embodiment, the described system can recycle the unburned fuel to the flame 101. For example, this can allow higher flow rates than could normally be sustained with high combustion efficiency.
In still another embodiment,
Finally, particles 104 in exhaust gases that are recirculated trough flame 101 and re-burned may be charged again during another cycle of corona discharge application and may be collected by collector plate 102 for later disposal according to established methods for exhaust gas emissions.
In step 504 an electrically conductive collector plate is provided. The collector plate may be disposed above and away from the combustion volume distal to the flame.
In step 506, a second electrical potential is applied to the electrically conductive collector plate. The second electrical potential may have a polarity opposite that of the first polarity, wherein some fraction of the plurality of the charged particles may be collected at a surface of the collector plate.
In step 508, a “flow” or director conduit is provided. The director conduit may include an inlet port disposed above the combustion volume, an outlet port disposed adjacent to the flame, a tubular body between the inlet and outlet ports, and a fan, impeller or vacuum means for drawing some portion of the exhaust flows through the tubular body thereby redirecting some portion of the burned and unburned particles not captured by the collector plate back into the combustion volume.
Finally, while various aspects and embodiments have been disclosed herein, other aspects and embodiments are contemplated. The various aspects and embodiments disclosed herein are for purposes of illustration and are not intended to be limiting, with the true scope and spirit being indicated by the following claims.
The present application claims priority benefit from U.S. Provisional Patent Application No. 61/775,482, entitled “ELECTRICALLY-DRIVEN CLASSIFICATION OF COMBUSTION PARTICLES”, filed Mar. 8, 2013; which, to the extent not inconsistent with the disclosure herein, is incorporated by reference.
Number | Date | Country | |
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61775482 | Mar 2013 | US |