A gliding electric arc is a conventional apparatus for implementing oxidation and reformation reactions to incinerate waste products through full oxidation and to generate synthetic gas (syngas) through partial oxidation, respectively. A gliding electric arc generates an electrical discharge between two or more electrodes.
Oxidation and some reformation reactions are very energetic, resulting in high temperature product streams. While most of the components of an oxidation or reformation reactor structure can be actively cooled, the electrodes cannot easily be cooled due to the position of the electrodes within the reactor and the high voltage imposed on the electrodes. Additionally, the electrodes are immersed in the reactant stream, resulting in high heat flux conditions that increase the difficulty of cooling the electrodes.
Electrodes are conventionally fabricated from metal sheet using well-established machining techniques. Metals electrodes are used for their electric current carrying properties and their relatively simple manufacturing process. However, metal electrodes have maximum operating temperature limits, particularly in an oxidation implementation. These operating temperature limits are substantially below the temperatures reached in the oxidation product stream. As a result, the metal electrodes can oxidize and melt because of the temperature of the oxidation product stream.
A ceramic electrode for a gliding electric arc system is disclosed. The ceramic electrode includes a ceramic fin defining a spine, a heel, and a tip. A discharge edge of the ceramic fin defines a diverging profile approximately from the heel of the ceramic fin to the tip of the ceramic fin. A mounting surface coupled to the ceramic fin facilitates mounting the ceramic fin within the gliding electric arc system. One or more ceramic electrodes may be used in the gliding electric arc system or other systems which at least partially oxidize a combustible material.
Embodiments of a method are also described. In one embodiment, the method is a method for fabricating a ceramic electrode. An embodiment of the method includes fabricating a ceramic fin which includes a spine, a heel, a tip, and a discharge edge. The discharge edge defines a diverging profile approximately from the heel of the ceramic fin to the tip of the ceramic fin. The method also includes implementing a densification operation to densify the ceramic fin. Other embodiments of the method are also described.
Embodiments of a system are also described. In one embodiment, the system is a gliding electric arc system. An embodiment of the system includes a plasma zone to generate a plasma. The system also includes at least one channel to direct a combustible material and an oxidizer into the plasma zone. The system also includes a plurality of electrically conductive ceramic electrodes within the plasma zone. The plurality of electrically conductive ceramic electrodes generates the plasma to at least partially oxidize the combustible material. Other embodiments of the system are also described.
Other aspects and advantages of embodiments of the present invention will become apparent from the following detailed description, taken in conjunction with the accompanying drawings, which are illustrated by way of example of the various principles and embodiments of the invention.
Throughout the description, similar reference numbers may be used to identify similar elements.
In the following description, specific details of various embodiments are provided. However, some embodiments may be practiced with less than all of these specific details. In other instances, certain methods, procedures, components, structures, and/or functions are described in no more detail than to enable the various embodiments of the invention, for the sake of brevity and clarity.
The illustrated oxidation system includes a medical waste source 102, a gliding electric arc incineration system 104, an oxidizer source 106, and an oxidizer controller 108. Although certain functionality is described herein with respect to each of the illustrated components of the incineration system 100, other embodiments of the incineration system 100 may implement similar functionality using fewer or more components. Additionally, some embodiments of the incineration system 100 may implement more or less functionality than is described herein.
In one embodiment, the medical waste source 102 supplies a biological or medical waste material to the gliding arc electric incineration system 104. The biological or medical waste material may be, for example, in liquid or solid form. However, the content and composition of the waste material that may be incinerated using the incineration system 100 is not limited. In one embodiment, the waste material is human tissues and organs removed during a medical treatment process. In another embodiment, the waste material is a living or dead biological material resulting from medical research activities. Additionally, in some embodiments, the biological or medical waste material may be introduced to the gliding electric arc incineration system 104 using a carrier material. For example, the biological or medical waste material may be entrained with a liquid or a gas, and the combination of the waste material and the carrier material is introduced into the gliding electric arc incineration system 104.
In one embodiment, the gliding electric arc incineration system 104 is a high energy plasma arc system. Additionally, some embodiments of the gliding electric arc incineration system 104 are referred to as non-thermal plasma generators or systems because the process employed by the gliding electric arc incineration system 104 does not provide a substantial heat input (e.g., compared to conventional incineration systems) for the incineration reaction. It should also be noted that, although the illustrated incineration system 100 includes a gliding electric arc incineration system 104, other embodiments of the incineration system 100 may include other types of non-thermal plasma generators.
In order to facilitate the incineration process implemented by the gliding electric arc incineration system 104, the oxidizer source 106 supplies an oxidizer, or oxidant, to the gliding electric arc incineration system 104. In one embodiment, the oxidizer controller 108 controls the amount of oxidizer such as oxygen that is supplied to gliding electric arc incineration system 104. For example, the oxidizer controller 108 may control the flow rate of the oxidizer from the oxidizer source 106 to the gliding electric arc incineration system 104. The oxidizer may be air, oxygen, steam (H2O), or another type of oxidizer. In some embodiments, oxygen may be used instead of air in order to lower the overall volume of oxidized gas. Embodiments of the oxidizer controller 108 include a manually controlled valve, an electronically controlled valve, a pressure regulator, an orifice of specified dimensions, or another type of flow controller. Another embodiment of the oxidizer controller 108 incorporates an oxidant composition sensor feedback system.
In one embodiment, the oxidizer mixes with the waste material within the gliding electric arc incineration system 104. Alternatively, the waste material and the oxidizer may be premixed before the mixture is injected into the gliding electric arc incineration system 104. Additionally, the oxidizer, the waste material, or a mixture of the oxidizer and the waste material may be preheated prior to injection into the gliding electric arc incineration system 104.
In general, the gliding electric arc incineration system 104 oxidizes the waste material and outputs an incineration product that is free or substantially free of harmful materials. More specific details of the incineration process are described below with reference to the following figures. It should be noted that the incineration process depends, at least in part, on the amount of oxidizer that is combined with the waste material and the temperature of the reaction. In some instances, it may be beneficial to input heat into the gliding electric arc incineration system 104 to increase the effectiveness of the incineration process.
In one embodiment, full oxidation (referred to simply as oxidation) of the waste material produces an incineration product. Full oxidation occurs when the amount of oxygen used in the incineration reaction is more than a stoichiometric amount of oxygen. In some embodiments, 5-100% excess of stoichiometric oxygen levels are used to implement full oxidation within the incineration process. An exemplary oxidation equation is:
Other equations may be used to describe other types of reformation and oxidation processes.
The incineration process implemented using the gliding electric arc incineration system 104 may be endothermic or exothermic. In some instances, given the composition of biological and medical waste material, heat may be input into the gliding electric arc system 104 to facilitate incineration. For example, it may be useful to maintain part or all of the gliding electric arc incineration system 104 at an operating temperature within an operating temperature range for efficient operation of the gliding electric arc incineration system 104. In one embodiment, the gliding electric arc incineration system 104 is mounted within a furnace (refer to
Alternatively, or in addition to generally heating the gliding electrical arc incineration system 104, some embodiments of the incineration system 100 may preheat the medical waste material from the medical waste source 102, the oxidizer from the oxidizer source 106, or both. The waste material and/or the oxidizer may be preheated individually at the respective sources or at some point prior to entering the gliding electric arc incineration system 104. For example, the waste material may be preheated within the medical waste channel which couples the medical waste source 102 to the gliding electric arc incineration system 104. Alternatively, the waste material and/or the oxidizer may be preheated individually within the gliding electric arc incineration system 104. In another embodiment, the waste material and the oxidizer may be mixed and preheated together as a mixture before or after entering the gliding electric arc incineration system 104.
The illustrated incineration system 110 shown in
In one embodiment, the waste material and the oxidizer are introduced into the preheat zone 113. Within the preheat zone 113, the waste material and the oxidizer are preheated (represented by the heat transfer Q1) individually or together. In an alternative embodiment, one or both of the waste material and the oxidizer may bypass the preheat zone 113. The waste material and the oxidizer then pass to the plasma zone 114 from the preheat zone 113 (or pass directly to the plasma zone from the respective sources, bypassing the preheat zone 113). Within the plasma zone, the waste material is at least partially incinerated by a non-thermal plasma generator (refer to
After ionization, the reactants pass to the post-plasma reaction zone 116, which facilitates homogenization of the oxidized composition. Within the post-plasma reaction zone 116, some of the reactants and the products of the reactants are oxygen rich while others are oxygen lean. A homogenization material such as a solid state oxygen storage compound within the post-plasma reaction zone 116 acts as a chemical buffering compound to physically mix, or homogenize, the oxidation reactants and products. Hence, the oxygen storage compound absorbs oxygen from oxygen-rich packets and releases oxygen to oxygen-lean packets. This provides both spatial and temporal mixing of the reactants to help the reaction continue to completion. In some embodiments, the post-plasma reaction zone 116 also facilitates equilibration of gas species and transfer of heat.
The heat transfer zone 118 also facilitates heat transfer (represented by the heat transfer Q2) from the incineration product to the surrounding environment. In some embodiments, the heat transfer zone 118 is implemented with passive heat transfer components which transfer heat, for example, from the oxidation product to the homogenization material and to the physical components (e.g., housing) of the gliding electrical arc incineration system 104. Other embodiments use active heat transfer components to implement the heat transfer zone 118. For example, forced air over the exterior surface of a housing of the gliding electric arc oxidation system 104 may facilitate heat transfer from the housing to the nearby air currents. As another example, an active stream of a cooling medium may be used to quench an oxidation product. In another embodiment, the gliding electric arc incineration system 104 may be configured to facilitate heat transfer from the heat transfer zone 118 to the preheat zone 113 to preheat the waste material and/or the oxidizer.
In one embodiment, one or more of the ceramic electrodes 122 are made of silicon carbide (SiC). In another embodiment, one or more of the ceramic electrodes 122 are made of lanthanum chromite (LaCrO3). It will be appreciated by those of skill in the art that other suitable electrically conductive ceramics may be used for the electrodes 122.
The electrical signals on the ceramic electrodes 122 produce a high electrical field gradient between each pair of ceramic electrodes 122. For example, if there is a separation of 2 millimeters between a pair of ceramic electrodes 122, the electrical potential between the ceramic electrodes 122 is about 6-9 kV.
The mixture of the waste material and the oxidizer enters and flows axially through the plasma generator 120 (in the direction indicated by the arrow). The high voltage between the ceramic electrodes 122 ionizes the mixture of reactants, which allows current to flow between the ceramic electrodes 122 in the form of an arc 124, as shown in
Due to the flow of the mixture into the plasma generator 120, the ionized particles are forced downstream, as shown in
Eventually, the gap between the ceramic electrodes 122 becomes wide enough that the current ceases to flow between the ceramic electrodes 122. However, the ionized particles continue to move downstream under the influence of the mixture. Once the current stops flowing between the ceramic electrodes 122, the electrical potential increases on the ceramic electrodes 122 until the current arcs again, as shown in
In order to introduce the waste material and the oxidizer into the plasma generator 120, the gliding electric arc incineration system 130 includes multiple channels, or conduits. In the illustrated embodiment, the gliding electric arc incineration system 130 includes a first channel 138 for the waste material and a second channel 140 for the oxidizer. The first channel is also referred to as the medical waste channel, and the second channel is also referred to as the oxidizer channel. The medical waste and oxidizer channels 138 and 140 join at a mixing manifold 142, which facilitates premixing of the waste material and the oxidizer. In other embodiments, the waste material and the oxidizer may be introduced separately into the plasma generator 120. Additionally, the locations of the medical waste and oxidizer channels 138 and 140 may be arranged in a different configuration.
In order to contain the reactants during the incineration process, and to contain the incineration product resulting from the incineration process, the plasma generator 120 and the housing 134 may be placed within an outer shell 144. In one embodiment, the outer shell 144 facilitates heat transfer to and/or from the gliding electric arc incineration system 130. Additionally, the outer shell 144 is fabricated from steel or another material having sufficient strength and stability at the operating temperatures of the gliding electric arc incineration system 130.
In order to remove the incineration product (e.g., including any carbon dioxide, steam, etc.) from the annular region 146 of the outer shell 144, the gliding electric arc incineration system 130 includes an exhaust channel 148. In one embodiment, the exhaust channel is coupled to a collector ring manifold 150 that circumscribes the housing 134 and has one or more openings to allow the incineration product to flow to the exhaust channel 148. In the illustrated embodiment, the incineration product is exhausted out the exhaust channel 148 at approximately the same end as the intake channels 138 and 140 for the waste material and the oxidizer. This configuration may facilitate easy maintenance of the gliding electric arc incineration system 130 since all of the inlet, outlet, and electrical connections are in about the same place. Other embodiments of the gliding electric arc incineration system 130 may have alternative configurations to exhaust the incineration products from the outer shell 144.
The illustrated gliding electric arc incineration system 130 also includes a heater (not shown) coupled to the medical waste channel 138. In one embodiment, the heater preheats the medical waste material within the medical waste channel 138 before the medical waste material enters the plasma zone of the gliding electric arc incineration system 130.
The illustrated gliding electric arc incineration system 160 of
In another embodiment, the gliding electric arc incineration system 160 facilitates heat transfer to the plasma zone, for example, to facilitate an endothermic incineration process. The illustrated gliding electric arc incineration system 160 includes a heat source (not shown) coupled to the outer shell 144. The heat source supplies a heating agent in thermal proximity to the outer wall of the housing 134 (e.g., within the annular region 146 of the outer shell 144) to transfer heat from the heating agent to the plasma zone of the gliding electric arc incineration system 160. The heating agent may be a gas or a liquid. For example, the heating agent may be air. Although not shown in detail, the heating agent may be circulated within or exhausted from the outer shell 144.
In one embodiment, the gliding electric arc incineration system 160 is initially heated by introducing a mixture of a gaseous hydrocarbon and air. Exemplary gaseous hydrocarbons include natural gas, liquefied petroleum gas (LPG), propane, methane, and butane. Once the temperature of the gliding electric arc oxidation system 160 reaches an operating temperature of about 800° C., the flow of the gaseous hydrocarbon is turned off and waste material is introduced. The flow rates of oxidizer and waste material are adjusted to maintain a proper stoichiometric ratio, while the total flow is adjusted to maintain the plasma generator 120 at a particular operating temperature or within an operating temperature range.
The illustrated gliding electric arc oxidation system 160 also includes a homogenization material 166 located in the channel 136 of the housing 134. The homogenization material 166 serves one or more of a variety of functions. In some embodiments, the homogenization material 166 facilitates homogenization of the incineration product by transferring oxygen from the oxidizer to the waste material. In some embodiments, the homogenization material 166 also provides both spatial and temporal mixing of the reactants to help the reaction continue to completion. In some embodiments, the homogenization material 166 also facilitates equilibration of gas species. In some embodiments, the homogenization material 166 also facilitates heat transfer, for example, from the incineration product to the homogenization material 166 and from the homogenization material 166 to the housing 134. In some embodiments, the homogenization material 166 may provide additional functionality.
The illustrated gliding electric arc incineration system 160 also includes a ceramic insulator 168 to electrically insulate the ceramic electrodes 122 from the housing 134. Alternatively, the gliding electric arc incineration system 160 may include an air gap between the ceramic electrodes 122 and the housing 134. While the dimensions of the air gap may vary in different implementations depending on the operating electrical properties and the fabrication materials used, the air gap should be sufficient to provide electrical isolation between the ceramic electrodes 122 and the housing 134 so that electrical current does not arc from the ceramic electrodes 122 to the housing 134.
In some embodiments, the bottom mounting plate 184 may be removed from the flanges 172 and 174 to remove the mixing manifold 142 and the ceramic electrodes 122 from the housing 134 and the outer shell 144. Additionally, in some embodiments, one or more notches 190 are formed in the bottom mounting plate 184 to facilitate proper alignment of the mixing manifold 142 with the channels 138 and 140.
Additionally, it should be noted that the discharge edge 204 may be a tapered discharge edge which tapers from the thickness of the ceramic fin 200 to a thinner edge at the discharge edge. In other words, the discharge edge 204 may taper to a sharp edge, or point, similar to a cutting knife.
The illustrated ceramic electrode 122 also includes a mounting surface 210 which is coupled to the ceramic fin 200. In one embodiment, the mounting surface 210 facilitates mounting the ceramic fin 200 within a gliding electric arc system, as described above. As one example, the mounting surface 210 may include one or more mounting holes 212 through which mounting screws (not shown) may be attached. Alternatively, the mounting surface 210 may facilitate another type of mounting such as friction fit, snap fit, adhesion, or another type of mounting. Also, in one embodiment, the mounting surface 210 may be defined by a mounting tab that extends substantially perpendicular (or at another angle) from the ceramic fin 200. The ceramic tab may be formed integrally with the ceramic fin 200 or, alternatively, may be formed separately and attached to the ceramic fin 200.
The ceramic fin 200 is made of an electrically conductive ceramic material in order to facilitate generation of an electrical arc during the plasma reformation process described above. In one embodiment, the ceramic fin 200 is made out of a metal oxide material. As one example, the ceramic fin 200 may be made out of a perovskite material such as a magnesium-doped lanthanum chromite material. In other embodiments, the ceramic fin 200 may be made out of a silicon carbide material or another type of conductive material.
After the ceramic fin 200 is fabricated, the ceramic fin 200 is then densified 234. In one embodiment, densifying the ceramic fin 200 includes sintering the ceramic fin 200. For example, pressureless sintering may be used to densify the ceramic fin 200. In another embodiment, densifying the ceramic fin 200 includes hot pressing the ceramic fin 200. For example, hot isostatic pressing may be used to densify the ceramic fin 200. Other ceramic densification processes also may be used.
Reference throughout this specification to “one embodiment,” “an embodiment,” or similar language means that the described feature, operation, structure, or characteristic may be implemented in at least one embodiment. Thus, the phrases “in one embodiment,” “in an embodiment,” and similar phrases throughout this specification may, but do not necessarily, refer to the same embodiment.
Furthermore, the described features, operations, structures, or characteristics of the described embodiments may be combined in any suitable manner. Hence, the numerous details provided here, such as examples of electrode configurations, housing configurations, substrate configurations, channel configurations, catalyst configurations, and so forth, provide an understanding of several embodiments of the invention. However, some embodiments may be practiced without one or more of the specific details, or with other features operations, components, materials, and so forth. In other instances, well-known structures, materials, or operations are not shown or described in at least some of the figures for the sake of brevity and clarity.
Although specific embodiments of the invention have been described and illustrated, the invention is not to be limited to the specific forms or arrangements of parts so described and illustrated. The scope of the invention is to be defined by the claims appended hereto and their equivalents.
This application claims the benefit of U.S. Provisional Application No. 60/891,421, filed on Feb. 23, 2007, which is incorporated by reference herein in its entirety.
Number | Name | Date | Kind |
---|---|---|---|
3159765 | Schultz | Dec 1964 | A |
3863107 | Mogensen et al. | Jan 1975 | A |
3920417 | Fernandez | Nov 1975 | A |
3974108 | Staut et al. | Aug 1976 | A |
4141694 | Camacho | Feb 1979 | A |
4144444 | Dementiev et al. | Mar 1979 | A |
4198590 | Harris | Apr 1980 | A |
4361441 | Tylko | Nov 1982 | A |
4485334 | de Witte | Nov 1984 | A |
4580505 | Golden | Apr 1986 | A |
4588850 | Mueller et al. | May 1986 | A |
4606799 | Pirklbauer et al. | Aug 1986 | A |
4640023 | Mori et al. | Feb 1987 | A |
4661763 | Ari et al. | Apr 1987 | A |
4861446 | Blom et al. | Aug 1989 | A |
4934283 | Kydd | Jun 1990 | A |
5043636 | Klopotek et al. | Aug 1991 | A |
5339754 | Lyon | Aug 1994 | A |
5376332 | Martens et al. | Dec 1994 | A |
5399829 | Ogilvie | Mar 1995 | A |
5460792 | Rosenbaum | Oct 1995 | A |
5492777 | Isenberg et al. | Feb 1996 | A |
RE35219 | Kent | Apr 1996 | E |
5711859 | Caramel et al. | Jan 1998 | A |
5993761 | Czernichowski et al. | Nov 1999 | A |
6007742 | Czernichowski et al. | Dec 1999 | A |
6152050 | Tsantrizos et al. | Nov 2000 | A |
6810821 | Chan | Nov 2004 | B2 |
6924608 | Czernichowski et al. | Aug 2005 | B2 |
7089745 | Roby et al. | Aug 2006 | B2 |
7299756 | Gnedenko et al. | Nov 2007 | B2 |
7459594 | Czernichowski et al. | Dec 2008 | B2 |
7588746 | Muradov et al. | Sep 2009 | B1 |
7973262 | Matveev | Jul 2011 | B2 |
20010020582 | Barankova et al. | Sep 2001 | A1 |
20020185487 | Divakar et al. | Dec 2002 | A1 |
20030024806 | Foret | Feb 2003 | A1 |
20040065259 | Inazumachi et al. | Apr 2004 | A1 |
20050269978 | Czernichowski et al. | Dec 2005 | A1 |
20060016471 | Greiff | Jan 2006 | A1 |
20060018823 | Czernichowski et al. | Jan 2006 | A1 |
20060144305 | Vera | Jul 2006 | A1 |
20060154189 | Ramotowski | Jul 2006 | A1 |
20060234100 | Day et al. | Oct 2006 | A1 |
20060279290 | Swenson et al. | Dec 2006 | A1 |
20070186474 | Rabovitser et al. | Aug 2007 | A1 |
20070254966 | Eskin et al. | Nov 2007 | A1 |
20090056222 | Gutsol et al. | Mar 2009 | A1 |
20090056604 | Hartvigsen et al. | Mar 2009 | A1 |
20090100752 | Sessa et al. | Apr 2009 | A1 |
20090119994 | Johnson et al. | May 2009 | A1 |
20100266908 | de Graffenried, Sr. | Oct 2010 | A1 |
20120118862 | Hartvigsen et al. | May 2012 | A1 |
Number | Date | Country |
---|---|---|
1059065 | Jul 1979 | CA |
378296 | Jun 1964 | CH |
0601797 | Jun 1994 | EP |
374278 | Jun 1907 | FR |
2049269 | Mar 1971 | FR |
2593493 | Jul 1987 | FR |
2639172 | May 1990 | FR |
2689116 | Oct 1993 | FR |
2724806 | Mar 1996 | FR |
2775864 | Sep 1999 | FR |
2873306 | Jan 2006 | FR |
2172011 | Sep 1986 | GB |
5828186 | Feb 1983 | JP |
5508830 | Aug 1992 | JP |
6016471 | Jan 1994 | JP |
8150315 | Jun 1996 | JP |
9276691 | Oct 1997 | JP |
01514150 | Sep 2001 | JP |
2003251176 | Sep 2003 | JP |
2004339557 | Dec 2004 | JP |
172152 | Jul 1995 | PL |
196319 | Jan 2003 | PL |
112225 | Jun 1997 | RO |
WO-9212929 | Aug 1992 | WO |
WO-9426656 | Nov 1994 | WO |
PCTGB9401818 | Mar 1995 | WO |
WO-9506225 | Mar 1995 | WO |
WO-9911572 | Mar 1999 | WO |
WO-2011119274 | Sep 2011 | WO |
Number | Date | Country | |
---|---|---|---|
20120267996 A1 | Oct 2012 | US |
Number | Date | Country | |
---|---|---|---|
60891421 | Feb 2007 | US |