Method of combusting coal in concentrated streams with NOx reduction
12 claims: 1 independent, 11 dependent
- 1Zastrzeżenia patentowe 1. Sposób spalania węgla w skoncentrowanych strumieniach z redukcją NOx, w którym za pomocą nośnika gazowego wprowadza się do komory spalania rozpylone, stałe paliwo węglowodorowe, znamienny tym, że ze strumienia paliwa zasilającego tworzy się przynajmniej jeden strumień obejmujący paliwo i nośnik, przy czym stosunek ilości paliwa do nośnika w tym strumieniu jest większy niż w stosunek iloś ci paliwa do noś nika w strumieniu zasilają cym, a nastę pnie podaje się uzyskany strumień i powietrze z palnika (3) do komory spalania (1), wdmuchując tlen do tego strumienia przy lub w pobliż u palnika (3) i spala się paliwo wprowadzone w tym strumieniu w komorze spalania (1) wraz z powietrzem i tlenem w obszarze pł omienia posiadają cym strefę (8), bogatą w paliwo, w której to strefie, ilość tlenu jest mniejsza niż 25% ilości stechiometrycznej, wymaganej do zrealizowania spalania zupełnego dostarczonego paliwa i utrzymuje się tę strefę, podczas gdy redukuje się ilość powietrza podawanego przez palnik (3) przy ilości zawierającej wystarczającą ilość tlenu, tak że w całej strefie spalania zależność stechiometryczna zmienia się nie więcej, niż w granicach 10% w porównaniu do zależności stechiometrycznej uzyskiwanej bez dodawania tlenu.
- 2Sposób według zastrz. 1, znamienny tym, że w strefie bogatej w paliwo zależność stechiometryczna wynosi od 0,6 do 1,0.
- 3Sposób według zastrz. 1, znamienny tym, że ze źródła (7) dodaje się powietrze, inne od tego, które podawane jest z palnika do obszaru (9) wewnątrz komory spalania (1), poza strefą (8), bogatą w paliwo i tworzy się pierwotną strefę spalania, przy czym powietrze podaje się w ilości zawierającej przynajmniej taką ilość tlenu, która jest wystarczająca do tego, żeby ogólna ilość tlenu podawanego do komory spalania (1) była równa przynajmniej ilości stechiometrycznej, koniecznej do zupełnego spalenia paliwa.
- 4Sposób według zastrz. 3, znamienny tym, że w pierwotnej strefie spalania zależność stechiometryczna jest zawarta między 0,6 i 1,0.
- 5Sposób według zastrz. 1, znamienny tym, że jako paliwo stosuje się węgiel.
- 6Sposób według zastrz. 5, znamienny tym, że w strefie bogatej w paliwo zależność stechiometryczna wynosi od 0,6 do 1,0.
- 7Sposób według zastrz. 5, znamienny tym, że ponadto ze źródła (7) dodaje się powietrze, inne od tego, które podawane jest z palnika do obszaru (9) wewnątrz komory spalania (1), poza strefą (8), bogatą w paliwo i tworzy się pierwotną strefę spalania, przy czym powietrze podaje się w ilości zawierającej przynajmniej taką ilość tlenu, która jest wystarczająca do tego, żeby ogólna ilość tlenu podawanego do komory spalania (1) była równa przynajmniej ilości stechiometrycznej, koniecznej do zupełnego spalenia paliwa.
- 8Sposób według zastrz. 7, znamienny tym, że w pierwotnej strefie spalania zależność stechiometryczna jest zawarta między 0,6 i 1,0. PL 196 858 B1
- 9Sposób według zastrz. 5, znamienny tym, że jako nośnik paliwa stosuje się powietrze.
- 10Sposób według zastrz. 5, znamienny tym, że w strefie bogatej w paliwo zależność stechiometryczna wynosi od 0,6 do 1,0.
- 11Sposób według zastrz. 9, znamienny tym, że ponadto ze źródła (7) dodaje się powietrze, inne od tego, które podawane jest z palnika do obszaru (9) wewnątrz komory spalania (1), poza strefą (8), bogatą w paliwo i tworzy się pierwotną strefę spalania, przy czym powietrze podaje się w ilości zawierającej przynajmniej taką ilość tlenu, która jest wystarczająca do tego, żeby ogólna ilość tlenu podawanego do komory spalania (1) była równa przynajmniej ilości stechiometrycznej, koniecznej do zupełnego spalenia paliwa.
- 12Sposób według zastrz. 7, znamienny tym, że w pierwotnej strefie spalania zależność stechiometryczna jest zawarta między 0,6 i 1,0.
Independent claims12
77 paragraphs in 5 sections, as filed
(12) PATENT DESCRIPTION (19) PL (11) 196858 (13) B1 (21) Application number: 361169 <sup>(51) Int.Cl.</sup>
F23K 5/00 (2006.01) (22) Reported date: 09/07/2003 (54) Method of burning coal in concentrated streams with NOX reduction
<td>(30) Priority: 2002-07-11, US, 10 / 194,828</td><td>(73) The right holder of the patent: PRAXAIR TECHNOLOGY, INC., Danbury, US</td>
<td>(43) Application was announced: 12.01.2004 BUP 01/04</td><td>(72) Inventor (s): Hisashi Kobayashi, Putnam Valley, US Lawrence E.III Bool, East Aurora, US William J. Snyder, Ossining, US</td>
<td>(45) The grant of the patent was announced: 29 February 2008 WUP 02/08</td><td>(74) Representative: Misztak Irena, PATPOL Sp. z o. o</td>
(57) 1. A process for the combustion of coal in concentrated streams with NOx reduction in which an atomized solid hydrocarbon fuel is introduced into the combustion chamber by means of a gaseous carrier, characterized in that at least one fuel-carrier stream is formed from the feed fuel stream, wherein the fuel ratio is the carrier in this stream is greater than the ratio of fuel to carrier in the feed stream, and then the resulting stream and air from the burner (3) are fed into the combustion chamber (1), blowing oxygen into this stream at or near the burner (3), and the fuel introduced in this stream in the combustion chamber (1) is burned together with the air and oxygen in a flame region having a fuel-rich zone (8), in which zone, the amount of oxygen is less than 25% of the stoichiometric amount required to effect complete combustion of the fuel supplied, and this zone is maintained; while reducing the amount of air fed through the burner (3) with an amount containing sufficient oxygen, such that the stoichiometric relationship in the entire combustion zone changes no more than within 10% compared to the stoichiometric relationship obtained without the addition of oxygen.
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PL 196 858 B1
Description of the invention
The present invention relates to a process for the combustion of coal in concentrated streams with the reduction of NOx, as well as solid fuels containing hydrocarbon compounds, especially fuels containing bound nitrogen.
Combustion of coal in the combustion chambers of power plants remains the basic means of generating energy. Since such combustion causes NOx emissions to the atmosphere, which contributes to the pollution of the natural environment, it is necessary to identify the main methods of reducing NOx emitted to the atmosphere during combustion.
One way to reduce NOx is to use any of the multistage combustion methods, or to use low NOx aerodynamic burners and supply air over the flame. In low-NOx aerodynamic burners, when the fuel is mixed with sufficient air for complete combustion of the fuel, flame development is delayed with a relatively large fuel-rich flame region. In general, multi-stage combustion, or multi-stage combustion with secondary air supply in the area above the primary air supply for combustion, provides only a partial supply of oxygen necessary for complete combustion of the coal, with fuel being supplied to the burner in the primary combustion zone to produce a fuel-rich flame region. following the fuel-poor area to which a balance quantity of combustion air is supplied, (secondary air) to make up the amount of air necessary for fuel combustion. The main complete combustion zone, with the exception of the area near the burner, where primary air is blown in and not yet fully mixed with the fuel, a fuel-rich area may be produced under multi-stage combustion conditions, resulting in a significant increase in emission reduction times NOx. In order to achieve combustion conditions where a fuel-rich region is formed, it is proposed in the prior art to limit the amount of primary air supplied with the fuel to the main combustion zone, and to add combustible gases to this region, or to use an oxygen-poor, recirculated flue gas stream. . The addition of an oxygen-poor gas stream in this region in the prior art process is disadvantageous as it is not compatible with the stated aim of eliminating excess oxygen from this region of the flame. In combustion chambers where pulverized coal is burned, it is normally transported to and through the burner in the form of a stream of coal particles intimately mixed with primary air (so-called "lift air").
The carrier air is also used to some extent as the air necessary for the combustion of coal. The carrier air may also contain exhaust gas recirculated from the exhaust gas circuit, or combustion products used in the case of burners with internal passages, to limit the amount of moisture in the coal. Limiting the amount of carrier air is one of the known methods of reducing the amount of NOx produced by burning coal. However, in many cases limiting the amount of carrier air is impossible to implement if it adversely affects the operation of the coal mill and the entire coal supply and appropriate separation system.
A second known NOx reduction method when pulverized coal burners are used is that concentrating devices or coal crushers are used. Coal concentrating devices or crushers separate, under the inertia forces, of the coal particles and air from the carrier air stream at or near the burner tip in two or more separate pulverized coal streams at which the velocity at which the coal particles flow in one or more the number of streams is greater than in the other streams. These devices blow two or more jets separately or in layers into the combustion chamber. In this way, the fuel-rich stream burns under the conditions specified for such a stream, and along with the fuel-lean stream, there would be additional air and some heat necessary to carry out the coal denitrification process. These devices also allow the burner range to be reduced, because as the burner loads with pulverized coal are reduced, along with a reduction in combustion speed (less coal and less carrier air), the concentrators allow the coal streams to be densified at the burner tip, which helps to maintain stability. ignition of the flame. Methods of this kind are generally known in the industry, and many coal concentrators for this purpose are currently used. However, the proposed regulations regarding the NOX content in the exhaust from steam boilers are very strict and the application of the system
Combustion using only a coal concentrator and with the low NOx emissions of the prior art is insufficient to comply with these regulations.
Thus, a need arose for a method of burning coal whereby both NOx emissions are low and the content of unburned carbon particles in the ashes is significantly reduced, preferably by taking advantage of the advantages of using coal concentrators.
The present invention relates to a process for the combustion of coal in concentrated streams with NOx reduction, in which an atomized solid hydrocarbon fuel is introduced into the combustion chamber by means of a gaseous carrier. The subject matter of the invention is that at least one stream comprising fuel and carrier is formed from the feed fuel stream, the fuel to carrier ratio in this stream being greater than the fuel to carrier ratio in the feed stream.
The resulting stream and air from the burner are then fed into the combustion chamber by blowing oxygen into the stream at or near the burner. The supplied fuel introduced in this stream burns in a combustion chamber together with air and oxygen in a region of the flame having a fuel-rich zone, in which zone, the amount of oxygen is less than 25% of the stoichiometric amount required to effect complete combustion of the supplied fuel. This zone is maintained while the amount of air supplied by the burner is reduced with sufficient oxygen such that the stoichiometric relationship in the entire combustion zone changes no more than 10% compared to the stoichiometric relationship obtained without the addition of oxygen. Preferably, the stoichiometric relationship is between 0.6 and 1.0 in the fuel-rich zone.
According to the invention, air is added from a suitable source, different from that supplied from the burner to the area inside the combustion chamber, outside the fuel-rich zone, and a primary combustion zone is created. The air is supplied in an amount containing at least the amount of oxygen sufficient to ensure that the total amount of oxygen supplied to the combustion chamber is at least the stoichiometric amount required to completely burn the fuel.
In the primary combustion zone, the stoichiometric relationship is between 0.6 and 1.0.
In the process according to the invention, coal is used as fuel and air is used as the fuel carrier.
It is understood that one or more coal and air streams can be produced having a greater proportion of fuel solids to air than the feed stream, but there is no need for the stream or streams to produce separate streams whose dependencies are the inverse quantification between solid particles and air, although such fluxes may occur. This means that there may be areas in the combustion chamber where both types of jets of fuel-air mixture occur.
The invention relates to a high temperature combustion process in which a fuel rich flame zone is created by first concentrating the carbon stream and then introducing oxygen to the concentrated stream in a localized area at the burner discharge. This allows a relatively high concentration of oxygen to be achieved, which contacts the carbon and can sustain the stoichiometric relationships at or below the original amount of air depending on the degree of carbon concentration achieved.
The combination of local high oxygen concentrations with low stoichiometric relationships creates ideal conditions for reducing the level of nitrogen oxide production. The use of oxygen with concentrated coal streams can achieve these conditions, excluding some of the inert components, i.e. nitrogen contained in the air, from the normal combustion process of coal, which allows a higher combustion temperature to be achieved and contributes to the overall reduction of oxide emissions. nitrogen, and reduces the amount of unburned carbon in the ash. In addition, when oxygen is supplied in this way, less oxygen is required, which is significant for the economy of the process.
By the term "stoichiometric relationship" is meant the ratio of the oxygen fed to the furnace to the amount of oxygen that would be required to convert all the carbon, sulfur and hydrogen contained in the substances entering the combustion chamber into carbon dioxide, sulfur dioxide and water. In the fuel-rich zone, the stoichiometric relationship is particularly preferably between 0.7 and 0.85.
The term NOx is understood to mean nitrogen oxides such as NO, NO2, NO3, N2O, N2O3, N2O4, N3O4 and mixtures thereof. The term "multi-stage combustion using low-NOx burners" as used in the description means combustion in a combustion chamber in which the process of mixing the fuel with the air necessary for complete combustion of that fuel is delayed to produce a flame having a relatively fuel-rich zone. The solution according to the invention uses the generally known multi-stage combustion process, in which the air streams necessary for complete combustion,
They are introduced into the combustion chamber at different levels, also above the flame region.
A gaseous medium with or without oxygen was used as a carrier for the pulverized coal, allowing the transport of pulverized coal without the risk of its ignition in the fuel lines. This support may contain inert components also derived from the primary combustion process. Practically the flow volume of the carrier gas should be adequate to introduce and move the pulverized coal particles in all dimensions. The term "bound nitrogen" also includes nitrogen, which is part of a molecule that also contains carbon and hydrogen, sometimes also oxygen.
1 shows a longitudinal section of a device for carrying out the method according to the invention, fig. 2 - a longitudinal section of a burner used to carry out the method according to the invention, fig. 3-6 show longitudinal sections of a device for carrying out the method according to the invention for forming, from the streams of solid fuel and air, streams with a greater velocity of solid fuel compared to air than in the feed area, fig. 7-9 show longitudinal sections of devices for implementing the method. according to the invention used in practice.
While the subject matter of the proposed invention will be described below using terms relating to the combustion processes of coal and air as a carrier gas, similar to that set forth in the preferred embodiments of the invention, the procedures set forth below could be applied to another pulverized fuel and a different gaseous carrier. The present invention has been described using the accompanying drawing figures, which does not limit the scope of protection of the proposed solution.
Generally speaking, the process of the present invention first divides the coal and carrier air stream into several streams ("recovered" streams) in which the first portion of the stream has a higher fuel particle velocity relative to air than in the feed stream. After the formation of the "recovered" stream or streams, one or more streams are formed in which the velocity of the solid fuel particles relative to air is lower in the inlet stream. Oxygen in an amount sub-stoichiometric to the amount of fuel in the resulting stream or streams is then blown into or near the resulting stream in the burner to achieve faster combustion at a higher temperature and gasification of the fuel particles. Subjecting the fuel particles to these conditions, in the earlier periods of combustion, favors the conversion of nitrogen bound in the fuel into N2 more than into NOx and facilitates complete incineration at the end of the combustion process. The streams, or stream relatively low in carbon, are produced by other means, e.g. may be blown into the combustion chamber separately from the oxygen stream, or each is directed to a specific location outside the burner (e.g. above the combustion air or otherwise). stepped air flow).
Generally, the velocity of the feed stream and the more concentrated coal-air mixture stream is from 7.6 m / s to 76 m / s, and preferably 15.2 m / s to 61 m / s. Typically, the ratio of solid fuel to air is from 0.25: 1 to 1.5: 1, and preferably from 0.35: 1 to 0.7: 1. Generally, the ratio of solid fuel to air in the resulting, more concentrated the stream is from 0.4: 1 to 10: 1, preferably 0.5 to 3: 1.
Figure 1 shows the combustion device 1, which may be any device capable of carrying out a combustion process, in the chamber 2 of the device. Furnaces and boilers that are used to generate electricity using conventional means not shown can advantageously be used here. Each of the burners 3, located in the side wall of the combustion apparatus, or at its end, supplies fuel, air and oxygen to chamber 2 from sources outside the combustion apparatus 1. In a preferred embodiment of the invention, the fuel comprises atomized solid hydrocarbon fuels. and in a preferred embodiment, pulverized coal or petroleum coke.
As shown in Fig. 1, and more specifically in Fig. 2, the burner 3 is preferably provided with several concentrically arranged channels, although another structure may also be used to achieve the same effect. Fuel is supplied to the combustion device 1 through the annular channel 4. Preferably, fuel and carrier air are fed from the feed source 20 to one or more burners 3, where the mixture stream passes through the coal concentrator 18 and the resulting streams are blown into chamber 2 of the combustion apparatus 1. Effective amount of primary air supplied as carrier for 0.45 kg of coal it is about 0.68 to 0.9 kg, which corresponds to about 20% of the stoichiometric amount of air necessary for complete combustion of the bituminous coal.
PL 196 858 B1
Primary air 22 is fed by a "FD" fan to one or more air boxes 21 and blown into the air duct of one or more burners 3. Secondary air 15, necessary for combustion, is fed through burner 3 to combustion device 1 preferably through centrally located annular channels 11 surrounding the space 4 through which the hydrocarbon fuel is supplied. Preferably, the third combustion air 16 is fed through the burner 3 to the combustion device 1, preferably through concentrically arranged, annular channels 12 surrounding the secondary air channel. Preferably, the air necessary for combustion is also fed through a nozzle 7 provided in the combustion apparatus (see Fig. 1) above the combustion area.
Preferably, the low NOx burners have a primary (fuel) duct, and second and third air ducts that are designed to provide good aerodynamic control. However, other low NOx burner designs having only first and second air flow passages may be used herein. If optimal three channel designs are used, the airflow of the second can induce vortices, and a flow pattern may occur in the duct with flow characteristics mixed with the aerodynamic streams, as in the case of a three-channel burner. Alternatively, burners with an additional (fourth) duct can be used.
The combustion of the hydrocarbon fuel is carried out using the oxygen contained in the primary air and the oxygen resulting from the formation of the flame 6. The region 8 of the flame closest to the burner 3, i.e. where the hydrocarbon fuel exits the burner, is the fuel-rich zone. The area of the flame 6 around this space is relatively small when the second and third air do not fully react with the fuel. If enough air is supplied through the nozzle 7, located above the flame region, to achieve a general multi-stage combustion, the lower inflow zone of the combustion chamber, or the primary air zone (PCZ), below nozzle 7, becomes a fuel-rich zone, with except in the area near the burners 3 where air is blown in and it has not yet reacted with the fuel.
Advantageously, the air fed through the nozzle opening 7 into the combustion chamber of the device 1 makes the primary combustion zone 10 more fuel-rich and introduces additional oxygen support, allowing complete combustion of the fuel to be achieved in the combustion zone 9. The oxygen contained in the air supplied to the combustion chamber through the burner 3, combined with the oxygen supplied through the nozzle 7, is at least sufficient to enable complete combustion and typically comprises 10 to 15 vol% excess oxygen necessary to completely burn the fuel.
Preferably, the second and third air are fed to the burner 3 in order to swirl the linear flow, thereby creating a recirculation zone proximate the burner, improving the conditions for the formation of the fuel-air mixture. The vortex can be produced by known methods, such as the use of deflectors 13 and 14 mounted in annular channels for the second and third air in the burner, which direct the flow of the jets along the vortex line. Advantageously, a high degree vortex may be used, preferably a predetermined number of vortices, i.e. from 0.6 to 2.0.
Preferably, the total amount of air fed through burner 3, i.e. the sum of the first, second and third air, is between 60% and 100% of the stoichiometric amount required for complete combustion. Most preferably, the total amount of air supplied from burner 3 is 70 to 85% of the stoichiometric amount required for complete combustion.
When oxygen is premixed or mixed at high speed in the carrier stream using 20% stoichiometric air and the total stoichiometric combustion ratio is 1.15, the following average oxygen concentrations in the carrier air and in the whole treated air necessary for combustion have been calculated. .
<td>% of air replaced with O2 *</td><td>O2 concentration in the carrier air (by volume)</td><td>Push. concentr. O2 in the area to burn. (by volume)</td>
<td> 0</td><td> 21,0</td><td> 21,0</td>
<td> 5</td><td> 24,9</td><td> 21,7</td>
<td> 10</td><td> 28,5</td><td> 22,5</td>
<td> 15</td><td> 31,7</td><td> 23,4</td>
<td> 20</td><td> 34,7</td><td> 24,3</td>
<td> 25</td><td> 37,4</td><td> 25,4</td>
(* e.g. 0.142 m<sup>3</sup> air from 0.003 m<sup>3</sup> pure O2 to get the same amount of O2)
PL 196 858 B1
The amount of oxygen supplied to the burners should be sufficient to achieve a stoichiometric ratio in the fuel-rich flame zone of less than 0.85. The amount of oxygen supplied through channel 5 should be less than 25% of the stoichiometric amount necessary for complete combustion of the fuel. It would be more advantageous if this amount corresponds to 15% of the stoichiometric amount required for complete combustion of the fuel.
At the same time, there is a need to reduce the amount of second and third air fed by the burner 3 into the combustion chamber to an amount of oxygen corresponding to that fed through duct 5. More specifically, the amount of second, third and fourth air, if used, in addition, the amount of air fed through the burner 3 should be reduced with an amount of 10% of the amount of oxygen fed to the fuel through duct 5.
The NOx emission depends strongly on the local stoichiometric conditions. When oxygen injection produces a local stoichiometric condition at a lower level, first consider changing the local stoichiometric condition after oxygen injection. For example, blowing oxygen corresponding to 10% of the stoichiometric amount of air into a locally rich zone with a stoichiometric relationship of 0.4, without changing the amount of combustion air, would change the local stoichiometric conditions to 0.5, and a significant reduction could be expected. NOx emissions. This effect is much greater than that obtained by "replacing 10% air with oxygen" as long as the local stoichiometric conditions are kept constant within 0.4, if the amount of oxygen blown into the flame zone is the same, without changing the amount of air blown. , local stoichiometric conditions are kept at 0.95 and NOx emissions increase sharply if local stoichiometric conditions increase to 1.05.
According to the invention, the object of the procedure is to maintain the flame zone at a high temperature by first concentrating the coal stream, which lowers the stoichiometric relationship, and then supplying the concentrated coal stream with oxygen to a localized area at the exit of the burner. This allows for a sufficiently high concentration of oxygen which contacts the carbon fuel and can maintain the stoichiometric ratio at or below the original value for air depending on the degree of carbon concentration achieved.
The combination of locally high oxygen concentrations with low stoichiometric ratios creates ideal conditions to contain NOx formation. The use of oxygen in concentrated coal streams can achieve these conditions by excluding inert components from the coal combustion process, which allows for higher temperatures to be achieved and overall reduces NOx emissions from the combustion process and reduces unburned carbon content in the ash. Thus, when supplying oxygen according to the above-described process, less oxygen is required to achieve favorable combustion conditions, so that the economics of using oxygen is greatly improved. For example, when a coal feed stream containing 20% of the stoichiometric amount of air is used as carrier air a concentrated stream, and the concentrated carbon stream now contains 10% of the stoichiometric amount of air, the following oxygen concentrations in the carrier air stream and the total amount of air necessary for burning, assuming that the oxygen is premixed or immediately after contact with the concentrated carbon stream and that the stoichiometric ratio, taken as a whole, is 1.15.
<td>% of air replaced with O2 *</td><td>O2 concentration in the carrier air (by volume)</td><td>Push. concentr. O2 in the area to burn. (by volume)</td>
<td> 0</td><td> 21,0</td><td> 21,0</td>
<td> 5</td><td> 28,5</td><td> 21,7</td>
<td> 10</td><td> 34,7</td><td> 22,5</td>
<td> 15</td><td> 39,9</td><td> 23,4</td>
<td> 20</td><td> 44,4</td><td> 24,3</td>
<td> 25</td><td> 48,2</td><td> 25,4</td>
(* e.g. 0.142 m<sup>3</sup> air from 0.003 m<sup>3</sup> pure O2 to get the same amount of O2)
The example above shows that the amount of oxygen required to achieve the same oxygen concentration in the carrier air is halved when using a concentrator.
PL 196 858 B1
The injection or mixing of oxygen with the third and fourth air, if used, should not take place in an aerodynamically staged burner without air being supplied above the flame. Theoretically, optimization of the local conditions of the combustion stoichiometry can be carried out with the use of air with any oxidant content. However, oxygen is more effective because only a small volume of this gas is required to change the local combustion stoichiometry conditions without significantly affecting the overall aerodynamic conditions of the burning mixture.
The burner 3 includes a structure 18 through which it is passed and a stream of coal and air is fed. At the outlet of this structure, one or more streams are obtained in which the ratio of the amount of solid fuel to air is higher than that ratio in the feed stream. Known designs of concentrators used to achieve such a purpose are used herein, which operate mainly by inertia, and use the difference in weight between the carbon particles and the carrier gas. When separating the two media, the carbon particles will tend to flow along a straight line and will be mainly affected by the high velocity gas flowing in the channel. This gas can be introduced very easily to change direction and speed than coal, which allows for an easy and sufficient separation for the process.
The injectors for introducing coal into the burners generally have three basic shapes: a central axial channel (i.e., a tube), an annular channel (e.g., a space between two concentric tubes), and a surface or rectangular cross-section (e.g., tangentially positioned boiler injectors). They can be classified into one of the two categories set out above, but can also have a different geometrical configuration that is different from cylindrical carbon injectors. The carbon flowing from each burner design may be concentrated in the radial direction (i.e., towards the outer edge) or in the circumferential direction (i.e. successive high and low density areas scattered around the cross-sectional area of the opening), or a combination of both. The main devices for concentrating the carbon are Venturi tubes which accelerate the mixture and then delay the gas flow, have tangential inlets to create a vortex flow, swirl vanes and flow dividing plates sequentially connecting and separating channels that collect the particles and push them together. Fig. 3 to 6 show some typical examples of such devices in longitudinal section, taken along the concentrated carbon streams they produce.
Figure 3 shows a coal concentrator 30 that uses a venturi 31 to provide carbon-air jets with a greater and less carbon-to-air ratio than that of the stream 32 entering the burner. Passage of the feed stream through the constricted annular throat of the venturi 31 creates a more concentrated carbon stream in area 33, near the inner surface of element 30, and a less concentrated carbon stream flowing through central region 34.
Figure 4 shows a coal concentrator 40 having blades 41 which introduce vortex energy into the incoming feed stream 42. The vortex energy causes more coal particles to move towards an area radially outside the stream, making the coal stream more concentrated in that area. . The vanes 44 restrict the flow as it exits the element.
Figure 5 shows a coal concentrator 50 in which the coal feed stream 51 and air are fed tangentially to the axis of element 50. The stream is then directed into a channel formed in the element, circumferentially imparting energy to the feed stream, causing more the fuel particle flows in an area closer to the inner surface of the element. This produces a more concentrated stream of solid fuel particles than stream 52 surrounding the less concentrated stream 53.
Figure 6 shows a coal concentrator 60 provided with vanes which define successively a converging and diverging shape of the feed flow channels. For example, the blades 61 and 62 converge towards each other, while the blades 62 and 63 diverge towards each other. A more concentrated stream of coal in the air is obtained in the channels existing between the converging pairs of blades, and a less concentrated stream is produced in the channels formed between the converging pairs of blades. This type of concentrator produces streams in which the concentration of solid fuel particles in the air around the circumference of the element is varied, while the elements shown in Fig. 3-5 produce jets in which the concentration varies along the radius of the element.
PL 196 858 B1
In the case of smooth pipes through which carbon particles and air flow, the concentration of the carbon usually occurs at the inner edge of the pipe wall, or less commonly around the center of the pipe. This is because the more concentrated coal stream is usually so positioned that it can interact with the pointed element of the flame stabilizers. Under conditions where a more concentrated coal flow is obtained at the inner surface of the tube, the best solution would be an annular flow of oxygen surrounding the tube through which the carbon particles pass. This stream should be blown in a direction along or at an angle to the flow axis of the coal particle stream. Such a configuration is shown in Fig. 7, whereby stream 71 is fed tangentially to element 70 and exits as stream 72, represented by dark arrows, this stream having a carbon concentration greater than the feed stream 71, and stream 73, represented by light arrows, with whereby this stream has a carbon concentration lower than the feed stream 71. A stream of oxygen 74 is fed to the annular channel 75 from which the outgoing oxygen contacts the concentrated stream 72 of the carbon-air mixture. The burner may have deflectors or vanes at the top of the burner to slow down the vortex flow, but the carbon stream usually flows out with swirling. The vortex energy of the tangential blowing of the coal flow also causes the air flow to travel radially outward, although slower than the coal flow, so that the ratio of carbon to air may not be as high as in other combustion methods.
Figure 8 shows the method of the present invention in practice using a carbon concentrator element employing a Venturi 81 installed in the pipe 80. The flow of the feed stream through the venturi 81 causes the carbon particles to concentrate near the center of the pipe 80 and exit. flowing stream closer to the inner surface with a relatively narrow stream. In this situation, an oxygen lance 84 installed below the center of the pipe and provided with injection holes 86, axially or slightly offset from the axis, will mix the oxygen with the most concentrated carbon stream. Depending on the position of the venturi 81, it may be necessary to include concentric deflectors to prevent the concentrated stream from being remixed with the coal lean fuel stream before it exits the torch tip.
In both cases described above, deflectors or swirl blades may be installed in the pipe to induce a layered flow of the carbon stream and divide it into appropriate high and low density segments around the circumference of the pipe. Likewise, two injectors could be used in these cases, the ends of the injectors could not be plugged and holes drilled at various points along the circumference such that the injection point could correspond to the location of the high density jet.
As shown in Fig. 9, a coal concentrator of the type shown in Fig. 6 may be adapted to the present invention by using an axial oxygen lance 91 having a closed end and holes 92 made in the bottom of the lance in an amount appropriate to the number of jets. wherein the ratio of carbon solids to air is greater than in the feed stream. Each of the apertures may be radially positioned with respect to the flowing streams of concentrated coal, or may be inclined or deviated from the axis of the stream by a suitable angle and so located that the concentrated carbon streams exiting the narrow opening intersect between the lobes. In cases where the dense stream is segmented along the circumference of the pipe and directed radially outward, the oxygen rings with holes or slots are located adjacent to the openings from which the dense coal stream flows.
Due to their design, tangentially fired boilers are not equipped with standard burners. In each corner of the boiler there is an air installation and nozzles injecting coal fuel or air into the boiler, which are mutually mixed in the combustion chamber. Due to the fact that the combustion chamber does not have a cylindrical shape, most injectors of this type are equipped with blades arranged in converging and diverging channels. Due to the fact that they have the same minimum cross-section at the end and beginning of these channels, the air flow is divided fairly evenly. However, the converging channel acts as a funnel and collects more coal particles on the inlet side and causes them to concentrate near the outlet, which favors the coal flux concentration process. With this design, oxygen could be delivered via
An annulus surrounding the carbon nozzle (typically a secondary air source) or through a plurality of lances installed in the dense coal stream in the burner.
When oxygen is blown into a dense coal stream, it should be mixed with the stream, but it can be envisaged that the oxygen will cause a recoil effect or obstruct the model flow as it exits the nozzle. With this in mind, oxygen should be injected at a velocity close to that of coal fuel injection. A typical range for this speed is 50 to 150% of the velocity achieved by the coal fuel stream, and an attempt should be made to equalize these velocities. When the air streams are split and the oxygen injectors occupy part of the carbon channel space, it can be difficult to precisely determine the velocity of the carbon particles in the dense stream.
In addition to the inertia devices described above, other methods may be used to concentrate the coal flux before it is mixed with oxygen. External devices such as cyclones can be mounted next to the burner and the two layered streams then enter the burner through two separate channels. Oxygen could be blown somewhere in, along, or around a channel through which the dense coal fuel stream flows. As such, external separation devices can be used in exceptional cases where the coal lean stream is introduced into the combustion chamber at a distance from the high carbon density stream.
Contents5
6 sheets
Sheet 1 Sheet 2 Sheet 3 Sheet 4 Sheet 5 Sheet 6
Every citation, both ways
| Document | Relation | Office | Cited during |
|---|---|---|---|
| PL425271A1 | Cited by | Poland | Search report |
93 members in 14 offices
Priority claims3
| Document | Office | Kind | Date |
|---|---|---|---|
| 19482802 | United States of America | A | |
| 10194828 | – | – | – |
| US20020194828 | – | – | – |
Members93
| Document | Office | Kind | |
|---|---|---|---|
| CA2434445A1 | Canada | A1 | |
| WO02055933A1 | World Intellectual Property Organization (WIPO) | A1 | |
| US2002127505A1 | United States of America | A1 | |
| US2003009932A1 | United States of America | A1 | |
| US2003091948A1 | United States of America | A1 | |
| US2003099912A1 | United States of America | A1 | |
| US2003099913A1 | United States of America | A1 | |
| US2003104328A1 | United States of America | A1 | |
| US2003108833A1 | United States of America | A1 | |
| MXPA03006238A | Mexico | A | |
| EP1350063A1 | European Patent Office (EPO) | A1 | |
| CA2485934A1 | Canada | A1 | |
| WO03096918A1 | World Intellectual Property Organization (WIPO) | A1 | |
| WO03098024A2 | World Intellectual Property Organization (WIPO) | A2 | |
| TW200306884A | Taiwan Province of China | A | |
| AU2003237815A1 | Australia | A1 | |
| AU2003237884A1 | Australia | A1 | |
| BR0116771A | Brazil | A | |
| US2003236518A1 | United States of America | A1 | |
| CA2434774A1 | Canada | A1 | |
| PL361169A1 | Poland | A1 | |
| CA2492115A1 | Canada | A1 | |
| WO2004007351A2 | World Intellectual Property Organization (WIPO) | A2 | |
| WO2004008027A2 | World Intellectual Property Organization (WIPO) | A2 | |
| WO2004008028A2 | World Intellectual Property Organization (WIPO) | A2 | |
| KR20040007278A | Republic of Korea | A | |
| AU2003212026A1 | Australia | A1 | |
| TW200401871A | Taiwan Province of China | A | |
| AU2003247916A1 | Australia | A1 | |
| AU2003247916A8 | Australia | A8 | |
| AU2003248848A1 | Australia | A1 | |
| AU2003248848A8 | Australia | A8 | |
| AU2003253817A1 | Australia | A1 | |
| AU2003253817A8 | Australia | A8 | |
| JP2004037072A | Japan | A | |
| US6699029B2 | United States of America | B2 | |
| US6699030B2 | United States of America | B2 | |
| US6699031B2 | United States of America | B2 | |
| US6702569B2 | United States of America | B2 | |
| KR20040028709A | Republic of Korea | A | |
| US2004074427A1 | United States of America | A1 | |
| CN1492982A | China | A | |
| EP1416221A1 | European Patent Office (EPO) | A1 | |
| TW200409884A | Taiwan Province of China | A | |
| CN1510334A | China | A | |
| TW200412408A | Taiwan Province of China | A | |
| JP2004523717A | Japan | A | |
| BR0302366A | Brazil | A | |
| WO2004007351A3 | World Intellectual Property Organization (WIPO) | A3 | |
| WO2004008028A3 | World Intellectual Property Organization (WIPO) | A3 | |
| WO2004008027A3 | World Intellectual Property Organization (WIPO) | A3 | |
| TW200419110A | Taiwan Province of China | A | |
| MXPA04011343A | Mexico | A | |
| KR20050017111A | Republic of Korea | A | |
| WO2004007351A9 | World Intellectual Property Organization (WIPO) | A9 | |
| WO03098024A3 | World Intellectual Property Organization (WIPO) | A3 | |
| EP1537362A2 | European Patent Office (EPO) | A2 | |
| EP1540252A2 | European Patent Office (EPO) | A2 | |
| PL373563A1 | Poland | A1 | |
| CN1666065A | China | A | |
| CN1668876A | China | A | |
| CN1668877A | China | A | |
| US6957955B2 | United States of America | B2 | |
| EP1350063A4 | European Patent Office (EPO) | A4 | |
| CN1243927C | China | C | |
| TWI272356B | Taiwan Province of China | B | |
| TWI272357B | Taiwan Province of China | B | |
| TWI275414B | Taiwan Province of China | B | |
| KR100709849B1 | Republic of Korea | B1 | |
| US7225746B2 | United States of America | B2 | |
| CN1328540C | China | C | |
| US2007215022A1 | United States of America | A1 | |
| CN100343574C | China | C | |
| CN100343576C | China | C | |
| JP4017521B2 | Japan | B2 | |
| PL196858B1This record | Poland | B1 | |
| CN100394109C | China | C | |
| AU2003237815B2 | Australia | B2 | |
| AU2003212026B2 | Australia | B2 | |
| US7438005B2 | United States of America | B2 | |
| CA2434445C | Canada | C | |
| US7588565B2 | United States of America | B2 | |
| CA2485934C | Canada | C | |
| US2010042092A1 | United States of America | A1 | |
| US2010057075A1 | United States of America | A1 | |
| KR101030361B1 | Republic of Korea | B1 | |
| EP1350063B1 | European Patent Office (EPO) | B1 | |
| PL212230B1 | Poland | B1 | |
| EP1537362A4 | European Patent Office (EPO) | A4 | |
| ES2392506T3 | Spain | T3 | |
| IN2631DEN2012A | India | A | |
| EP1537362B1 | European Patent Office (EPO) | B1 | |
| ES2566798T3 | Spain | T3 |
1 legal event, as the office reported them to INPADOC
Events
| Event | Code | |
|---|---|---|
| Decisions on the lapse of the protection rightsLapsedLAPS | LAPS |
Numbers
- Publication
- 196858
- Publication, DOCDB
- 196858
- Publication, EPODOC
- PL196858B
- Application
- 361169
- Application, DOCDB
- 36116903
- Application, EPODOC
- PL20030361169
Titles2
- English
- Method of combusting coal in concentrated streams with NOx reduction
- Polish
- Sposób spalania węgla w skoncentrowanych strumieniach z redukcją NOx
Classification
- CPC, 21
- F23C5/32
- F23C6/045
- F23C6/047
- F23C7/004
- F23C2201/101
- F23C2201/20
- F23C2900/06041
- F23C2900/99004
- F23D1/00
- F23D14/24
- F23D2900/00006
- F23D2900/01001
- F23L7/007
- F23L2900/07006
- F23L2900/07007
- F23N2237/08
- F23N2037/08
- F23N2237/28
- F23N2037/28
- Y02E20/344
- Y02E20/34
- IPC, 10
- F23C99 00
- F23K5 00
- A61B18 08
- F23C5 32
- F23C6 04
- F23C7 00
- F23D1 00
- F23D14 24
- F23D14 32
- F23L7 00
