EP3734158B1 - Method for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, particularly grate boilers. - Google Patents
Method for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, particularly grate boilers. Download PDFInfo
- Publication number
- EP3734158B1 EP3734158B1 EP20020236.4A EP20020236A EP3734158B1 EP 3734158 B1 EP3734158 B1 EP 3734158B1 EP 20020236 A EP20020236 A EP 20020236A EP 3734158 B1 EP3734158 B1 EP 3734158B1
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- European Patent Office
- Prior art keywords
- furnace chamber
- process gas
- injection
- reagent
- injected
- Prior art date
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- 238000000034 method Methods 0.000 title claims description 148
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims description 56
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims description 39
- 230000009467 reduction Effects 0.000 title claims description 22
- 229910002091 carbon monoxide Inorganic materials 0.000 title claims description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 6
- 230000008569 process Effects 0.000 claims description 110
- 239000007789 gas Substances 0.000 claims description 108
- 239000003153 chemical reaction reagent Substances 0.000 claims description 83
- 238000002347 injection Methods 0.000 claims description 82
- 239000007924 injection Substances 0.000 claims description 82
- 239000003546 flue gas Substances 0.000 claims description 50
- 239000000446 fuel Substances 0.000 claims description 15
- 241000842962 Apoda limacodes Species 0.000 claims description 13
- 238000010586 diagram Methods 0.000 claims description 5
- 239000000203 mixture Substances 0.000 claims description 4
- 238000006722 reduction reaction Methods 0.000 description 30
- 238000002485 combustion reaction Methods 0.000 description 27
- 239000000243 solution Substances 0.000 description 15
- 239000010881 fly ash Substances 0.000 description 14
- 239000003245 coal Substances 0.000 description 8
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 7
- 229910052799 carbon Inorganic materials 0.000 description 7
- 239000001301 oxygen Substances 0.000 description 7
- 229910052760 oxygen Inorganic materials 0.000 description 7
- 239000000047 product Substances 0.000 description 7
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 5
- 238000009434 installation Methods 0.000 description 5
- 239000002956 ash Substances 0.000 description 4
- 230000008901 benefit Effects 0.000 description 4
- 150000002830 nitrogen compounds Chemical class 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 3
- 239000000428 dust Substances 0.000 description 3
- 229910017464 nitrogen compound Inorganic materials 0.000 description 3
- 230000003134 recirculating effect Effects 0.000 description 3
- 230000002441 reversible effect Effects 0.000 description 3
- 239000011265 semifinished product Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 235000011114 ammonium hydroxide Nutrition 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000005260 corrosion Methods 0.000 description 2
- 230000007797 corrosion Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 239000007800 oxidant agent Substances 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- 231100000167 toxic agent Toxicity 0.000 description 2
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000003628 erosive effect Effects 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 239000002737 fuel gas Substances 0.000 description 1
- 239000008240 homogeneous mixture Substances 0.000 description 1
- 230000001939 inductive effect Effects 0.000 description 1
- 238000003780 insertion Methods 0.000 description 1
- 230000037431 insertion Effects 0.000 description 1
- 238000007689 inspection Methods 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 230000000670 limiting effect Effects 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 230000000737 periodic effect Effects 0.000 description 1
- 238000011946 reduction process Methods 0.000 description 1
- 230000002787 reinforcement Effects 0.000 description 1
- 230000002269 spontaneous effect Effects 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Images
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J7/00—Arrangement of devices for supplying chemicals to fire
-
- 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
- F23C9/00—Combustion apparatus characterised by arrangements for returning combustion products or flue gases to the combustion chamber
-
- 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
- F23C2202/00—Fluegas recirculation
Definitions
- the object of the invention is a method for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, especially grate boilers and a system for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, especially grate boilers, used to reduce the formation of nitrogen oxides and carbon monoxide and/or their reduction in the furnace chambers of heating boilers and power boilers, especially grate boilers, and a system for the application of this method.
- the method described in the patent application P.423576 assumes that the process gas, or process gas and reagent, are injected into the furnace chamber in the opposite direction to the main natural direction of the flue gas flow through the chamber, preferably from top to bottom, i.e. in the case of injection from the top, side or front wall of the firebox, in the direction of temperature rise in the furnace chamber, and in the case of process gas injection through lances from the back wall of the firebox, as an additional reinforcement of the swirl, the process gas is supplied horizontally, with a jet deviation of +/-45°, in a plane parallel to the longitudinal symmetry plane of the furnace chamber.
- the process gas injection points are located on the front, top, side or rear wall of the furnace chamber, while the reagent and process gas injection points are located on the front, side or top wall of the furnace chamber, while the process gas injection points are located at a distance of up to 0.5 depth of the furnace chamber from the pipe axis of the front wall while when process gas is injected from the rear wall of the furnace chamber, the injection points are located at a distance of up to 0.2 depth of the furnace chamber from the pipe axis of the rear wall of the chamber.
- the above described method of feeding process gas or process gas and reagent causes a flue gas stream of high NOx concentration at the rear wall of the furnace chamber, on a significant part of the boiler width, and the described method of feeding process gas and reagent through lances mounted on the side walls of the boiler furnace chamber makes it possible for the reagent to enter this stream and reduce NOx compounds in this area.
- the technical problem to be solved is how to eliminate the abovementioned drawbacks and limitations, while guaranteeing further reduction of NOx emissions, reduction of CO emissions, minimising or completely eliminating the reagent in flue gases and fly ashes, increasing the efficiency of the system and lowering operating costs.
- the essence of the invention which is a method for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, especially grate boilers consists in that process gas, being air, flue gas or combustion air mixture, in its full range, i.e.
- process gas is supplied to the furnace chamber at a speed of 30 to 180 m/s, preferably 135 m/s, in the amount of up to 20% of stoichiometric air demand necessary to burn the fuel supplied to the boiler, preferably 15%, with up to 60% of the process gas being injected via lances built into the front wall of the furnace chamber, with up to 60% of the process gas being injected through lances installed on the rear wall of the furnace chamber, up to 25% of the process gas is injected through lances installed on the upper wall of the furnace chamber and up to 15% of the process gas is injected through lances installed on the side walls of the furnace chamber; moreover, the reagent is delivered to the furnace chamber at a rate of 30 to 180 m/s, preferably 135
- temperature and the share of O 2 , CO or NOx in the flue gas such parameters being monitored by measuring devices mounted inside the furnace chamber in the form of temperature sensors and/or devices mounted outside the furnace chamber being the flue gas analyser, and the regulation is carried out by means of actuators individually for each injection point or group of injection points mounted on a given wall of the furnace chamber, on a given level or with a specific injection direction.
- the dynamic effect of the process gas stream was used to intensify the mixing process in the furnace chamber by inducing strong internal flue gas recirculation inside the furnace chamber and a strong swirl whose direction is opposite to the main, natural flue gas flow direction and the swirl plane is parallel to the longitudinal symmetry plane of the furnace chamber.
- the solution according to the method allows for precise control of the temperature in the furnace chamber in the area where nitrogen oxides are reduced and CO is burned, reducing the concentration of the reagent in the furnace chamber, which minimises the risk of corrosion of the equipment components; moreover, the invention according to one of the embodiments, increases the capacity of the system by placing the lances on several levels of the furnace chamber, especially in the case of a considerable variability of the boiler load and this is usually used in units with higher power output.
- the invention according to the method also reduces reagent consumption in relation to known methods and thus allows to minimize the content of unreacted reagent in fly ashes and flue gases, which plays a very important role in terms of system operating costs, environmental protection and ash management.
- the opposite direction of reagent injection in relation to the main, natural direction of flue gas flow and to the inside of the generated swirls, as well as the described points and directions of injection have a very important advantage in relation to the traditional directions and places of reagent injection cited in the state of the art investigation, because in the described method according to the invention, there is no such phenomenon (or if it occurs it is limited to a minimum) as entrainment of unreacted reagent particles, directly after it has been injected into the furnace chamber by the flue gases into the convection part of the boiler, i.e.
- the reduction reaction takes place in the temperature range from 850°C to 1050°C and in the presence of nitrogen compounds; further on, the unreacted particles of the reagent enter the temperature area above 1 050°C where they bind with oxygen and form NOx-type compounds, which then, together with the products of combustion, head up the furnace chamber in accordance with the main natural draught of the combustion chamber where they encounter the unreacted reagent and the temperature conditions required for the occurrence of the NOX reduction reaction; part of the still unreacted reagent and unreacted nitrogen compounds (NOX) are returned to an area convenient for the NOX reduction reaction, through strong swirls of recirculating flue gas produced by the process gas stream.
- NOX nitrogen compounds
- This natural and spontaneous course of the process contributes to the efficiency of the reduction process and to a large extent protects the system against the ingress of unreacted reagent into the ash, dust or flue gas treatment and discharge systems;
- another advantage of the method according to the invention is that the process gas is injected into the furnace chamber in the opposite direction to the natural direction of the flue gas movement in the furnace chamber and at a high rate turns back towards the grate i.e. into the high temperature area, particles of unburned coal, which in the hitherto known solutions are entrained from the layer of coal moving on the grate by the blast air supplied from the grate and, as coal, together with fly ashes enter the dust extraction systems significantly reducing their efficiency.
- the presented method according to the invention significantly reduces the content of the carbon element in fly ash, which directly contributes to the increase in the efficiency of the system and also reduces the amount of fly ash carried by the flue gases leaving the boiler and entering the dedusting systems, which extends the service life of the devices and in newly built units enables the use of smaller first-stage dedusting systems reducing the equipment cost. This effect is particularly noticeable when burning poorer quality coal containing a lot of coal fines.
- the presented method of feeding the process gas or process gas and reagent produces a strong, main, reverse internal recirculation swirl and, depending on the boiler capacity, one to two additional swirls, one called the upper swirl, which is formed in the area bounded by the front wall, the upper and the stream of process gas injected from the lances mounted on the rear wall of the furnace chamber, this swirl being particularly noticeable at medium and high boiler loads, and a second one, called the down swirl, which is formed in the area bounded by the rear wall, the grate deck and the flue gas stream moving from the front zones of the grate towards the rear wall and further on towards the festoon, this swirl being particularly noticeable at low boiler loads;
- the main swirl and the upper swirl generated at medium and high boiler loads suck in flue gases from the main flue gas stream, from the area just before the furnace chamber is connected to the convection line, and thus create optimal conditions for nitrogen oxide reduction and carbon monoxide afterburning, with minimal oxygen content in flue gas and minimum amount of reagent entering the chimney
- Figure 1 shows the block diagram of the system for the realization of the method where: 4 - is the furnace chamber, 5 - is the front process gas/reagent collector, 6 - is the front process gas injection lance, 7 - is the front reagent injection lance/nozzle, 8 - is the convection part of the boiler, 9 - is the rear process gas collector, 10 - is the rear process gas injection lance, 11 - is the upper process gas/reagent collector, 12 - is the upper process gas injection lance, 13 - is the upper reagent injection lance, 15 - is the side process gas/reagent collector, 16 - is the side process gas injection lance, 17 - is the side reagent injection lance, 18 - is the process gas intake, 19 - is the control and shut-off component of the process gas feeder - air system, 20 - is the control and shut-off component of the process gas feeder - flue gas system, 21 - is the process gas fan, 22 - is the measuring system installed on the process gas collector, 23
- Figure 2 shows in a schematic and illustrative manner the place of installation of process gas and reagent injection lances, as well as the flow lines and swirl directions which occur during combustion in the furnace chamber of the equipment, preferably a grate boiler, where: 1 - is the sub-grate box of air, 2 - is the layer of fuel moving on the grate, 3 - is the grate, 4 - is the furnace chamber, 5 - is the front process gas/reagent collector, 6 - is the front process gas injection lance, 7 - is the front reagent injection lance/nozzle, 8 - is the convection part of the boiler, 9 - is the rear process gas collector, 10 - is the rear process gas injection lance, 11 - is the top process gas/reagent collector, 12 - is the top process gas injection lance, 13 - is the top injection lance of the reagent, 14 - is the temperature sensor, 15 - is the side collector of the process gas/reagent, 16 - is the side injection lance
- FIG. 2 The example embodiment according to the method will be illustrated by Fig. 2 in which A is the primary air pumped by the blast air fan to the control valves and then to the sub-grate boxes 1, whose task is to dose the oxidant in a controlled way to fuel 2 moving on the grate 3.
- A is the primary air pumped by the blast air fan to the control valves and then to the sub-grate boxes 1, whose task is to dose the oxidant in a controlled way to fuel 2 moving on the grate 3.
- fuel is burned and the amount of oxidant supplied in the form of primary air A ranges from 0.7 to 1.3 of the amount of stoichiometric air needed for full and complete combustion of fuel 2, preferably less than 1.0, moving on grate 3 as defined by the standards for this type of equipment.
- process gas (PG) or process gas and reagent (PG+R) are injected through collector 5 mounted outside the chamber, up to 60% of the process gas supplied to the system, through a series of lances 6 and 7 made and installed in such a way that the direction of injection of process gas (PG) or process gas with reagent (PG+R ) is opposite to the main direction of flow through the furnace chamber 4 with a jet deviation of +/-15° in the plane parallel to the longitudinal symmetry plane of the furnace chamber, whereby part of the process gas (PG) or process gas with reagent (PG+R ) accounting for up to 20% of the total amount of the process gas or process gas and reagent fed through
- process gas (PG) accounting for up to 60% of the process gas supplied to the system through collector 9 built in the convection part of boiler 8 and through lances 10 mounted on the rear wall of the furnace chamber 4, at the level of the lower edge of the boiler festoon is injected in the direction of grate 3 at an angle of 45°, and this angle is measured between the centre line of the jet and the back wall of the furnace chamber and another portion of process gas (PG) or process gas and reagent (PG+R) accounting for up to 25% of the process gas supplied to the system, via collector 11 mounted outside the boiler furnace chamber and through lances 12 and 13 mounted on the upper wall of the boiler furnace chamber 4 is injected in the opposite direction to the main direction of the FG flow through furnace chamber 4, whereby injection from each of lances 12 and/or 13 is made from at least one point, with a jet deviation of up to +/- 60° in the plane parallel to the longitudinal symmetry plane of the furnace chamber; the remaining process gas (PG) or process gas and
- the injection rate of process gas (PG) or reagent (R) is from 30 to 180 m/s, preferably 135 m/s, and the process gas stream accounts for up to 20% of the air stream necessary for full and complete combustion of the fuel as defined by the standards for this type of equipment; due to high speed, significant mass of the process gas stream and the way it is fed into the furnace chamber, a strong internal recirculation of iFGR flue gas inside furnace chamber 4 and a strong main swirl (MS) are produced, and depending on the boiler capacity, one or two additional swirls, one called upper swirl (US) and the other called down swirl (DS); the swirls rotate in a plane parallel to the longitudinal symmetry plane of the furnace chamber.
- PG process gas
- R reagent
- Lance 6 and 7 are shaped similarly to letter "L" and are introduced through deflections made in the front wall of furnace chamber 4. Thanks to the way in which lance 6 and 7 are fixed, it possible to change their position in the plane parallel to the longitudinal plane of symmetry of the boiler by +/- 15°.
- the back lances 10 are mounted directly in the boiler festoon or are introduced through the deflections made in the back wall of furnace chamber 4.
- the top lances 12 and 13 are mounted on the ceiling of furnace chamber 4 and are introduced through deflections made in this wall and each of the lances has at least one injection point.
- such a method of feeding process gas PG and reagent R is conducive to creating favourable conditions for conducting the process of nitrogen oxide reduction with very high efficiency due to the fact that the reagent after injection into furnace chamber 4 mixes with the injected process gas and combustion products moving in the direction of the temperature rise, i.e.
- the reduction reaction takes place in a temperature range from 850°C to 1050°C and in the presence of nitrogen oxides; the excess unreacted reagent R is transported to an area of increasingly higher temperature where the unreacted reagent reacts with oxygen and forms nitrogen oxides, which then, together with the products of combustion, head up the furnace chamber in a direction consistent with the main natural draught in the furnace chamber, where they encounter an unreacted reagent and suitable temperature conditions for the occurrence of the reduction reaction; part of the still unreacted reagent and unreduced nitrogen compounds (NOx) just before leaving the furnace chamber is returned to the area with suitable conditions for the reduction reaction by a strong stream of recirculating exhaust gas produced by the process gas stream.
- NOx nitrogen compounds
- the feeding of process gas and reagent in a manner according to the invention creates a strong main reverse swirl parallel to the longitudinal plane of symmetry of the furnace chamber and, depending on the boiler output, additionally an upward or downward swirl, which rotate in the same plane as the main swirl but in opposite directions; as a result, the system is, in a broad spectrum of operation, a selfregulating system, thus protecting itself against the ingress of unreacted reagent into the exhaust gases and ashes; moreover, the system according to the invention is hardly sensitive to fluctuations in the amount of nitrogen oxides produced in the process of burning fuel on the grate.
- the process gas is injected into the furnace chamber in the opposite direction to the natural direction of the flue gas movement in the furnace chamber and at high rate, it returns towards the grate, i.e. into the high-temperature area, particles of unburned coal, which in the hitherto known solutions, are entrained from the layer of coal moving on the grate by the blast air supplied from the grate and, as coal, enter together with fly ashes into the dust extraction systems, significantly reducing the overall equipment efficiency.
- the presented method significantly reduces carbon content in fly ashes, which directly contributes to the increase in boiler efficiency, as well as reduction in the amount of fly ashes captured by flue gases leaving the boiler and the content of unreacted reagent in such ashes entering the dedusting systems, resulting in the extension of the service life of these units due to the reduction of erosion and corrosion of the equipment and in newly built units allows for the use of smaller first-stage dedusting systems, reducing the related costs.
- the invention may be used in all applications where emphasis is placed on high quality of the combustion process, low emissions, especially of nitrogen oxides and carbon monoxide, investment savings, energy savings, and reagent savings, i.e. operating costs.
- the method presented in the description is intended for use in heating boilers and power boilers, especially grate-type boilers.
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- Combustion & Propulsion (AREA)
- Regulation And Control Of Combustion (AREA)
Description
- The object of the invention is a method for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, especially grate boilers and a system for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, especially grate boilers, used to reduce the formation of nitrogen oxides and carbon monoxide and/or their reduction in the furnace chambers of heating boilers and power boilers, especially grate boilers, and a system for the application of this method.
- The methods described in patents
PL 196745 B1 WO 95/15463 - The methods described in patent
US 20160003473 A1 present solutions which consist in inserting into the combustion chamber one or more lances supplying air with the reagent through one or two side walls of the boiler. In these solutions, the lances are rigidly fixed directly in the boiler shell, which means there is no need to install drive systems to withdraw the lances or provide considerable space around the combustion chamber; however, periodic inspection and cleaning of the lances requires stopping the combustion process inside the boiler. When this method of installation is used, the length and diameter of the lances are also limited due to the stress to which they are subjected inside the boiler and the total weight of equipment. - The methods described in patents
US 2006/0118013 A1 andWO 2013/09566 A2 - The method described in patent
WO 2004/085922 A2 assumes the reduction of NOx emissions by using a method of primary reduction of toxic compounds by splitting the combustion air stream. In this solution, part of the air is supplied near the fuel feed as primary air and the remaining part of the air necessary for full and complete combustion of the fuel is supplied above the fuel feed point, in the higher parts of the combustion area, by means of nozzles located on the walls of the combustion chamber; the air stream supplied in this area forms a swirl parallel or close to a plane perpendicular to the vertical axis of the combustion chamber. - The method described in patent
CN101545630A assumes the reduction of NOx emissions by using a method of primary reduction of toxic compounds by recirculating flue gas to two areas of the boiler. In this solution, part of the flue gas is added to the primary air supplied under the boiler grate. The remaining part of the fuel gas is supplied to the boiler's combustion chamber through orifices located at a short distance above the grate in the side walls forming a horizontal swirl. - The methods described in patents
US 2013/291772 A1 andUS 2013/244190 A1 apply to systems for burning fuel in pulverised burners with enriched oxygen content. In this solution, the circulated flue gas is mixed with a gas with high oxygen content and then with the fuel in the pulverised fuel burner. This system is therefore limited to pulverised fuel boilers and is intended in particular for carbon dioxide removal (CDR) systems. - The method described in the patent application
P.423576 - The technical problem to be solved is how to eliminate the abovementioned drawbacks and limitations, while guaranteeing further reduction of NOx emissions, reduction of CO emissions, minimising or completely eliminating the reagent in flue gases and fly ashes, increasing the efficiency of the system and lowering operating costs.
- The essence of the invention which is a method for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, especially grate boilers consists in that process gas, being air, flue gas or combustion air mixture, in its full range, i.e. from 0 to 100% share, or in the next combination process gas and reagent, being a solution of ammonia water, or urea solution, preferably a solution of ammonia water with ammonia with a concentration up to 25%, are injected into the furnace chamber, with the injection from lances installed on the front wall of the furnace chamber taking place on one to three levels in the opposite direction to the main, natural direction of the flue gas flow through the furnace chamber, preferably from top to bottom, with a deviation of +/- 15°, the angle being measured between the centre line of the jet and the front wall of the furnace chamber, in a plane parallel to the longitudinal plane of symmetry of the furnace chamber, i.e. in the direction of the temperature rise in the furnace chamber, and part of the injected stream (up to 20%) fed by the lances installed on the front wall of the furnace chamber is injected perpendicularly to the front wall with a possible deviation of the stream +/- 15°, while the stream injected from the lances installed on the rear wall of the furnace chamber takes place towards the front wall at an angle of 30° to 60°, and this angle is measured between the stream centre line and the rear wall of the furnace chamber, in the plane parallel to the longitudinal symmetry plane of the furnace chamber, while the stream injected from the lance installed on the upper wall of the furnace chamber occurs on one to four levels and its direction is opposite to the main direction of the flow of products/semi-finished products of the combustion process, flowing through the furnace chamber of the device, i.e. from top to bottom, in the direction of the boiler grate, with a deviation of the jet of +/-60°, the angle being measured between the centre line of the jet and the symmetry axis of the injection lance, which is perpendicular to the grate deck, in a plane parallel to the longitudinal symmetry plane of the furnace chamber, and this deviation, as well as the number of injection points, varies according to the boiler load, while the injection from the lances mounted on the side walls of the furnace chamber occurs on one to three levels, and the direction of injection is perpendicular to the side walls, i.e. it is perpendicular to the main direction of flow of products/semi-finished products of the combustion process, flowing through the furnace chamber of the device, with a possibility of deflecting the jet by an angle of +/-20°, which means that it goes inside the down swirl, while process gas is supplied to the furnace chamber at a speed of 30 to 180 m/s, preferably 135 m/s, in the amount of up to 20% of stoichiometric air demand necessary to burn the fuel supplied to the boiler, preferably 15%, with up to 60% of the process gas being injected via lances built into the front wall of the furnace chamber, with up to 60% of the process gas being injected through lances installed on the rear wall of the furnace chamber, up to 25% of the process gas is injected through lances installed on the upper wall of the furnace chamber and up to 15% of the process gas is injected through lances installed on the side walls of the furnace chamber; moreover, the reagent is delivered to the furnace chamber at a rate of 30 to 180 m/s, preferably 135 m/s, where the process gas injection points are located on the front wall of the furnace chamber, and/or on the upper wall of the furnace chamber and/or on the side walls of the furnace chamber, and/or on the rear wall of the furnace chamber, while the reagent and process gas injection points are located on the front wall of the furnace chamber, and/or on the side walls of the furnace chamber, and/or on the upper wall of the furnace chamber and the number of reagent injection points may be equal to or different from the number of process gas injection points; in the case of injection from the front wall of the furnace chamber, the injection points being up to 0.5 depth of the furnace chamber from the axis of the front wall pipes, preferably 0.1 and at a height from 0.2 to 0.8 of the furnace chamber above the grate deck, preferably 0.5; in the case of injection from the upper wall of the furnace chamber, the injection points are at a distance of 0.05 to 0.3 of the furnace chamber depth from the pipe axis of the rear wall of the furnace chamber, preferably 0.15, and at a height of 0.5 to 1.5 of the height of the festoon from the pipe axis of the upper wall, preferably 0.9 of the festoon height, while when injecting from the side walls of the furnace chamber, the injection points are located at a distance of 0.05 to 0.5 of the furnace chamber depth from the axis of the tubes of the rear wall of the furnace chamber and are located on one to three levels, preferably on three levels, with each level located at equal or different distances from the rear wall of the furnace chambers, preferably, the lowest level in the furnace chamber being located farthest from the wall of the rear furnace chamber and the lances are located at a height of 0.1 to 0.7 of the furnace chamber height above the grate deck, and when injected from the rear wall of the furnace chamber, the injection points are located at the bottom edge of the boiler festoon, i.e. at the height of the end of the sheet piling wall of the rear wall of the furnace chamber with a possible shift in both directions up to 0.6 of the festoon height, preferably, at the height of the bottom edge of the festoon, in one of the combinations in the upper part of the furnace chamber there is a set of temperature sensors, depending on the configuration of the system, which depends on the range of changes in boiler output. The amount of process gas or process gas and reagent injected into the furnace chamber can be changed within a full range of regulation, i.e. from 0 to 100%, for particular injection point groups or injection points, by the control unit based on the predefined control diagram i.e. depending on the boiler load as well as on the measured values: temperature and the share of O2, CO or NOx in the flue gas, such parameters being monitored by measuring devices mounted inside the furnace chamber in the form of temperature sensors and/or devices mounted outside the furnace chamber being the flue gas analyser, and the regulation is carried out by means of actuators individually for each injection point or group of injection points mounted on a given wall of the furnace chamber, on a given level or with a specific injection direction.
- Due to this solution, in the presented invention according to the method, the dynamic effect of the process gas stream was used to intensify the mixing process in the furnace chamber by inducing strong internal flue gas recirculation inside the furnace chamber and a strong swirl whose direction is opposite to the main, natural flue gas flow direction and the swirl plane is parallel to the longitudinal symmetry plane of the furnace chamber. This solution results in the equalisation of the temperature profile in the furnace chamber, which equalizes the thermal load of the chamber, which in turn leads directly to an increase in the efficiency and service life of the equipment; the solution according to the method allows for precise control of the temperature in the furnace chamber in the area where nitrogen oxides are reduced and CO is burned, reducing the concentration of the reagent in the furnace chamber, which minimises the risk of corrosion of the equipment components; moreover, the invention according to one of the embodiments, increases the capacity of the system by placing the lances on several levels of the furnace chamber, especially in the case of a considerable variability of the boiler load and this is usually used in units with higher power output. The invention according to the method also reduces reagent consumption in relation to known methods and thus allows to minimize the content of unreacted reagent in fly ashes and flue gases, which plays a very important role in terms of system operating costs, environmental protection and ash management. The opposite direction of reagent injection in relation to the main, natural direction of flue gas flow and to the inside of the generated swirls, as well as the described points and directions of injection, have a very important advantage in relation to the traditional directions and places of reagent injection cited in the state of the art investigation, because in the described method according to the invention, there is no such phenomenon (or if it occurs it is limited to a minimum) as entrainment of unreacted reagent particles, directly after it has been injected into the furnace chamber by the flue gases into the convection part of the boiler, i.e. the place where there are no conditions (no appropriate temperature window range), for the reduction reaction to occur, and further on into the flue gas treatment and discharge systems; another advantage of the method according to the invention resulting from the opposite direction of the reagent feeding in relation to the flue gas flow direction and the inner direction of the generated swirl is, in comparison with the known methods, much longer time from the injection of the reagent into the furnace chamber into the area of relatively low temperature until the occurrence of a reduction reaction, in which the reagent mixes with the process gas and combustion products moving in the direction of the temperature rise, i.e. towards the combustion area, where the reduction reaction takes place in the temperature range from 850°C to 1050°C and in the presence of nitrogen compounds; further on, the unreacted particles of the reagent enter the temperature area above 1 050°C where they bind with oxygen and form NOx-type compounds, which then, together with the products of combustion, head up the furnace chamber in accordance with the main natural draught of the combustion chamber where they encounter the unreacted reagent and the temperature conditions required for the occurrence of the NOX reduction reaction; part of the still unreacted reagent and unreacted nitrogen compounds (NOX) are returned to an area convenient for the NOX reduction reaction, through strong swirls of recirculating flue gas produced by the process gas stream. This natural and spontaneous course of the process contributes to the efficiency of the reduction process and to a large extent protects the system against the ingress of unreacted reagent into the ash, dust or flue gas treatment and discharge systems; another advantage of the method according to the invention is that the process gas is injected into the furnace chamber in the opposite direction to the natural direction of the flue gas movement in the furnace chamber and at a high rate turns back towards the grate i.e. into the high temperature area, particles of unburned coal, which in the hitherto known solutions are entrained from the layer of coal moving on the grate by the blast air supplied from the grate and, as coal, together with fly ashes enter the dust extraction systems significantly reducing their efficiency. The presented method according to the invention, significantly reduces the content of the carbon element in fly ash, which directly contributes to the increase in the efficiency of the system and also reduces the amount of fly ash carried by the flue gases leaving the boiler and entering the dedusting systems, which extends the service life of the devices and in newly built units enables the use of smaller first-stage dedusting systems reducing the equipment cost. This effect is particularly noticeable when burning poorer quality coal containing a lot of coal fines.
- The presented method of feeding the process gas or process gas and reagent produces a strong, main, reverse internal recirculation swirl and, depending on the boiler capacity, one to two additional swirls, one called the upper swirl, which is formed in the area bounded by the front wall, the upper and the stream of process gas injected from the lances mounted on the rear wall of the furnace chamber, this swirl being particularly noticeable at medium and high boiler loads, and a second one, called the down swirl, which is formed in the area bounded by the rear wall, the grate deck and the flue gas stream moving from the front zones of the grate towards the rear wall and further on towards the festoon, this swirl being particularly noticeable at low boiler loads; the main swirl and the upper swirl generated at medium and high boiler loads suck in flue gases from the main flue gas stream, from the area just before the furnace chamber is connected to the convection line, and thus create optimal conditions for nitrogen oxide reduction and carbon monoxide afterburning, with minimal oxygen content in flue gas and minimum amount of reagent entering the chimney; this limiting effect is due to the fact that the opposite direction of reagent injection consistent with the direction of temperature increase in the furnace chamber and strong internal recirculation ensure sufficient time to mix the reagent with process gas and flue gas, resulting in a homogeneous mixture, thus reducing the time needed for the NOX reduction reaction, which occurs after the mixture enters the area with a temperature between 850°C and 1050°C; subsequently, the excess unreacted reagent enters the area where the temperature is above 1050°C where it combines with oxygen to form NOX compounds, which are then transported with the main flue gas stream to a lowertemperature area of the furnace chamber, where the reagent is again encountered and reduction takes place; part of the flue gas just before the connection of the furnace chamber with the boiler's convection line is returned again as a result of strong recirculation swirls and reaches subsequent zones; a similar mechanism is produced by a down swirl, which is visible at low boiler loads, except that the flue gases from the main flue gas stream are sucked in from the lower parts of the boiler and not, as before, from the festoon area and are returned towards the grate deck, which in the case of low boiler loads ensures that a suitable temperature range for NOx reduction reaction is maintained; this self-looping process ensures low NOx emissions from the system and low reagent consumption, low CO emissions with low oxygen content in the flue gas, low content of carbon and unreacted reagent in the fly ash, as well as reduced amount of fly ash carried by the flue gas leaving the boiler.
- The invention in an exemplary but not restrictive embodiment is shown in the following drawings:
- Fig. 1
- - Block diagram of the system to execute the method,
- Fig. 2
- - A diagram of the boiler showing the location of the lances injecting process gas and reagent into the furnace chamber with marked directions of flue gas, process gas and reagent flows and the resulting reverse swirl and internal recirculation of flue gas.
-
Figure 1 shows the block diagram of the system for the realization of the method where: 4 - is the furnace chamber, 5 - is the front process gas/reagent collector, 6 - is the front process gas injection lance, 7 - is the front reagent injection lance/nozzle, 8 - is the convection part of the boiler, 9 - is the rear process gas collector, 10 - is the rear process gas injection lance, 11 - is the upper process gas/reagent collector, 12 - is the upper process gas injection lance, 13 - is the upper reagent injection lance, 15 - is the side process gas/reagent collector, 16 - is the side process gas injection lance, 17 - is the side reagent injection lance, 18 - is the process gas intake, 19 - is the control and shut-off component of the process gas feeder - air system, 20 - is the control and shut-off component of the process gas feeder - flue gas system, 21 - is the process gas fan, 22 - is the measuring system installed on the process gas collector, 23 - is the control and shut-off component of the process gas system, 24 - is the reagent tank, 25 - is the reagent pump, 26 - is the measuring system built on the reagent installation, 27 - is the control and cut-off components mounted on the reagent installation, 28 - is the lance for the central injection of the reagent into the process gas, 29 - is the device measuring the flue gas composition, 30 - is the controller. -
Figure 2 shows in a schematic and illustrative manner the place of installation of process gas and reagent injection lances, as well as the flow lines and swirl directions which occur during combustion in the furnace chamber of the equipment, preferably a grate boiler, where: 1 - is the sub-grate box of air, 2 - is the layer of fuel moving on the grate, 3 - is the grate, 4 - is the furnace chamber, 5 - is the front process gas/reagent collector, 6 - is the front process gas injection lance, 7 - is the front reagent injection lance/nozzle, 8 - is the convection part of the boiler, 9 - is the rear process gas collector, 10 - is the rear process gas injection lance, 11 - is the top process gas/reagent collector, 12 - is the top process gas injection lance, 13 - is the top injection lance of the reagent, 14 - is the temperature sensor, 15 - is the side collector of the process gas/reagent, 16 - is the side injection lance of the process gas, 17 - is the side injection lance of the reagent, A - is the blast air stream (primary), PG - is process gas stream, PG+R - is process gas and reagent stream, FG - is flue gas stream, iFGR - is internal flue gas recirculation, MS - is main swirl, DS - is down swirl and US - is upper swirl. - The example embodiment according to the method will be illustrated by
Fig. 2 in which A is the primary air pumped by the blast air fan to the control valves and then to thesub-grate boxes 1, whose task is to dose the oxidant in a controlled way to fuel 2 moving on the grate 3. On and directly above grate 3, fuel is burned and the amount of oxidant supplied in the form of primary air A ranges from 0.7 to 1.3 of the amount of stoichiometric air needed for full and complete combustion of fuel 2, preferably less than 1.0, moving on grate 3 as defined by the standards for this type of equipment. The products and semi-finished products of FG combustion, move towards the top offurnace chamber 4, part of which goes near the rear wall offurnace chamber 4, which is a phenomenon normally found in furnace chambers of boilers of this kind. At a distance of 0.05 of the depth offurnace chamber 4, at the height of 0.5 of the height of the boiler's furnace chamber, on the front wall offurnace chamber 4, process gas (PG) or process gas and reagent (PG+R) are injected through collector 5 mounted outside the chamber, up to 60% of the process gas supplied to the system, through a series of lances 6 and 7 made and installed in such a way that the direction of injection of process gas (PG) or process gas with reagent (PG+R ) is opposite to the main direction of flow through thefurnace chamber 4 with a jet deviation of +/-15° in the plane parallel to the longitudinal symmetry plane of the furnace chamber, whereby part of the process gas (PG) or process gas with reagent (PG+R ) accounting for up to 20% of the total amount of the process gas or process gas and reagent fed through lances 6 and 7 installed on the front wall offurnace chamber 4, is injected in a direction perpendicular to the front wall with a possible deviation of the jet of +/- 15°, i.e. towards the centre of the emerging swirl, while another portion of process gas (PG) accounting for up to 60% of the process gas supplied to the system through collector 9 built in the convection part ofboiler 8 and throughlances 10 mounted on the rear wall of thefurnace chamber 4, at the level of the lower edge of the boiler festoon is injected in the direction of grate 3 at an angle of 45°, and this angle is measured between the centre line of the jet and the back wall of the furnace chamber and another portion of process gas (PG) or process gas and reagent (PG+R) accounting for up to 25% of the process gas supplied to the system, viacollector 11 mounted outside the boiler furnace chamber and throughlances boiler furnace chamber 4 is injected in the opposite direction to the main direction of the FG flow throughfurnace chamber 4, whereby injection from each oflances 12 and/or 13 is made from at least one point, with a jet deviation of up to +/- 60° in the plane parallel to the longitudinal symmetry plane of the furnace chamber; the remaining process gas (PG) or process gas and reagent (PG+R) is injected throughcollector 15 mounted outside the boiler, throughlances furnace chamber 4 of the boiler, in a direction perpendicular to these walls with a jet deviation of +/-20° at least on one level. The injection rate of process gas (PG) or reagent (R) is from 30 to 180 m/s, preferably 135 m/s, and the process gas stream accounts for up to 20% of the air stream necessary for full and complete combustion of the fuel as defined by the standards for this type of equipment; due to high speed, significant mass of the process gas stream and the way it is fed into the furnace chamber, a strong internal recirculation of iFGR flue gas insidefurnace chamber 4 and a strong main swirl (MS) are produced, and depending on the boiler capacity, one or two additional swirls, one called upper swirl (US) and the other called down swirl (DS); the swirls rotate in a plane parallel to the longitudinal symmetry plane of the furnace chamber. Lance 6 and 7 are shaped similarly to letter "L" and are introduced through deflections made in the front wall offurnace chamber 4. Thanks to the way in which lance 6 and 7 are fixed, it possible to change their position in the plane parallel to the longitudinal plane of symmetry of the boiler by +/- 15°. Theback lances 10 are mounted directly in the boiler festoon or are introduced through the deflections made in the back wall offurnace chamber 4. Thetop lances furnace chamber 4 and are introduced through deflections made in this wall and each of the lances has at least one injection point. In accordance with the patented method according to the invention, such a method of feeding process gas PG and reagent R is conducive to creating favourable conditions for conducting the process of nitrogen oxide reduction with very high efficiency due to the fact that the reagent after injection intofurnace chamber 4 mixes with the injected process gas and combustion products moving in the direction of the temperature rise, i.e. towards the combustion area, where the reduction reaction takes place in a temperature range from 850°C to 1050°C and in the presence of nitrogen oxides; the excess unreacted reagent R is transported to an area of increasingly higher temperature where the unreacted reagent reacts with oxygen and forms nitrogen oxides, which then, together with the products of combustion, head up the furnace chamber in a direction consistent with the main natural draught in the furnace chamber, where they encounter an unreacted reagent and suitable temperature conditions for the occurrence of the reduction reaction; part of the still unreacted reagent and unreduced nitrogen compounds (NOx) just before leaving the furnace chamber is returned to the area with suitable conditions for the reduction reaction by a strong stream of recirculating exhaust gas produced by the process gas stream. The feeding of process gas and reagent in a manner according to the invention creates a strong main reverse swirl parallel to the longitudinal plane of symmetry of the furnace chamber and, depending on the boiler output, additionally an upward or downward swirl, which rotate in the same plane as the main swirl but in opposite directions; as a result, the system is, in a broad spectrum of operation, a selfregulating system, thus protecting itself against the ingress of unreacted reagent into the exhaust gases and ashes; moreover, the system according to the invention is hardly sensitive to fluctuations in the amount of nitrogen oxides produced in the process of burning fuel on the grate. In addition, due to the fact that the process gas is injected into the furnace chamber in the opposite direction to the natural direction of the flue gas movement in the furnace chamber and at high rate, it returns towards the grate, i.e. into the high-temperature area, particles of unburned coal, which in the hitherto known solutions, are entrained from the layer of coal moving on the grate by the blast air supplied from the grate and, as coal, enter together with fly ashes into the dust extraction systems, significantly reducing the overall equipment efficiency. The presented method, according to the invention, significantly reduces carbon content in fly ashes, which directly contributes to the increase in boiler efficiency, as well as reduction in the amount of fly ashes captured by flue gases leaving the boiler and the content of unreacted reagent in such ashes entering the dedusting systems, resulting in the extension of the service life of these units due to the reduction of erosion and corrosion of the equipment and in newly built units allows for the use of smaller first-stage dedusting systems, reducing the related costs. - The invention may be used in all applications where emphasis is placed on high quality of the combustion process, low emissions, especially of nitrogen oxides and carbon monoxide, investment savings, energy savings, and reagent savings, i.e. operating costs. The method presented in the description is intended for use in heating boilers and power boilers, especially grate-type boilers.
- The following benefits have been achieved thanks to the invention:
- minimisation of investment costs,
- minimisation of operating costs,
- substantial simplification of the installation,
- minimisation of the space needed to install the system,
- reliability of operation,
- reduction of NOX emissions,
- reduction of carbon monoxide (CO) emissions,
- reduction of the carbon content in fly ashes,
- reduction of fly ash content in flue gases,
- increase in the efficiency of the equipment, compared to the known methods, by reducing the O2 and CO content in flue gas and carbon content in fly ashes,
- increase in the efficiency of the system by replacing the injection of water into the furnace chamber to distribute the reagent across the chamber or to atomise the reagent , by using process gas or compressed air, respectively,
- reduction of the unreacted reagent content in flue gas and ashes compared to known methods,
- increase the service life of the equipment by reducing the concentration of the reagent in the furnace chamber, especially at the walls of the furnace chamber, and by equalizing the temperature profile across the furnace chamber,
- increase in the thermal efficiency of the furnace chamber by increasing the average heat flow returned to the walls of the furnace chamber.
Claims (2)
- A method for the reduction of nitrogen oxides and carbon monoxide in the furnace chambers (4) of water and steam boilers, especially grate boilers, wherein a process gas being air, flue gas or or a mixture thereof, optionally mixed with a reagent is injected into the furnace chamber (4) through process gas injection lances (6) installed on the front wall of the furnace chamber (4) on one to three levels in the opposite direction to the main, natural direction of the flue gas flow through the furnace chamber, preferably from top to bottom, with a deviation of +/- 15°, the angle being measured between the centre line of the jet and the front wall of the furnace chamber, in a plane parallel to the longitudinal plane of symmetry of the furnace chamber, i.e. in the direction of the temperature rise in the furnace chamber, wherein part of the-stream, up to 20%, injected by the process gas injection lances (6) installed on the front wall of the furnace chamber (4) is injected perpendicularly to the front wall with a deviation of +/- 15°, wherein process gas injection-from process gas injection lances (10) installed on the rear wall of the furnace chamber (4) takes place towards the front wall at an angle of 30° to 60°, and this angle is measured between the stream centre line and the rear wall of the furnace chamber, in the plane parallel to the longitudinal symmetry plane of the furnace chamber, wherein process gas injection from process gas injection lances (12) installed on the upper wall of the furnace chamber (4) occurs on one to four levels and its direction is opposite to the main direction of the flue gas flow in the furnace chamber (4) with a deviation of the jet of +/-60°, the angle being measured between the centre line of the jet and the symmetry axis of the injection lance, which is perpendicular to the grate deck, in a plane parallel to the longitudinal symmetry plane of the furnace chamber, and this deviation, as well as the number of injection points, varies according to the boiler load; wherein process gas injection from process gas injection lances (16) installed on the side walls of the furnace chamber (4) occurs on one to three levels, and the direction of injection is perpendicular to the side walls, i.e. it is perpendicular to the main direction of flue gas flow in the furnace chamber, with a deviation of +/-20°, which means that it goes inside a down swirl; wherein process gas is supplied to the furnace chamber (4) at a speed of 30 to 180 m/s, preferably 135 m/s, in the amount of up to 20% of stoichiometric air demand necessary to burn the fuel supplied to the boiler, preferably 15%, with up to 60% of the process gas being injected through the process gas injection lances (6) installed on the front wall of the furnace chamber (4), with up to 60% of the process gas being injected through the process gas injection lances (10) installed on the rear wall of the furnace chamber (4), with up to 25% of the process gas is injected through the process gas injection lances (12) installed on the upper wall of the furnace chamber (4) and with up to 15% of the process gas is injected through the process gas injection lances (16) installed on the side wall of the furnace chamber (4); wherein reagent is injected to the furnace chamber (4) at a rate of 30 to 180 m/s, preferably 135 m/s, wherein the reagent is injected through injection points located on the front wall of the furnace chamber (4), on the upper wall of the furnace chamber and on the side walls of the furnace chamber, wherein the number of reagent injection points may be equal to or different from the number of process gas injection points; wherein the injection points on the front wall of the furnace chamber (4), are up to 0.5 depth of the furnace chamber from the axis of the front wall tubes, preferably 0.1 and at a height from 0.2 to 0.8 of the furnace chamber above the grate deck, preferably 0.5; wherein the injection points on the upper wall of the furnace chamber (4) are at a distance of 0.05 to 0.3 of the furnace chamber depth from the tube axis of the rear wall, preferably 0.15, and at a height of 0.5 to 1.5 of the height of the festoon from the tube axis of the upper wall, preferably 0.9 of the festoon height, wherein the injection points on the side walls of the furnace chamber (4) are located at a distance of 0.05 to 0.5 of the furnace chamber depth from the axis of the tubes of the rear wall and are located on one to three levels, preferably on three levels, with each level located at equal or different distances from the rear wall, preferably, the lowest level in the furnace chamber being located farthest from the rear wall and the injection points are located at a height of 0.1 to 0.7 of the furnace chamber height above the grate deck, and wherein the injection points on the rear wall of the furnace chamber (4), are located at the bottom edge of the boiler festoon, i.e. at the height of the end of the rear wall with a possible shift in both directions up to 0.6 of the festoon height.
- The method according to claim 1, wherein the amount of process gas or process gas and reagent injected into the furnace chamber, is changed within a full range of regulation, i.e. from 0 to 100%, for particular injection point groups or injection points, by a control unit based on a predefined control diagram i.e. depending on the boiler load as well as on the measured values: temperature and the share of O2, CO or NOx in the flue gas, such parameters being monitored by measuring devices mounted inside the furnace chamber in the form of temperature sensors and/or devices mounted outside the furnace chamber being the flue gas analyser, and the regulation is carried out by means of actuators individually for each injection point or group of injection points mounted on a given wall of the furnace chamber, on a given level or with a specific injection direction.
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PL429343A PL429343A1 (en) | 2019-03-21 | 2019-03-21 | Method of reducing nitrogen oxides and carbon monoxide in the furnace chambers of water and steam boilers, in particular grate boilers, and a system for reducing nitrogen oxides and carbon monoxide in the furnace chambers of water boilers and steam boilers, in particular grate boilers |
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US5809910A (en) * | 1992-05-18 | 1998-09-22 | Svendssen; Allan | Reduction and admixture method in incineration unit for reduction of contaminants |
SE502283C2 (en) | 1993-12-03 | 1995-09-25 | Ulf Hagstroem | Methods and supply means for regulating mixing conditions in a combustion or gasification plant |
SE515645C2 (en) | 2000-01-14 | 2001-09-17 | Ecomb Ab | Camera-supplied supply fluid for a combustion chamber |
US20040185401A1 (en) | 2003-03-19 | 2004-09-23 | Goran Moberg | Mixing process for combustion furnaces |
US6988454B2 (en) | 2003-09-09 | 2006-01-24 | Advanced Combustion Technology | Method and apparatus for adding reducing agent to secondary overfire air stream |
CN101545630B (en) * | 2009-04-30 | 2012-11-28 | 宁波怡诺能源科技有限公司 | Coal fired boiler capable of controlling flue gas oxygen content |
JP5489254B2 (en) * | 2010-09-29 | 2014-05-14 | バブコック日立株式会社 | Oxyfuel combustion system and operating method thereof |
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US9120898B2 (en) | 2011-07-08 | 2015-09-01 | Baker Hughes Incorporated | Method of curing thermoplastic polymer for shape memory material |
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