WO2006084954A1 - A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler and an air distribution system of a bubbling fluidized bed boiler - Google Patents

A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler and an air distribution system of a bubbling fluidized bed boiler Download PDF

Info

Publication number
WO2006084954A1
WO2006084954A1 PCT/FI2006/050056 FI2006050056W WO2006084954A1 WO 2006084954 A1 WO2006084954 A1 WO 2006084954A1 FI 2006050056 W FI2006050056 W FI 2006050056W WO 2006084954 A1 WO2006084954 A1 WO 2006084954A1
Authority
WO
WIPO (PCT)
Prior art keywords
air
fluidized bed
fuel
supplied
furnace
Prior art date
Application number
PCT/FI2006/050056
Other languages
French (fr)
Inventor
Pauli Dernjatin
Marko Fabritius
Jukka RÖPPÄNEN
Original Assignee
Metso Power Oy
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Metso Power Oy filed Critical Metso Power Oy
Priority to US11/883,887 priority Critical patent/US20080149012A1/en
Priority to CA2597159A priority patent/CA2597159C/en
Priority to EP06708960.7A priority patent/EP1846694B1/en
Publication of WO2006084954A1 publication Critical patent/WO2006084954A1/en

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C10/00Fluidised bed combustion apparatus
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/30Incineration of waste; Incinerator constructions; Details, accessories or control therefor having a fluidised bed
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/10Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of field or garden waste or biomasses
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23CMETHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN  A CARRIER GAS OR AIR 
    • F23C2201/00Staged combustion
    • F23C2201/10Furnace staging
    • F23C2201/101Furnace staging in vertical direction, e.g. alternating lean and rich zones

Definitions

  • the invention relates to a method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler burning biofuel according to the preamble of the appended claim 1.
  • the invention also relates to an air distribution system of a biofuel-burning bubbling fluidized bed boiler in accordance with the preamble of the appended claim 13.
  • biofuel refers to solid fuels, wherein the portion of volatile matter in ash-free dry solids is over 60%.
  • This type of fuels are, for example, peat, bark, wood chips, sawdust, waste construction timber, sludge created in process industry, and municipal solid waste.
  • Bubbling fluidized bed boilers are generally used in energy production, wherein the fuels include biofuels, such as, for example, peat and wood chips.
  • the fuels include biofuels, such as, for example, peat and wood chips.
  • a fluidized bed which is composed of a fine, incombustible material, typically sand, which fluidizes over a grate forming the bottom of the boiler.
  • the fluidizing of the material is created by feeding fluidizing gas through the grate to the fluidized bed.
  • the fluidizing gas can be composed solely of air, so-called primary air, or it may be a gas mixture formed by primary air and inert gas, for example, flue gas.
  • a bubbling fluidized bed boiler the flow rate of the fluidizing gas supplied through the grate is set into such that the particles forming the fluidized bed do not escape with air to the upper part of the boiler, but they remain in the lower part of the furnace forming a fluidized bed that is continuously moving and efficiently mixes the fluidized bed material and the fuel supplied to it.
  • the combustion air needed for burning fuel is generally supplied stagewise and in several portions to the furnace of the boiler in such a manner that a part of combustion air, i.e. fluidizing air, is formed by the primary air blown through the grate with the fluidizing gas a part is formed by secondary air supplied above the fluidized bed, and the rest of the combustion air is supplied to the upper part of the furnace of the boiler as so-called tertiary air.
  • the boiler can also be divided into different air zones according to the air supplied to the boiler: the area between the fluidized bed and the secondary air supply is called the primary air zone, and the area between the secondary air supply and the tertiary air supply is called the secondary
  • Fuel is fed by means of so-called carrier air to the bubbling fluidized bed boiler on the fluidized bed.
  • the drying of fuel particles i.e. pyrolysis
  • the combustion of the remaining carbon residue i.e. pyrolysis
  • Drying and pyrolysis are very fast compared to the total combustion time of fuel particles.
  • the volatile matter released in pyrolysis are mainly methane, CH 4 and carbon monoxide CO, as well as nitrogen oxide emissions causing ammonia NH 3 and hydrogen cyanide HCN.
  • the volatile matter rises upwards and burns when reaching an oxygenous area.
  • a boiler equipped with staged air the combustion of volatile matter primarily is done by secondary air and partly tertiary air, and the combustion of the carbon residue of fuel particle is done by fluidizing, secondary and tertiary air.
  • staged air supply By means of the staged air supply it is possible to reduce the formation of nitrogen oxides. That is, when there is oxygen, NH 3 and HCN react into nitrogen monoxide NO.
  • staging the air supply reducing, substoichiometric areas are formed in the furnace of the bubbling fluidized bed boiler. In these areas the NH 3 and HCN formed of fuel are reduced to molecular nitrogen in accordance with the following reaction equations 1 and 2:
  • reaction equation 3 wherein the hydrocarbon radical is -CHi.
  • the reducing areas are formed by adjusting the amount of fluidizing and secondary air.
  • the furnace is maintained substoichiometric in relation to oxygen until the tertiary air supply, in which case the delay time needed for reactions (1) and (2) is maximized and the amount of NH 3 and HCN is minimized before the tertiary air level.
  • the optimum total air coefficient before the tertiary air supply in relation to NO x emissions is slightly below 1 depending on the combustion temperature.
  • the air required for the burning out of volatile matter and carbon residue is supplied to the furnace as tertiary air.
  • the residue NH 3 and HCN in the flue gases are oxidized after the tertiary air zone into nitrogen oxides.
  • the nitrogen oxide emissions can be reduced approximately 30% in comparison to a non-staged air supply. Still problematic are the fine and light fuels, because most of the fuel particles do not end up in the fluidized bed, but they are pulled with the fluidizing gas and secondary air to the upper parts of the furnace. Thus, it is almost impossible for the fuels to create fuel combustion conditions in the furnace that are controlled and favourable to reducing nitrogen oxides.
  • Publication WO 02/090829 also discloses a nitrogen oxide reduction method based on the staging of combustion air.
  • recirculation gas composed of flue gases is supplied between the supply points of secondary and tertiary airs, in the elevation of the bubbling fluidized bed boiler.
  • the nitrogen oxides contained by the recirculation gas take part in the final stage of the above-presented reduction reactions (1) and (2) and intensify the reaction of nitrogen compounds formed of the fuel into molecular nitrogen.
  • the problem with this solution is that it causes the amount of flue gases in the boiler to increase, in which case the size of the furnace must be increased, which in turn raises the price of the boiler.
  • the method is suitable mainly for dry fuels. With wet fuels the amount of heat needed for drying reduces the combustion temperature in the secondary stage too much, thus preventing the creation of conditions favourable for reducing the nitrogen oxides.
  • the purpose of the present invention is to provide a method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler burning biofuel, by means of which the above-mentioned drawbacks can be avoided.
  • the purpose of the invention is to create an air distribution system of a bubbling fluidized bed boiler.
  • the method according to the invention is primarily characterized in what will be presented in the characterizing part of the independent claim 1.
  • the air distribution system of a bubbling fluidized bed boiler according to the invention is primarily characterized in what will be presented in the characterizing part of the independent claim 13.
  • the invention is based on the idea that the nitrogen oxide emissions of a bubbling fluidized bed boiler are reduced by using a staged air supply in such a manner that a part of primary air is supplied in connection with fuel supply, i.e. with the fuel or within the immediate vicinity of the fuel supply point in the same direction as the fuel itself.
  • This part of primary air is in this application referred to as the combustion air of volatile matter.
  • the pyrolysis following the drying and the combustion of the volatile matter released from the fuel in the pyrolysis also takes place almost immediately after the fuel has mixed with the fluidized bed, because the fuel and the oxygen in the air supplied in connection with it are mixed quickly. Due to the quick mixing of the fuel and the oxygen, most of the volatile matter released from the fuel can be burnt in the upper part of the fluidized bed and on the fluidized bed, before the supply of secondary air.
  • the combustion of volatile matter creates a high temperature, which maximizes the creation of hydrocarbon radicals formed of the fuel and promotes the reduction of the released nitrogen oxides.
  • the amount of combustion air of volatile matter supplied in connection with the fuel supply is adjusted into such that the combustion of volatile matter released in pyrolysis from the fuel being burnt takes place in substoichiometric conditions in relation to the volatile matter.
  • the air coefficient SR V in relation to the volatile matter is thus as high as possible, however, below 1 , advantageously between 0.75 to 0.97 and preferably between 0.90 to 0.95.
  • the total air coefficient SR tot on the same level of the furnace varies between 0.50 to 0.80, advantageously being 0.65.
  • Secondary air is supplied form the secondary air nozzles and tertiary air is supplied from the tertiary air nozzles placed above the secondary air nozzles.
  • the task of the fluidizing gas supplied to the furnace through its bottom is to maintain the fluidized bed bubbling and its temperature suitable.
  • the combustion air amounts supplied in different stages of the staged combustion are thus adjusted, i.e. the total air coefficient SR tot needed for combustion and further the air coefficient in relation to the volatile matter SR V .
  • This is illustrated later in tables 1 and 2 of this description. Feeding the fuel with air to the fluidized bed in such a manner that substantially all the fuel particles are forced there enables controlling the combustion substantially better than at present. Further, the amount of unburnt fuel can be minimized, because the delay time of fuel in the furnace is longer than in the solutions according to prior art.
  • the method according to the invention it is not the amount of air supplied to the furnace nor the total air coefficient that is affected, but how the air distribution is performed in order to have the air coefficient in relation to the volatile matter of the fuel as high as possible as low in the furnace as possible and yet as long as possible before the secondary air nozzles.
  • Fig. 1 shows schematically a furnace of a bubbling fluidized bed boiler in a side view
  • Fig. 2 shows schematically a furnace of a bubbling fluidized bed boiler in a front view
  • Fig. 3a shows fuel supply means seen from the inside of the furnace
  • Fig. 3b shows fuel supply means according to a second embodiment seen from the inside of the furnace
  • Fig. 3c shows fuel supply means according to a third embodiment seen from the inside of the furnace
  • Fig. 4 shows the amount of pyrolysis gas in a furnace
  • Fig. 5 shows temperature distribution in a furnace above the surface of the bed.
  • Fig. 1 shows a side view of a furnace of a bubbling fluidized bed boiler 1.
  • a fluidized bed 2 composed of bed material on the bottom of the furnace.
  • Fluidizing gas is supplied to the furnace 1 through nozzles 4 arranged on its bottom 3, which gas fluidizes the bed material.
  • the fluidizing gas can be solely air, or it may be a mixture of air and re- circulating gas.
  • the fuel is supplied to the fluidized bed 2 from fuel supply means 5 arranged above the surface of the fluidized bed and placed substantially on a mutually same level. In the figure there are three fuel feeding means, but their number may vary depending on the size of the furnace or other parameters of the boiler.
  • Fuel feeding means can also be arranged on the opposite side wall (not shown) of the furnace substantially on the same level with the fuel feeding means arranged on the side wall, as shown in the figure. They can also be placed on the front and/or back walls of the furnace.
  • the fuel is fed to the fluidized bed by means of air.
  • the amount of air used in connection with fuel feeding is so large, that it prevents fuel particles from escaping to the upper parts of the furnace by directing the fuel substantially on the surface of the fluidized bed.
  • the additional air, combustion air of the volatile matter supplied in connection with air supply is a part of primary air.
  • Secondary air is supplied from secondary air nozzles 6 located above the fuel feeding means to above the fluidized bed 2. Tertiary air is supplied to the furnace above the secondary air nozzles 6 via tertiary air nozzles 7 arranged in the upper part of the furnace.
  • the amount of air supplied to the furnace does not therefore increase in comparison to a conventional solution, but it is distributed in a different manner.
  • the amount of primary air supplied as fluidizing gas or as a part of it and the amount of tertiary air remain substantially equal to conventional staged combustion.
  • separate combustion air of volatile matter is supplied to the furnace, which air correspondingly decreases the amount of secondary air.
  • Fig. 2 shows a front view of a furnace 1 of a bubbling fluidized bed boiler.
  • Fuel is fed from a fuel supply means 5 to the fluidized bed 2.
  • Fuel feeding takes place by means of carrier air and the combustion air of volatile matter, in which case the fuel-air-mixture 8 is forced all the way to the surface 2a of the fluidized bed 2.
  • Finely divided fuel supplied to the fluidized bed dries immediately when coming into contact with hot bed material and pyrolizes substantially entirely.
  • the volatile matter released from the fuel burn on the surface 2a of the fluidized bed 2 and above the surface 2a of the fluidized bed by means of primary air forming a first, reducing primary air zone 9, which extends from the upper part of the fluidized bed to the secondary air nozzles 6.
  • the combustion of volatile matter takes place in the primary air zone 9 in substoichiometric conditions in relation to the air coefficient SR V of volatile matter.
  • the total air coefficient SR tot is naturally below 1.
  • the air coefficient SR V in relation to volatile matter is as large as possible, but still a little below 1 , the volatile matter burns quickly and forms a high local temperature, and it forms a maximum amount of hydrocarbon radicals, which are needed in order to reduce nitrogen oxides formed from the fuel.
  • the reducing secondary air zone 10 extends from the secondary air nozzles all the way to the tertiary air nozzles arranged over them.
  • Reducing the nitrogen oxides formed from fuel into molecular nitrogen is thus performed in two stages.
  • the first reducing stage i.e. in the primary air zone 9
  • most of the volatile matter released from the fuel and a part of the carbon residue is burnt. This takes place in relation to both the total air coefficient SR tot and the air coefficient SR V of the volatile matter of the fuel in substoichiometric conditions, which results in a large amount of hydrocarbon radicals.
  • the primary air required in this stage is brought to the furnace in connection with fuel supply and at least as a part of the fluidizing gas. 75 to 95%, preferably 90% of the air needed for combustion of pyrolysis gases is supplied as primary air.
  • the second reducing stage i.e.
  • combustion air is supplied to the furnace from secondary air nozzles 6 arranged within a distance from the surface of the fluidized bed in such a manner that the substoichiometric conditions remain, i.e. the total air coefficient SR tot is still below 1.
  • the air coefficient SR V of volatile matter of the fuel rises in this zone above 1. Feeding of primary air in the manner described above in two stages, as fluidizing air and as combustion air of volatile matter has the effect that the temperatures in the lower parts of the furnace are higher than in known boilers equipped with staged air distribution.
  • the fuel is inflamed quickly and most of the volatile matter can be burnt before the actual secondary air level.
  • FIG 2 there are three secondary and tertiary air nozzles 6 and 7 side by side on the front wall of the furnace. Their number and placement may vary depending on the size of the boiler. The air nozzles can also be placed on the side walls of the boiler.
  • the following tables 1 and 2 show two examples of applying the invention in a bubbling fluidized bed boiler, whose firing rate is 300 MW.
  • the examples show stagewise both the air distribution in a bubbling fluidized bed boiler according to prior art and the air distribution in the same boiler in accordance with the invention when the fuel and boiler load remain the same.
  • the air amount (kg/s) supplied to the boiler in each stage, the total air coefficient SR tot of the stage in question and the air coefficient in relation to the volatile matter SR V are shown.
  • the fuel is peat and in the example of table 2 the fuel is wood.
  • the percentage of the volatile matter of the dry fuel flow is approximately 70 mass-%, coke approximately 24.5 mass-% and ash approximately 5.5 mass-%.
  • the moisture content of the fuel is 46 mass-%.
  • the percentage of the volatile matter of the dry fuel flow is approximately 85 mass-%, coke approximately 13 mass-% and ash approximately 2 mass-%.
  • the moisture content of the fuel is 46 mass- %.
  • the new air distribution according to the invention has an effect on the amounts of additional air and secondary air supplied in connection with fuel supply.
  • the other, fluidizing air and tertiary air supplied together with the fluidizing gas, as well as the small air amounts used in cooling start-up burners and load carrying burners remain the same as in air distribution according to prior art.
  • the amount of air supplied together with the fuel is significantly larger than the amount of carrier air used for fuel supply in prior art.
  • the amount of air supplied with the fuel varies depending on the fuel, because different fuels contain different amounts of volatile matter and the purpose is to burn them in substoichiometric conditions before the supply of secondary air.
  • the additional air fed in connection with fuel supply i.e. the combustion air of volatile matter, which is a part of primary air
  • fuel supply i.e. the combustion air of volatile matter, which is a part of primary air
  • Figure 3a shows a fuel supply means 5, i.e. a fuel feeding opening 5a seen from the inside of the furnace, wherein the fuel and the combustion air supplied with it are mixed right before they are fed to the furnace together.
  • the feeding opening 5a is rectangular, which is the most advantageous form for a feeding opening, but otherwise shaped feeding openings may also be applied.
  • the fuel and combustion air are fed parallel to the furnace.
  • the fuel is fed to the furnace by means of carrier air from the fuel feeding opening 5a, which is on three sides surrounded by a uniform air channel 11 for supplying combustion air of volatile matter.
  • the air channel 11 is a uniform channel and it surrounds the fuel feeding opening from its three sides in such a manner that there is no air supply from below the feeding opening 5a.
  • the air channels 11a, 11b and 11c are separate air channels in relation to the fuel feeding opening 5a, which channels are placed within a small distance from the fuel feeding opening 5a, on its three sides.
  • the air channels 11a to 11c are also placed in such a manner that there is no air channel under the fuel feeding opening 5a.
  • the design of the air channel and the placement of the air channels 11a to 11c in relation to the fuel feeding opening help in directing the fuel particles to be directed to the fluidized bed.
  • FIGS. 4 and 5 The invention is illustrated in figures 4 and 5 by means of graphs, which are formed by modelling a bubbling fluidized bed boiler with a fuel power of 300 MW with a full load, wherein the fuel has been a mixture of peat (70%) and wood (30%).
  • Each graph shows two curves: curves for both the air distribution according to prior art and the air distribution according to the invention. These different air distributions are explained in connection with tables 1 and 2.
  • Figure 4 shows the portion of pyrolysis gas in a furnace above the surface of the bed, wherein the portion of pyrolysis gases formed as a result of air distribution according to prior art is illustrated by dashed lines and the portion of pyrolysis gases reached by means of the invention is illustrated with a solid line.
  • the graphs show that by means of the invention the releasing and combustion of pyrolysis gas mostly take place before the secondary air supply.
  • the releasing of pyrolysis gas significantly takes place before the secondary air level, but because of lack of oxygen hardly any combustion takes place. Because of the escaping fuel particles, the releasing of pyrolysis gases takes place even on secondary and tertiary air levels.
  • Figure 5 shows the temperature distribution above the bed of a furnace.
  • the temperature distribution according to prior art is shown by dashed lines and the temperature distributions reached by means of the invention are shown by a solid line. It can be seen from the graphs that by means of the invention the temperature of the furnace is higher in the primary air zone than in a bubbling fluidized bed boiler equipped with air distribution according to prior art. The temperature remains higher almost to the tertiary level, after which it decreases to lower than in prior art, because there is no more combustible matter left.

Abstract

A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler burning biofuel and an air distribution system for a bubbling fluidized bed boiler biofuel. A fluidized bed (2) is arranged in the lower part of a furnace (1) of the bubbling fluidized bed boiler, which is fluidized by means of fluidizing gas, which comprises at least primary air. Fuel is fed to the fluidized bed (2), which dries and pyrolizes into pyrolysis gas comprising volatile matter of fuel, which gas rises upwards in the furnace and burns there. Secondary air is supplied above the fluidized bed (2) from secondary air nozzles (6), and tertiary air is supplied above the secondary air nozzles (6). A part of primary air is supplied in connection with fuel feeding in such a manner that the fuel is forced substantially on the surface of the fluidized bed (2), thus pyrolizing entirely, and at least a part of the pyrolysis gases formed in the pyrolysis is burnt by means of primary air in such a manner that the air coefficient in relation to the volatile matter of fuel in the pyrolysis gases is in the substoichiometric area.

Description

A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler and an air distribution system of a bubbling fluidized bed boiler
Field of the invention
The invention relates to a method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler burning biofuel according to the preamble of the appended claim 1. The invention also relates to an air distribution system of a biofuel-burning bubbling fluidized bed boiler in accordance with the preamble of the appended claim 13.
In this description biofuel refers to solid fuels, wherein the portion of volatile matter in ash-free dry solids is over 60%. This type of fuels are, for example, peat, bark, wood chips, sawdust, waste construction timber, sludge created in process industry, and municipal solid waste.
Background of the invention
Bubbling fluidized bed boilers are generally used in energy production, wherein the fuels include biofuels, such as, for example, peat and wood chips. In the lower part of the furnace of a bubbling fluidized bed boiler there is a fluidized bed, which is composed of a fine, incombustible material, typically sand, which fluidizes over a grate forming the bottom of the boiler. The fluidizing of the material is created by feeding fluidizing gas through the grate to the fluidized bed. The fluidizing gas can be composed solely of air, so-called primary air, or it may be a gas mixture formed by primary air and inert gas, for example, flue gas. In a bubbling fluidized bed boiler the flow rate of the fluidizing gas supplied through the grate is set into such that the particles forming the fluidized bed do not escape with air to the upper part of the boiler, but they remain in the lower part of the furnace forming a fluidized bed that is continuously moving and efficiently mixes the fluidized bed material and the fuel supplied to it. The combustion air needed for burning fuel is generally supplied stagewise and in several portions to the furnace of the boiler in such a manner that a part of combustion air, i.e. fluidizing air, is formed by the primary air blown through the grate with the fluidizing gas a part is formed by secondary air supplied above the fluidized bed, and the rest of the combustion air is supplied to the upper part of the furnace of the boiler as so-called tertiary air. The boiler can also be divided into different air zones according to the air supplied to the boiler: the area between the fluidized bed and the secondary air supply is called the primary air zone, and the area between the secondary air supply and the tertiary air supply is called the secondary air zone.
Fuel is fed by means of so-called carrier air to the bubbling fluidized bed boiler on the fluidized bed. In and on the fluidized bed takes place the drying of fuel particles, the releasing of the volatile matter contained in them (i.e. pyrolysis), and finally the combustion of the remaining carbon residue. Drying and pyrolysis are very fast compared to the total combustion time of fuel particles. The volatile matter released in pyrolysis are mainly methane, CH4 and carbon monoxide CO, as well as nitrogen oxide emissions causing ammonia NH3 and hydrogen cyanide HCN. The volatile matter rises upwards and burns when reaching an oxygenous area. In a boiler equipped with staged air supply the combustion of volatile matter primarily is done by secondary air and partly tertiary air, and the combustion of the carbon residue of fuel particle is done by fluidizing, secondary and tertiary air.
By means of the staged air supply it is possible to reduce the formation of nitrogen oxides. That is, when there is oxygen, NH3 and HCN react into nitrogen monoxide NO. By staging the air supply, reducing, substoichiometric areas are formed in the furnace of the bubbling fluidized bed boiler. In these areas the NH3 and HCN formed of fuel are reduced to molecular nitrogen in accordance with the following reaction equations 1 and 2:
NH, +OH ->NH, +H -»NH- +H -»N- +NO
>N, (1 )
and HCN +0 >NCO +H >NH +H >N ÷N0 >N2 (2)
In addition, nitrogen oxides are reduced by means of an internal reburning reaction, wherein the hydrocarbon radicals formed in pyrolysis take part in reducing nitrogen oxides. An example of this kind of reaction is shown in reaction equation 3, wherein the hydrocarbon radical is -CHi.
NO +CHi > HCN +0 +0H > H1NCO-^UNHi +N0 >N2 (3)
10
Generally, the reducing areas are formed by adjusting the amount of fluidizing and secondary air. The furnace is maintained substoichiometric in relation to oxygen until the tertiary air supply, in which case the delay time needed for reactions (1) and (2) is maximized and the amount of NH3 and HCN is minimized before the tertiary air level. The optimum total air coefficient before the tertiary air supply in relation to NOx emissions is slightly below 1 depending on the combustion temperature. The air required for the burning out of volatile matter and carbon residue is supplied to the furnace as tertiary air. The residue NH3 and HCN in the flue gases are oxidized after the tertiary air zone into nitrogen oxides.
With these procedures according to a conventional, staged air supply, the nitrogen oxide emissions can be reduced approximately 30% in comparison to a non-staged air supply. Still problematic are the fine and light fuels, because most of the fuel particles do not end up in the fluidized bed, but they are pulled with the fluidizing gas and secondary air to the upper parts of the furnace. Thus, it is almost impossible for the fuels to create fuel combustion conditions in the furnace that are controlled and favourable to reducing nitrogen oxides.
It is known from patent Fl 108809 (corresponds to WO 01/96783) to reduce the nitrogen oxide emissions formed in the fluidized bed combustion by staging and directing the combustion air supply. The secondary air supplied above the fluidized bed is supplied in a directed manner to the furnace in such a manner that a cyclone is formed, in the middle of which there is a substoichiometric, hydrocarbon-radicals- containing zone and an oxygen-rich zone on the edges. A reburning reaction takes place on the interface of the zones. A purpose of the method is to slow down the combustion of volatile matter on the secondary air level and thus limit the rising of the combustion temperature. However, this method is not efficient enough for getting the nitrogen oxide emissions of the boiler in accordance with the strict emission standards.
Publication WO 02/090829 also discloses a nitrogen oxide reduction method based on the staging of combustion air. In the method, recirculation gas composed of flue gases is supplied between the supply points of secondary and tertiary airs, in the elevation of the bubbling fluidized bed boiler. Thus, the nitrogen oxides contained by the recirculation gas take part in the final stage of the above-presented reduction reactions (1) and (2) and intensify the reaction of nitrogen compounds formed of the fuel into molecular nitrogen. The problem with this solution is that it causes the amount of flue gases in the boiler to increase, in which case the size of the furnace must be increased, which in turn raises the price of the boiler. In addition, the method is suitable mainly for dry fuels. With wet fuels the amount of heat needed for drying reduces the combustion temperature in the secondary stage too much, thus preventing the creation of conditions favourable for reducing the nitrogen oxides.
Brief description of the invention
The purpose of the present invention is to provide a method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler burning biofuel, by means of which the above-mentioned drawbacks can be avoided. In addition, the purpose of the invention is to create an air distribution system of a bubbling fluidized bed boiler.
To attain this purpose, the method according to the invention is primarily characterized in what will be presented in the characterizing part of the independent claim 1. The air distribution system of a bubbling fluidized bed boiler according to the invention, in turn, is primarily characterized in what will be presented in the characterizing part of the independent claim 13.
The other, dependent claims will present some preferred embodiments of the invention.
The invention is based on the idea that the nitrogen oxide emissions of a bubbling fluidized bed boiler are reduced by using a staged air supply in such a manner that a part of primary air is supplied in connection with fuel supply, i.e. with the fuel or within the immediate vicinity of the fuel supply point in the same direction as the fuel itself. This part of primary air is in this application referred to as the combustion air of volatile matter. Thus, substantially all the fuel fed to the furnace is forced onto the surface of the fluidized bed for mixing it to the fluidized bed and for drying it quickly due to the effect of the hot fluidized bed material. The pyrolysis following the drying and the combustion of the volatile matter released from the fuel in the pyrolysis also takes place almost immediately after the fuel has mixed with the fluidized bed, because the fuel and the oxygen in the air supplied in connection with it are mixed quickly. Due to the quick mixing of the fuel and the oxygen, most of the volatile matter released from the fuel can be burnt in the upper part of the fluidized bed and on the fluidized bed, before the supply of secondary air. The combustion of volatile matter creates a high temperature, which maximizes the creation of hydrocarbon radicals formed of the fuel and promotes the reduction of the released nitrogen oxides.
The amount of combustion air of volatile matter supplied in connection with the fuel supply is adjusted into such that the combustion of volatile matter released in pyrolysis from the fuel being burnt takes place in substoichiometric conditions in relation to the volatile matter. The air coefficient SRV in relation to the volatile matter is thus as high as possible, however, below 1 , advantageously between 0.75 to 0.97 and preferably between 0.90 to 0.95. The total air coefficient SRtot on the same level of the furnace varies between 0.50 to 0.80, advantageously being 0.65.
Secondary air is supplied form the secondary air nozzles and tertiary air is supplied from the tertiary air nozzles placed above the secondary air nozzles. The task of the fluidizing gas supplied to the furnace through its bottom is to maintain the fluidized bed bubbling and its temperature suitable.
Thus, in the method according to the invention the combustion air amounts supplied in different stages of the staged combustion are thus adjusted, i.e. the total air coefficient SRtot needed for combustion and further the air coefficient in relation to the volatile matter SRV. This is illustrated later in tables 1 and 2 of this description. Feeding the fuel with air to the fluidized bed in such a manner that substantially all the fuel particles are forced there enables controlling the combustion substantially better than at present. Further, the amount of unburnt fuel can be minimized, because the delay time of fuel in the furnace is longer than in the solutions according to prior art.
Thus, in the method according to the invention, it is not the amount of air supplied to the furnace nor the total air coefficient that is affected, but how the air distribution is performed in order to have the air coefficient in relation to the volatile matter of the fuel as high as possible as low in the furnace as possible and yet as long as possible before the secondary air nozzles.
Several advantages are reached by means of the invention. Because combustion air is supplied together with the fuel or in the immediate vicinity of the fuel feeding point in the same direction as the fuel itself, the finely divided fuels, such as, for example peat, are forced on the surface of the fluidized bed, in which case they come into immediate contact with the hot fluidized bed material and do not escape to the upper parts of the furnace. Thus, the fuel is made to dry and inflame quickly in its entirety and the volatile matter released from it are burnt as low in the furnace as possible. Most of the volatile matter can be burnt before the actual secondary air level. The high temperature created in the combustion of volatile matter creates hydrocarbon radicals, which breaks down the formed nitrogen monoxide into molecular nitrogen before the secondary air zone.
Because the fine particles are forced by means of air on the surface of the fluidized bed, their delay time in the furnace before the secondary air supply is longer than in the solutions of prior art. Thus, the volatile matter in the fuel have time to bum almost completely before they travel upwards in the furnace.
The fact that the fuel particles are forced by means of air to the fluidized bed also reduces the fouling of heat exchange surfaces of the furnace. That is, the fuel particles escaping from the fuel supply and burning in the upper parts of the furnace raise the temperature of the fuel gases before they reach the heat surfaces and increase the fouling caused by ash melting. Fouling of the heat exchange surfaces diminishes the efficiency of the boiler and causes economical losses through boiler shutdowns required by the possible cleaning. By means of the invention fouling is minimized and through that, economic advantage is gained.
By means of the invention it is also possible to build the furnace of the boiler smaller in size and thus decrease the investment expenses of the boiler, because the combustion reactions take place lower in the boiler, in which case the heat transfer in the lower part of the boiler is more efficient.
Brief description of the drawings
In the following, the invention will be described in more detail with reference to the appended drawings, in which
Fig. 1 shows schematically a furnace of a bubbling fluidized bed boiler in a side view, Fig. 2 shows schematically a furnace of a bubbling fluidized bed boiler in a front view,
Fig. 3a shows fuel supply means seen from the inside of the furnace,
Fig. 3b shows fuel supply means according to a second embodiment seen from the inside of the furnace,
Fig. 3c shows fuel supply means according to a third embodiment seen from the inside of the furnace,
Fig. 4 shows the amount of pyrolysis gas in a furnace, and
Fig. 5 shows temperature distribution in a furnace above the surface of the bed.
Detailed description of the invention
Fig. 1 shows a side view of a furnace of a bubbling fluidized bed boiler 1. There is a fluidized bed 2 composed of bed material on the bottom of the furnace. Fluidizing gas is supplied to the furnace 1 through nozzles 4 arranged on its bottom 3, which gas fluidizes the bed material. The fluidizing gas can be solely air, or it may be a mixture of air and re- circulating gas. The fuel is supplied to the fluidized bed 2 from fuel supply means 5 arranged above the surface of the fluidized bed and placed substantially on a mutually same level. In the figure there are three fuel feeding means, but their number may vary depending on the size of the furnace or other parameters of the boiler. Fuel feeding means can also be arranged on the opposite side wall (not shown) of the furnace substantially on the same level with the fuel feeding means arranged on the side wall, as shown in the figure. They can also be placed on the front and/or back walls of the furnace. The fuel is fed to the fluidized bed by means of air. The amount of air used in connection with fuel feeding is so large, that it prevents fuel particles from escaping to the upper parts of the furnace by directing the fuel substantially on the surface of the fluidized bed. The additional air, combustion air of the volatile matter supplied in connection with air supply is a part of primary air. Secondary air is supplied from secondary air nozzles 6 located above the fuel feeding means to above the fluidized bed 2. Tertiary air is supplied to the furnace above the secondary air nozzles 6 via tertiary air nozzles 7 arranged in the upper part of the furnace.
The amount of air supplied to the furnace does not therefore increase in comparison to a conventional solution, but it is distributed in a different manner. The amount of primary air supplied as fluidizing gas or as a part of it and the amount of tertiary air remain substantially equal to conventional staged combustion. However, in connection with fuel feeding, separate combustion air of volatile matter is supplied to the furnace, which air correspondingly decreases the amount of secondary air.
Fig. 2 shows a front view of a furnace 1 of a bubbling fluidized bed boiler. Fuel is fed from a fuel supply means 5 to the fluidized bed 2. Fuel feeding takes place by means of carrier air and the combustion air of volatile matter, in which case the fuel-air-mixture 8 is forced all the way to the surface 2a of the fluidized bed 2. Finely divided fuel supplied to the fluidized bed dries immediately when coming into contact with hot bed material and pyrolizes substantially entirely. In pyrolysis the volatile matter released from the fuel burn on the surface 2a of the fluidized bed 2 and above the surface 2a of the fluidized bed by means of primary air forming a first, reducing primary air zone 9, which extends from the upper part of the fluidized bed to the secondary air nozzles 6. The combustion of volatile matter takes place in the primary air zone 9 in substoichiometric conditions in relation to the air coefficient SRV of volatile matter. Thus, also the total air coefficient SRtot is naturally below 1. When the air coefficient SRV in relation to volatile matter is as large as possible, but still a little below 1 , the volatile matter burns quickly and forms a high local temperature, and it forms a maximum amount of hydrocarbon radicals, which are needed in order to reduce nitrogen oxides formed from the fuel. The reducing secondary air zone 10 extends from the secondary air nozzles all the way to the tertiary air nozzles arranged over them.
Reducing the nitrogen oxides formed from fuel into molecular nitrogen is thus performed in two stages. In the first reducing stage, i.e. in the primary air zone 9, most of the volatile matter released from the fuel and a part of the carbon residue is burnt. This takes place in relation to both the total air coefficient SRtot and the air coefficient SRV of the volatile matter of the fuel in substoichiometric conditions, which results in a large amount of hydrocarbon radicals. The primary air required in this stage is brought to the furnace in connection with fuel supply and at least as a part of the fluidizing gas. 75 to 95%, preferably 90% of the air needed for combustion of pyrolysis gases is supplied as primary air. In the second reducing stage, i.e. the secondary air zone 10 following the first stage, combustion air is supplied to the furnace from secondary air nozzles 6 arranged within a distance from the surface of the fluidized bed in such a manner that the substoichiometric conditions remain, i.e. the total air coefficient SRtot is still below 1. The air coefficient SRV of volatile matter of the fuel rises in this zone above 1. Feeding of primary air in the manner described above in two stages, as fluidizing air and as combustion air of volatile matter has the effect that the temperatures in the lower parts of the furnace are higher than in known boilers equipped with staged air distribution. By means of the invention, the fuel is inflamed quickly and most of the volatile matter can be burnt before the actual secondary air level.
In figure 2 there are three secondary and tertiary air nozzles 6 and 7 side by side on the front wall of the furnace. Their number and placement may vary depending on the size of the boiler. The air nozzles can also be placed on the side walls of the boiler.
The following tables 1 and 2 show two examples of applying the invention in a bubbling fluidized bed boiler, whose firing rate is 300 MW. The examples show stagewise both the air distribution in a bubbling fluidized bed boiler according to prior art and the air distribution in the same boiler in accordance with the invention when the fuel and boiler load remain the same. The air amount (kg/s) supplied to the boiler in each stage, the total air coefficient SRtot of the stage in question and the air coefficient in relation to the volatile matter SRV are shown. In the example of table 1 the fuel is peat and in the example of table 2 the fuel is wood. When comparing the air amounts it is to be taken into account that in air distribution according to prior art air is supplied to the primary air zone only as fluidizing air along with the fluidizing gas and the carrier air amount used in fuel supply is a small part of the total amount of combustion air. In the method according to the invention the combustion air of volatile matter supplied in connection with fuel supply and the fluidizing air supplied together with the fluidizing gas form the amount of primary air supplied to the furnace. The small amounts of cooling air of the start-up burners have not been taken into account in dimensioning the combustion air of volatile matter, because they do not penetrate to the furnace and therefore they do not take part in the combustion in the primary air zone.
Table 1.
Figure imgf000013_0001
The percentage of the volatile matter of the dry fuel flow is approximately 70 mass-%, coke approximately 24.5 mass-% and ash approximately 5.5 mass-%. The moisture content of the fuel is 46 mass-%.
Table 2.
Figure imgf000014_0001
The percentage of the volatile matter of the dry fuel flow is approximately 85 mass-%, coke approximately 13 mass-% and ash approximately 2 mass-%. The moisture content of the fuel is 46 mass- %.
As can be seen in the examples, the new air distribution according to the invention has an effect on the amounts of additional air and secondary air supplied in connection with fuel supply. The other, fluidizing air and tertiary air supplied together with the fluidizing gas, as well as the small air amounts used in cooling start-up burners and load carrying burners remain the same as in air distribution according to prior art. The amount of air supplied together with the fuel is significantly larger than the amount of carrier air used for fuel supply in prior art. The amount of air supplied with the fuel varies depending on the fuel, because different fuels contain different amounts of volatile matter and the purpose is to burn them in substoichiometric conditions before the supply of secondary air.
The additional air fed in connection with fuel supply, i.e. the combustion air of volatile matter, which is a part of primary air, can be supplied either with the fuel, mixed into the carrier air of the fuel, or parallelly with the fuel supply taking place by the carrier air. Figure 3a shows a fuel supply means 5, i.e. a fuel feeding opening 5a seen from the inside of the furnace, wherein the fuel and the combustion air supplied with it are mixed right before they are fed to the furnace together. The feeding opening 5a is rectangular, which is the most advantageous form for a feeding opening, but otherwise shaped feeding openings may also be applied. In the fuel feeding means 5 shown in figure 3b the fuel and combustion air are fed parallel to the furnace. The fuel is fed to the furnace by means of carrier air from the fuel feeding opening 5a, which is on three sides surrounded by a uniform air channel 11 for supplying combustion air of volatile matter. The air channel 11 is a uniform channel and it surrounds the fuel feeding opening from its three sides in such a manner that there is no air supply from below the feeding opening 5a. Thus, when being fed, the fuel is forced in an "air tunnel" formed by combustion air of volatile matter, which directs the fuel, forces it onto the surface 2a of the fluidized bed 2 and thus prevents the fuel particles from escaping to the upper parts of the furnace. Thus, the momentum of combustion air is so high that the fuel cannot escape. In the embodiments of figure 3c, the air channels 11a, 11b and 11c are separate air channels in relation to the fuel feeding opening 5a, which channels are placed within a small distance from the fuel feeding opening 5a, on its three sides. The air channels 11a to 11c are also placed in such a manner that there is no air channel under the fuel feeding opening 5a. The design of the air channel and the placement of the air channels 11a to 11c in relation to the fuel feeding opening help in directing the fuel particles to be directed to the fluidized bed.
The invention is illustrated in figures 4 and 5 by means of graphs, which are formed by modelling a bubbling fluidized bed boiler with a fuel power of 300 MW with a full load, wherein the fuel has been a mixture of peat (70%) and wood (30%). Each graph shows two curves: curves for both the air distribution according to prior art and the air distribution according to the invention. These different air distributions are explained in connection with tables 1 and 2.
Figure 4 shows the portion of pyrolysis gas in a furnace above the surface of the bed, wherein the portion of pyrolysis gases formed as a result of air distribution according to prior art is illustrated by dashed lines and the portion of pyrolysis gases reached by means of the invention is illustrated with a solid line. The graphs show that by means of the invention the releasing and combustion of pyrolysis gas mostly take place before the secondary air supply. In a bubbling fluidized bed boiler equipped with air distribution according to prior art the releasing of pyrolysis gas significantly takes place before the secondary air level, but because of lack of oxygen hardly any combustion takes place. Because of the escaping fuel particles, the releasing of pyrolysis gases takes place even on secondary and tertiary air levels.
Figure 5 shows the temperature distribution above the bed of a furnace. The temperature distribution according to prior art is shown by dashed lines and the temperature distributions reached by means of the invention are shown by a solid line. It can be seen from the graphs that by means of the invention the temperature of the furnace is higher in the primary air zone than in a bubbling fluidized bed boiler equipped with air distribution according to prior art. The temperature remains higher almost to the tertiary level, after which it decreases to lower than in prior art, because there is no more combustible matter left.
The invention is not intended to be limited to the embodiments presented as examples above, but the invention is intended to be applied widely within the scope of the inventive idea as defined in the appended claims.

Claims

Claims
1. A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler burning biofuel, in which method a) at least primary air is supplied to a fluidized bed (2) arranged in the lower part of a furnace (1) of the fluidized bed boiler for fluidizing the bed material forming the fluidized bed (2) in the furnace, b) fuel is fed to the fluidized bed (2), which dries when coming into contact with hot bed material and pyrolizes into pyrolysis gas comprising volatile matter of fuel, which gas rises upwards in the furnace and burns there, c) at least a part of the carbon residue from the pyrolysis is burnt in the fluidized bed (2) by means of primary air, d) secondary air is supplied above the fluidized bed (2) from secondary air nozzles (6), e) tertiary air is supplied above the secondary air nozzles (6), characterized in that
- a part of primary air is supplied in connection with fuel feeding in stage b) in such a manner that the fuel is forced substantially on the surface of the fluidized bed (2), thus pyrolizing substantially entirely, and in that
- at least a part of the pyrolysis gases formed in the pyrolysis is burnt by means of primary air in such a manner that the air coefficient in relation to the volatile matter of fuel in the pyrolysis gas is in the substoichiometric area.
2. The method according to claim 1 , characterized in that at least a part of the pyrolysis gases are burnt by means of combustion air of volatile matter supplied in connection with fuel feeding before secondary air is supplied to the furnace.
3. The method according to claim 2, characterized in that 75 to 95%, preferably 90% of the air needed for combustion of pyrolysis gases is supplied as primary air.
4. The method according to claim 2, characterized in that a part of the pyrolysis gases formed in the pyrolysis is burnt by primary air supplied for fluidizing the fluidized bed.
5. The method according to claim 1 , characterized in that fuel is forced onto the surface of the fluidized bed by means of the momentum of the primary air supplied in connection with fuel feeding.
6. The method according to claim 2, characterized in that a primary air zone (9), which reduces nitrogen oxides, is formed between the upper part of the fluidized bed (2) and the secondary air nozzles (6), which zone comprises a great deal of hydrocarbon radicals.
7. The method according to claim ^ characterized in that at least a part of the pyrolysis gases formed in the pyrolysis is burnt by means of the air supplied in connection with fuel feeding in such a manner that the air coefficient (SRV) in relation to volatile matter of fuel is 0.75 to - 0.97, advantageously 0.90 to 0.95.
8. The method according to claim 7, characterized in that at least a part of the pyrolysis gases formed in the pyrolysis is burnt by means of the air supplied in connection with fuel feeding in such a manner that the total air coefficient (SRtot) is 0.5 to 0.8, advantageously 0.65.
9. The method according to claim 1 , characterized in that secondary air is supplied to the furnace (1 ) in such a manner that a substoichiometric, nitrogen-oxides-reducing secondary air zone (10) is formed between the secondary air nozzles (6) and the tertiary air nozzles (7), in which zone the total air coefficient (SRtot) is 0.7 to 0.95, advantageously 0.85 to 0.9.
10. The method according to claim 1 , characterized in that the part of the primary air supplied in stage b) is supplied to the furnace (1) together with the fuel or parallel with the fuel feeding.
11. The method according to claim 10, characterized in that a part of primary air is supplied to the furnace (1) around the fuel feeding opening (5a).
12. The method according to claim 1 , characterized in that recirculating gas is supplied to the fluidized bed (2) in order to fluidize the bed material forming the fluidized bed (2) in the furnace (1).
13. An air distribution system of a biofuel-buming bubbling fluidized bed boiler, in which system a) nozzles (4) are arranged on the bottom of a furnace (1) of the bubbling fluidized bed boiler for supplying at least primary air for fluidizing the bed material forming the fluidized bed (2) arranged in the lower part of the furnace (1 ), b) fuel feeding means (5) are arranged on the walls of the furnace (1) for feeding fuel to the fluidized bed (2), which fuel dries when coming into contact with hot bed material and pyrolizes into pyrolysis gas comprising volatile matter of the fuel, which gas rises upwards in the furnace and it burns there, c) at least a part of the carbon residue from the pyrolysis is arranged to be burnt in the fluidized bed (2) by means of primary air, d) secondary air nozzles (6) are arranged on the walls of the furnace (1) above the fluidized bed (2) in order to supply secondary air into the furnace (1 ), e) tertiary air nozzles (7) are arranged on the walls of the furnace (1) above the secondary air nozzles (6) in order to supply tertiary air into the furnace (1), characterized in that - a part of primary air is arranged to be supplied in connection with fuel feeding in stage b) in such a manner that the fuel is forced substantially on the surface or the fluidized bed (2), thus pyrolizing substantially entirely, and in that
- at least a part of the pyrolysis gases formed in the pyrolysis is arranged to be burnt by means of primary air in such a manner that the air coefficient in relation to the volatile matter of fuel in the pyrolysis gas is in the substoichiometric area.
14. The air distribution system according to claim 13, characterized in that at least a part of the pyrolysis gases is arranged to be burnt by means of the combustion air of volatile matter supplied in connection with fuel feeding before secondary air is supplied to the furnace.
15. The air distribution system according to claim 13, characterized in that 75 to 95%, preferably 90% of the air needed for combustion of pyrolysis gases is supplied as primary air.
16. The air distribution system according to claim 14, characterized in that a part of the pyrolysis gases formed in the pyrolysis is arranged to be burnt by primary air supplied for fluidizing the fluidized bed.
17. The air distribution system according to claim 13, characterized in that the momentum of the primary air supplied in connection with fuel feeding forces the fuel onto the surface of the fluidized bed.
18. The air distribution system according to claim 14, characterized in that a primary air zone (9), which reduces nitrogen oxides, is arranged to be formed between the upper part of the fluidized bed (2) and the secondary air nozzles (6), which zone comprises a great deal of hydrocarbon radicals.
19. The air distribution system according to claim 13, characterized in that at least a part of the pyrolysis gases formed in the pyrolysis is arranged to be burnt by means of the air supplied in connection with fuel feeding in such a manner that the air coefficient (SRV) in relation to volatile matter of fuel is 0.75 to 0.97, advantageously 0.90 to 0.95.
20. The air distribution system according to claim 19, characterized in that at least a part of the pyrolysis gases formed in the pyrolysis is arranged to be burnt by means of the air supplied in connection with fuel feeding in such a manner that the total air coefficient (SRtot) is 0.5 to 0.8, advantageously 0.65.
21. The air distribution system according to claim 13, characterized in that secondary air is arranged to be supplied to the furnace (1) in such a manner that a substoichiometric, nitrogen-oxides-reducing secondary air zone (10) is formed between the secondary air nozzles (6) and the tertiary air nozzles (7), in which zone that total air coefficient (SRtot) is 0.7 to 0.95, advantageously 0.85 to 0.9.
22. The air distribution system according to claim 13, characterized in that the primary air supplied in connection with fuel feeding is arranged to be supplied to the furnace (1 ) together with the fuel or parallel with the fuel feeding.
23. The air distribution system according to claim 22, characterized in that the fuel feeding means (5) comprise a fuel feeding opening (5a) and in its immediate vicinity at least one air supply opening (11), and that the primary air supplied in connection with fuel feeding is arranged to be supplied to the furnace (1) around the fuel feeding opening (5a) parallel with the fuel fed from the fuel feeding opening (5a).
24. The air distribution system according to claim 23, characterized in that an air supply opening (11) is arranged around the fuel feeding opening (5a) in order to supply the primary air supplied in connection with fuel feeding.
25. The air distribution system according to claim 13, characterized in that the nozzles (4) are arranged to supply recirculation gas to the fluidized bed (2) in order to fluidize the bed material forming the fluidized bed (2) in the furnace (1).
PCT/FI2006/050056 2005-02-11 2006-02-09 A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler and an air distribution system of a bubbling fluidized bed boiler WO2006084954A1 (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
US11/883,887 US20080149012A1 (en) 2005-02-11 2006-02-09 Method For Reducing Nitrogen Oxide Emissions of a Bubbling Fluidized Bed Boiler and an Air Distribution System of a Bubbling Fluidized Bed Boiler
CA2597159A CA2597159C (en) 2005-02-11 2006-02-09 A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler and an air distribution system of a bubbling fluidized bed boiler
EP06708960.7A EP1846694B1 (en) 2005-02-11 2006-02-09 A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
FI20055063A FI20055063A (en) 2005-02-11 2005-02-11 Method for reducing nitrogen oxide emissions from a fluidized bed boiler and air distribution system for a fluidized bed boiler
FI20055063 2005-02-11

Publications (1)

Publication Number Publication Date
WO2006084954A1 true WO2006084954A1 (en) 2006-08-17

Family

ID=34224273

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/FI2006/050056 WO2006084954A1 (en) 2005-02-11 2006-02-09 A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler and an air distribution system of a bubbling fluidized bed boiler

Country Status (5)

Country Link
US (1) US20080149012A1 (en)
EP (1) EP1846694B1 (en)
CA (1) CA2597159C (en)
FI (1) FI20055063A (en)
WO (1) WO2006084954A1 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008082522A1 (en) 2006-12-22 2008-07-10 Covanta Energy Corporation Tertiary air addition to solid waste-fired furnaces for nox control
EP2206953A1 (en) * 2007-11-07 2010-07-14 Metawater Co., Ltd. Fluidized-bed incinerator and method of fluidized-bed incineration of sludge with the same
EP2574841A2 (en) 2011-09-30 2013-04-03 Fortum OYJ Method for reducing nitrogen oxide emissions and corrosion in a bubbling fluidized bed boiler and a bubbling fluidized bed boiler
US8443739B2 (en) 2006-12-22 2013-05-21 Covanta Energy Corporation Tertiary air addition to solid waste-fired furnaces for NOx control
EP3054214A1 (en) 2015-02-09 2016-08-10 Fortum OYJ Method for feeding air to a fluidized bed boiler, a fluidized bed boiler and fuel feeding means for a fluidized bed boiler

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FI123853B (en) * 2009-03-06 2013-11-15 Metso Power Oy A method for reducing nitrogen oxide emissions from oxygen combustion
FI125814B (en) * 2009-06-02 2016-02-29 Valmet Technologies Oy Method for performing pyrolysis and pyrolysis apparatus
CN102330973A (en) * 2011-10-13 2012-01-25 邹城市圣瑞达能源有限公司 Blending gas-solid mixed fuel technology of CFB (circulating fluid bed) boiler
FI126253B (en) * 2015-02-09 2016-08-31 Fortum Oyj Method for reducing nitrogen oxide emissions in a bubbling fluidized bed boiler and bubbling fluidized bed boiler
CN107787430B (en) * 2015-06-15 2021-10-15 因姆普朗伯德公司 Method for operating a fluidized bed boiler
CN113522743B (en) * 2021-07-30 2022-05-17 中国矿业大学 Method and system for weakening bubbles in gas-solid separation fluidized bed

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3863577A (en) * 1971-11-22 1975-02-04 Dorr Oliver Inc Fluidized bed reactor
US4060041A (en) * 1975-06-30 1977-11-29 Energy Products Of Idaho Low pollution incineration of solid waste
EP0386527A2 (en) * 1989-03-06 1990-09-12 PAULI, Balduin Method and device for injecting and burning fuels with low residue content
US5401130A (en) * 1993-12-23 1995-03-28 Combustion Engineering, Inc. Internal circulation fluidized bed (ICFB) combustion system and method of operation thereof
GB2286345A (en) * 1994-02-09 1995-08-16 Mark Frederick Wickham Feeding a fluidised bed

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5660125A (en) * 1995-05-05 1997-08-26 Combustion Engineering, Inc. Circulating fluid bed steam generator NOx control
JP3037134B2 (en) * 1996-04-26 2000-04-24 日立造船株式会社 Fluid bed incinerator
ATE228225T1 (en) * 1996-12-30 2002-12-15 Alstom Power Inc METHOD FOR CONTROLLING NITROGEN OXIDES IN A CIRCULATING FLUIDIZED STEAM GENERATOR
FI102411B (en) * 1997-02-07 1998-11-30 Kvaerner Power Oy Method and arrangement for supplying air to a fluidized bed boiler
US6336415B1 (en) * 1998-05-11 2002-01-08 Alstom (Switzerland) Ltd Method for the heat treatment of solids
WO2002093074A1 (en) * 2001-05-11 2002-11-21 Kvaerner Power Oy Combined fluidized bed and pulverized coal combustion method

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3863577A (en) * 1971-11-22 1975-02-04 Dorr Oliver Inc Fluidized bed reactor
US4060041A (en) * 1975-06-30 1977-11-29 Energy Products Of Idaho Low pollution incineration of solid waste
EP0386527A2 (en) * 1989-03-06 1990-09-12 PAULI, Balduin Method and device for injecting and burning fuels with low residue content
US5401130A (en) * 1993-12-23 1995-03-28 Combustion Engineering, Inc. Internal circulation fluidized bed (ICFB) combustion system and method of operation thereof
GB2286345A (en) * 1994-02-09 1995-08-16 Mark Frederick Wickham Feeding a fluidised bed

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See also references of EP1846694A4 *

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008082522A1 (en) 2006-12-22 2008-07-10 Covanta Energy Corporation Tertiary air addition to solid waste-fired furnaces for nox control
EP2121167A1 (en) * 2006-12-22 2009-11-25 Covanta Energy Corporation Tertiary air addition to solid waste-fired furnaces for nox control
EP2121167A4 (en) * 2006-12-22 2011-12-07 Covanta Energy Corp Tertiary air addition to solid waste-fired furnaces for nox control
US8443739B2 (en) 2006-12-22 2013-05-21 Covanta Energy Corporation Tertiary air addition to solid waste-fired furnaces for NOx control
EP2206953A1 (en) * 2007-11-07 2010-07-14 Metawater Co., Ltd. Fluidized-bed incinerator and method of fluidized-bed incineration of sludge with the same
US20100192816A1 (en) * 2007-11-07 2010-08-05 Metawater Co., Ltd. Fluidized bed incinerator and fluidized bed incinerating method for sludge using the same
US8881662B2 (en) * 2007-11-07 2014-11-11 Metawater Co., Ltd. Fluidized bed incinerator and fluidized bed incinerating method for sludge using the same
EP2206953A4 (en) * 2007-11-07 2017-05-03 Metawater Co., Ltd. Fluidized-bed incinerator and method of fluidized-bed incineration of sludge with the same
EP2574841A2 (en) 2011-09-30 2013-04-03 Fortum OYJ Method for reducing nitrogen oxide emissions and corrosion in a bubbling fluidized bed boiler and a bubbling fluidized bed boiler
EP2574841A3 (en) * 2011-09-30 2014-02-26 Fortum OYJ Method for reducing nitrogen oxide emissions and corrosion in a bubbling fluidized bed boiler and a bubbling fluidized bed boiler
EP3054214A1 (en) 2015-02-09 2016-08-10 Fortum OYJ Method for feeding air to a fluidized bed boiler, a fluidized bed boiler and fuel feeding means for a fluidized bed boiler

Also Published As

Publication number Publication date
CA2597159C (en) 2013-10-22
CA2597159A1 (en) 2006-08-17
EP1846694B1 (en) 2017-05-10
FI20055063A (en) 2006-08-12
EP1846694A4 (en) 2012-01-04
EP1846694A1 (en) 2007-10-24
US20080149012A1 (en) 2008-06-26
FI20055063A0 (en) 2005-02-11

Similar Documents

Publication Publication Date Title
CA2597159C (en) A method for reducing nitrogen oxide emissions of a bubbling fluidized bed boiler and an air distribution system of a bubbling fluidized bed boiler
EP1287290B1 (en) Low nitrogen oxides emissions using three stages of fuel oxidation and in-situ furnace flue gas recirculation
US4321233A (en) Combustion furnace or reactor with multi-stage fluidized bed system
US5626088A (en) Method and apparatus for utilizing biofuel or waste material in energy production
US5937772A (en) Reburn process
KR0164586B1 (en) Method and apparatus for reducing emission of n2o when burning nitrogen containing fuels in fluidized bed reactors
CN104154530B (en) Double-flow-state clean combustion boiler and double-flow-state clean combustion technology
SK279954B6 (en) Process for decreasing n2o content in combustion gas
CN102563690B (en) Method for controlling emission of nitrogen oxide of coal burning boiler
JP2002243108A (en) Mixed-fuel fired device of coal and biofuel and operating method thereof
US4681065A (en) Multibed fluidized bed boiler
EP1164331A1 (en) Waste incinerator flue gas recirculation
CA2446950C (en) Combined fluidized bed and pulverized coal combustion method
EP2574841A2 (en) Method for reducing nitrogen oxide emissions and corrosion in a bubbling fluidized bed boiler and a bubbling fluidized bed boiler
CN211502751U (en) Combustion apparatus
EP3054214B1 (en) Method for feeding air to a fluidized bed boiler, a fluidized bed boiler and fuel feeding means for a fluidized bed boiler
JP2009120695A (en) Method for fluidized bed-drying and classifying coal
JPS62169907A (en) Pulverized coal combustion boiler
CN111780095A (en) Combustion system, control method thereof and preheating equipment
WO2001096783A1 (en) Method and arrangement for reducing nitrogen oxide emissions from fluidized bed combustion
CN111706857A (en) Low-NOx-emission variable-section circulating fluidized bed staged combustion boiler system and method
SU1719781A1 (en) Fluidized-bed apparatus
US20090123883A1 (en) Swirling-type furnace operating method and a swirling-type furnace
CN111536507A (en) Low-emission type circulating fluidized bed boiler separation return regulation and control system and integration method
SK48798A3 (en) Method and apparatus for controlling the temperature of the bed of a bubbling bed boiler

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application
DPE2 Request for preliminary examination filed before expiration of 19th month from priority date (pct application filed from 20040101)
REEP Request for entry into the european phase

Ref document number: 2006708960

Country of ref document: EP

WWE Wipo information: entry into national phase

Ref document number: 2006708960

Country of ref document: EP

WWE Wipo information: entry into national phase

Ref document number: 2597159

Country of ref document: CA

WWE Wipo information: entry into national phase

Ref document number: 11883887

Country of ref document: US

NENP Non-entry into the national phase

Ref country code: DE

WWP Wipo information: published in national office

Ref document number: 2006708960

Country of ref document: EP