A METHOD OF PRODUCING SO2 SORBENT AND THEREAFTER UTILIZING SUCH SO2 SORBENT TO DESULFURIZE COMBUSTION GASES

Abstract: A method of producing SO2 sorbent and of thereafter utilizing such SO2 sorbent to effect therewith the desulfurization of combustion gases wherein limestone particles are injected (52) into a conventional solid fuel-fired steam generator (10) and are subjected therein to "deadburning" thereby creating unreactive lime particles therefrom with these unreactive lime particles thereafter being reactivated by virtue of being subjected to hydration (58), and following the reactivation thereof these reactive lime particles then being utilized in a flue gas desulfurization device (62) for the purpose of effecting therewith the desulfurization of the combustion gases generated as a result of the combustion of solid fuel in the conventional solid fuel-fired steam generator (10).

Description: A METHOD OF PRODUCING S0 2 SORBENT AND THEREAFTER UTILIZING SUCH S0 2 SORBENT TO DESULFURIZE COMBUSTION GASES BACKGROUND OF THE INVENTION This invention relates to the desulfurization of the gases that are generated as a consequence of the combustion of fossil fuels, and more specifically, to a method of producing S0 2 sorbent and thereafter of utilizing such S0 2 sorbent to desulfurize combustion gases. Sulfur in coal exists in two forms: organic and inorganic. The inorganic compound pyrite, FeS 2 , is present as discrete particles within the fuel, and typically accounts for twenty to fifty percent of the total sulfur. The milling and classifying operations associated with pulverized-fuel steam generators with which pulverizers are utilized separate a substantial portion of the pyritic sulfur from the coal. An additional amount of inorganic sulfur is retained in the bottom ash and the fly ash leaving the pulverized-fuel steam generators in solid form. Contained in the molecular structure of the coal, organic sulfur is oxidized during the combustion process and emitted from the pulverized- fuel steam generators as gaseous oxides of sulfur. The principal oxidizing reaction leads to the formation of sulfur dioxide, S0 2 . In addition to S0 2 , lesser quantities of sulfur trioxide, S0 3 , are formed during combustion. Typically, the ratio of S0 2 /S0 3 in combustion gases ranges from 20:1 to 80: 1. S0 3 is highly reactive and is extremely hygroscopic compared to S0 2 . As such, S0 3 is capable of readily combining with water to form sulfuric-acid aerosols. Such a reaction is enhanced by the presence of fine particles, which serve as condensation nuclei. The resulting aerosol is a principal constituent of visible stack plumes exiting from the stacks associated with pulverized-fuel steam generators. Historically, gaseous sulfur-dioxide emissions have been controlled by either dispersion or reduction. Dispersion of S0 2 and other pollutants through tall stacks is the oldest form of control. Under favorable meteorological conditions tall stacks can effectively limit ground-level S0 2 concentration to local ambient air-quality standards. Thermal inversions or comparable short-term meteorological conditions can impair the effectiveness of dispersion as a control method. A further and more critical concern over control by dispersion is the accumulating scientific evidence that oxides of sulfur and nitrogen are principal precursors to acid precipitation. Reduction of sulfur emissions is known to have been achieved through one or a combination of the following: switching to lower-sulfur fuels, use of fuel desulfurization methods, and use of flue-gas desulfurization systems. Switching to lower-sulfur fuels, however, is not possible for many large fossil fuel-fired steam generating plants. Fuel desulfurization processes range from conventional coal washing to coal liquefaction and gasification. Coal washing is effective in reducing the pyritic sulfur in the coal. Coal washing cannot, however, remove the organic sulfur from the coal matrix, and as such coal washing is limited to sulfur reduction of less than fifty percent. Flue-gas desulfurization is believed to have begun in England in 1935. Since that time, over fifty flue-gas desulfurization processes are known to have been developed, differing in the chemical reagents and the resultant end products. Lime or limestone scrubbing is the oldest and most common method of flue-gas desulfurization. The first successful closed-loop lime/limestone process has been credited to the English firm of J. Howden and Company. The first pilot plant tests thereof that were conducted had the scrubber effluent being recycled to the absorber. Unfortunately, however, scale was found to have formed in the absorber. The critical breakthrough in system chemistry for this process came when the problem was identified as one of excessive gypsum supersaturation in the scrubber. The solution to this problem was found to lie in the addition of a crystallization tank and in increasing the liquid-to-gas ratio. Adding a crystallization tank operating at high solids concentration allows calcium-sulfur compounds to precipitate outside the scrubber. Because of precipitation reactions, the absorbent recycled to the scrubber has a lower concentration of scale-forming gypsum. A high liquid-to-gas ratio minimizes the increase in supersaturation across the scrubber and thereby further diminishes the potential for scale formation. Later on, an attempt was made to develop and market a limestone-injection scrubbing process. In accordance therewith, pulverized limestone was injected into the furnace simultaneously with the coal. The resulting calcined limestone, CaO, was entrained in the flue gas along with fly ash. A water scrubber was used to remove the fly ash, limestone, and S0 2 from the flue gas. Several systems were placed into operation but persistent difficulties with scaling, poor additive utilization, and plugging of furnace convective surfaces prompted a return to the older Howden tail-end process. In a typical lime/limestone wet flue-gas desulfurization system, flue gas from the furnace enters the scrubber and contacts the absorbent slurry while sulfur dioxide and lesser amounts of oxygen are simultaneously absorbed. The spent absorbent returns to the reaction tank, or scrubber- effluent hold tank, where the dissolved sulfur compounds are precipitated as calcium salts. Fresh limestone or lime slurry is added to regenerate the spent absorbent. Minimizing the amount of alkali additive required to obtain a desired S0 2 removal efficiency reduces the operating cost of a flue-gas desulfurization system. To determine the factors influencing additive use, it is necessary to understand the additive dissolution process and the effect of system operating conditions, design, and additive properties on this process. In a lime/limestone S0 2 scrubbing system, the addition of alkali is controlled to neutralize the S0 2 absorbed and precipitate the calcium-sulfur salts. Although in theory the amount of lime or limestone required is stoichiometrically equal to the amount of S0 2 removed, the kinetics of the limestone dissolution process dictates the use of excess additive to achieve the desired S0 2 removal efficiency. Additive stoichiometry is usually defined as the moles of additive fed, excluding impurities, to a scrubber per mole of S0 2 absorbed. Although it can be, and sometimes is, defined as the moles of additive fed per mole of S0 2 entering the scrubber. Although not usually significant, the absorption of other acid gases such as HCl can influence utilization of the additive. Utilization then could be more broadly defined as the fraction of additive converted to reaction products in the scrubber. In order to increase utilization, one must thus either reduce the additive feed rate while maintaining constant S0 2 absorption efficiency or increase the S0 2 removal efficiency for a given limestone feed rate. The dissolution rate of alkali additives is inversely proportional to the solution pH. Therefore, better utilization is possible by operating a system at low pH levels. However, reducing the pH can also reduce S0 2 removal efficiency. As such, it is usually more productive to increase the absorber performance for the same system pH, or increase the additive dissolution and utilization at a constant system pH. Lime or calcium oxide, CaO, is obtained from calcination of limestone, CaC0 3 . The conditions under which the limestone is calcined or "burned" can have a great impact on the reactivity of the lime produced. Because of the high reactivity of most commercially available lime, it is possible to achieve high utilization, as much as ninety-five percent, with minimum impact on the remainder of the system. The main design parameter in maximizing utilization is the pH of the scrubbing slurry. With pH maintained above 8.5, considerable carbon-dioxide absorption occurs because of the ten to fifteen percent by volume of C0 2 in the flue gas. Carbon dioxide reacts with lime in a manner similar to sulfur dioxide to form calcium carbonate. Calcium carbonate, being insoluble at high pH, precipitates and thus prevents the calcium from reacting with sulfur dioxide. Based on known data, it has been found that a decrease in utilization from ninety-five percent to eighty-five percent may occur as pH is increased from 7.5 to 9.0. In order, therefore, to reduce waste of the relatively high-cost lime, the pH of lime systems should thus be held below 8.5. Limestone is usually less reactive than lime in flue-gas desulfurization systems operating under identical conditions. For this reason, system modifications are needed to produce limestone utilization in excess of ninety to ninety-five percent. Limestone dissolution is a function of surface area of the suspended limestone and hydrogen-ion concentration, i.e., pH, of the solutions. Two methods thus are suggested of increasing the limestone dissolution rate and, therefore, utilization; namely, first, by increasing the surface area, and secondly, by increasing the hydrogen-ion concentration, i.e., reducing pH. Large surface areas can be produced by finely grinding the limestone before the limestone is injected into the system. Limestone is typically ground to eighty to ninety percent through 325 mesh in flue-gas desulfurization applications. Finer grinds are possible, but more pulverizer power is required. However, this could still conceivably prove to be cost- effective. Limestone utilization can also be improved by operating at reduced pH's. However, this impairs efficiency. Namely, to maintain the same removal at reduced pH, the absorber design must be modified. For example, the liquid-to-gas ratio may be increased, with concomitant higher pumping costs, or tower height may be increased, with concomitant higher capital costs. Thus, the cost-effectiveness of any such adjustments need to be examined before being implemented. It is also possible to use a two-stage operation in which the primary stage is operated at reduced pH to optimize lime/limestone use, and the second stage is operated at high pH to accomplish the required S0 2 removal. In accord with such operation, limestone is fed to the second stage and the spent slurry from the second stage is fed to the primary stage before being bled off. Another technique for improving limestone utilization is to increase residence time. To this end, at a fixed rate of reaction, the longer a limestone particle remains in the absorber/reaction-tank loop, the greater will be the fraction of the particle that dissolves. The residence time of the solid particles in the process is a function of the particle inventory and the solids bleed rate. However, because the bleed rate is fixed by the S0 2 absorption rate at steady-state, only the inventory can be adjusted. In this regard, the solids inventory can be made greater by increasing the reaction-tank volume and/or the solids concentration. But, because the slurry is abrasive, the solids concentration has a practical upper limit of about fifteen percent. Thus, the relatively low cost of tanks and low mixer power requirements suggests that, in many situations it may, therefore, be less expensive to increase the tank size to improve limestone use. As such, although at present furnace limestone injection is perceived to be a commercially viable technology for purposes of accomplishing therewith cheap flue gas desulfurization, to date it has found only limited applicability because of the low utilization of the sorbent that is associated with the employment of furnace limestone injection. It is known, however, that such utilization of the sorbent when furnace limestone injection is employed could be increased by reducing the particle size of the sorbent. To do so though has been considered to be uneconomical because of the high cost associated with effecting the requisite reduction in the particle size of the sorbent, i.e., the limestone, by the grinding thereof. Continuing, dry scrubbing technology is considered by some to be a possible alternative to the employment of wet desulfurization technologies in a fossil fuel-fired power generation plant. The sorbent that is employed with the dry scrubbing technology is lime whereas the sorbent that is most often employed with the wet desulfurization technologies is limestone. Unfortunately, however, the dry scrubbing technology is disadvantageously characterized not only by the fact that lime is more expensive than limestone, but is also disadvantageously characterized by the fact that lime is not available in some markets. It is known that some attempts have been made to date to utilize furnace injection limestone as a possible source of potentially cheap lime that could be employed as the sorbent in applications wherein it is desired to use the dry scrubbing technology. To this end, in accordance with such attempts limestone is injected into the furnace where the injected limestone is calcined to lime and where this lime thereafter is operative to react within the furnace with S0 2 , which is generated from the combustion of the fossil fuel within the furnace, such that some sulfur absorption is thereby effected by such lime within the furnace. Although some sulfur absorption is effected in the furnace by the lime that results from the calcination within the furnace of the injected limestone, the intent is that most of the desired sulfur absorption be accomplished through use of the dry scrubbing technology. To this end, the active species insofar as the dry scrubbing technology is concerned is Ca(OH) 2 , which is formed by reactivating with water the lime that is entrained in the ash, the latter being generated as a result of the combustion of the fossil fuel in the furnace. A limiting factor insofar as the reactivation of such lime, i.e., the conversion thereof to Ca(OH) 2 is concerned, is that such lime represents only a very small portion of the contents of the ash in which such lime is entrained as contrasted to the amount of ash that is contained therein. Another limiting factor is that it is not possible to exercise control over the amount of such lime that becomes entrained in the ash such as to be able to thereby effectively coordinate the amount of lime, which is produced from the calcination within the furnace of the limestone injected thereinto, with the amount of lime that is required in order to thereby achieve the desired performance from the use of the dry scrubbing technology. With further regard to the matter of the attempts, which are known to have been made heretodate in an attempt to produce lime from limestone and/or to improve the S0 2 capture characteristics of sorbent for purposes of enhancing the utilization thereof in flue gas desulfurization systems, one such attempt, by way of exemplification and not limitation, is that to which the subject matter of U.S. Patent No. 4,867,955 is directed. U.S. Patent No. 4,867,955 issued on September 1 9, 1 989 and is entitled "Method Of Desulfurizing Combustion Gases". In accordance with the teachings of U.S. Patent No. 4,867,955, there is provided a method of desulfurizing gaseous products of combustion comprising the steps of: burning a sulfur-containing solid fuel within a combustion chamber to produce flyash and combustion gases comprising a sulfurous gas; heating a particulate calcinable compound comprising a compound selected from the group consisting of the carbonates of magnesium, calcium, sodium, and mixtures thereof, in a selected temperature zone within the combustion chamber for a residence time sufficient for calcination of the calcinable compound to its respective oxide, wherein the particle size of the calcinable compound, the selected temperature zone and the residence time are selected to effect calcination of a substantial amount of the calcinable compound to its respective oxide; removing the oxide of the calcinable compound from the combustion chamber; removing the combustion gases from the combustion chamber; and treating the removed combustion gases with the oxide to remove a substantial amount of the sulfurous gas from the combustion gases. Another such attempt, by way of exemplification and not limitation, is that to which U.S. Patent No. 5,006,323 is directed. U.S. Patent No. 5,006,323 issued on April 9, 1 991 and is entitled "Method Of Desulfurizing Combustion Gases". In accordance with the teachings of U.S. Patent No. 5,006,323, there is provided a method of desulfurizing gaseous products of combustion comprising the steps of: burning a sulfur-containing solid fuel within a combustion chamber to produce flyash and combustion gases comprising sulfur dioxide; heating a particulate calcinable compound comprising a compound selected from the group consisting of the carbonates of magnesium, calcium, sodium, and mixtures thereof, in a selected temperature zone within the combustion chamber for a residence time sufficient for calcination of the calcinable compound to its respective oxide, wherein the particle size of the calcinable compound, the selected temperature zone and the residence time are selected to effect calcination of a substantial amount of the calcinable compound to its respective oxide; removing the oxide of the calcinable compound from the combustion chamber; removing the combustion gases from the combustion chamber; forming a slurry comprised of the oxide of the calcinable compound; and treating the removed combustion gases with the slurry to remove a substantial amount of the sulfur dioxide from the combustion gases. A still another such attempt, by way of exemplification and not limitation, is that to which U.S. Patent No. 5,492,685 is directed. U.S. Patent No. 5,492,685 issued on February 20, 1996 and is entitled "High Surface Area Hydrated Lime And Method Of Removing S0 2 From A Gas Stream". In accordance with the teachings of U.S. Patent No. 5,492,685, there is provided: a) a hydrated lime alleged to have superior properties of high surface area, high porosity, and small particle size; b) methods of sorbing S0 2 from waste gas streams using the subject high surface area hydrated lime as a sorbent; and c) controlling the physical properties of the hydrated lime for optimum suitability for use in any one of a variety of dry sorbent injection systems for S0 2 removal. Yet another such attempt, by way of exemplification and not limitation, is that which is described in the technical paper entitled "FGD Experience At Poland's Rybnik Power Station: Dry Method With Humidification", the co-authors of which are: L. Pinko of Energopomiar; J. Chacula of the Rybnik Power Plant; W. Ellison of Ellison Consultants; and J. Podkanski of the Institute of Chemical Engineering, Polish Academy of Sciences. In this technical paper there is described a process wherein limestone is ground, and after being ground this limestone is next blown into a furnace. In the furnace, the limestone is decomposed into calcium oxide and carbon dioxide. This calcium oxide then reacts with S0 2 and thereafter, together with the flue gases and fly ash passes through a system of air reheaters. After these air reheaters, the flue gases are directed to the upper part of a concurrent reactor through a duct that is suitably designed so as to ensure uniform flow of the flue gases, fly ash and sorbent particles. Hydrogenated lime and recycled ash are blown into the duct just before the reactor. In the reactor the flue gases are subjected to humidification and desulfurization. After this humidification and desulfurization thereof, the flue gases, at the bottom of the reactor, are mixed with hot air and directed to electrostatic precipitators. Thereafter, the fly ash and sorbent from the bottom of the reactor, and a part of the fly ash and sorbent from the precipitators are recycled. Yet still another such attempt, by way of exemplification and not limitation, is that which is described in the technical paper entitled "B & W's E-LIDS™ Process-Advanced SO x , Particulate, And Air Toxics Control For The Year 2000", the co-authors of which are Deborah A. Madden and Michael J. Holmes, both of McDermott Technology, Inc. In this technical paper there is described a limestone-based furnace injection/dry scrubbing S0 2 removal process, which comprises the integration of three flue gas cleanup technologies: furnace limestone injection, dry scrubbing, and pulse- jet fabric filtration, which are alleged to be commercially-proven. More specifically, in accordance with the subject process S0 2 removal occurs in the boiler furnace and convection pass, in the dry scrubber, and in the fabric filter. To this end, limestone is pulverized and injected as a dry powder into the flue gases in the upper furnace cavity of the boiler. Upon being so injected, the limestone undergoes calcination to form lime, a portion of which reacts with S0 2 in the flue gases forming calcium sulfate. The flue gases exiting from the boiler are ultimately made to pass through a dry scrubber reactor where these flue gases are contacted by a slurry containing calcium hydroxide. In the dry scrubber, the flue gases are cooled and humidified to conditions near the water saturation temperature. Under these conditions, a portion of the S0 2 in the gas reacts with the calcium hydroxide. Water contained in the slurry droplets evaporates as the droplets pass through the dry scrubber reactor, and the products leave the dry scrubber as a dry powder still suspended in the flue gases. The flue gases then enter a baghouse where coal flyash, spent sorbent and unreacted sorbent particles are collected. The use of a baghouse is alleged to be a key feature because of the additional S0 2 removal the baghouse yields as the flue gases pass through the sorbent-containing filter cake on the filter bags of the baghouse. Upstream of the dry scrubber there is provided a particulate collection device to remove particulate matter from the flue gases. The portion of the solids from the particulate collection device are recycled to a reagent preparation system to produce a calcium hydroxide slurry for the dry scrubber. Thus, although the attempts to which reference has been had hereinbefore allegedly have been demonstrated to be operative for the purpose for which they have been intended, there has nevertheless been evidenced in the prior art a need for a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to desulfurize combustion gases. More specifically, a need has been evidenced in the prior art for a new and improved method of producing S0 2 sorbent in a more efficient manner than that which is currently available through the use of the methods of producing S0 2 sorbent that are presently known in the prior art. Also, more specifically there has been evidenced in the prior art a need for a new and improved method of thereafter utilizing such S0 2 sorbent such that through the use thereof a more optimum desulfurization of combustion gases may be had therewith as compared to that which is currently capable of being realized through the use of the methods for effecting the desulfurization of combustion gases that are presently known in the prior art. It is an object of the present invention to provide a new and improved method of producing S0 2 sorbent in a more efficient manner than that which is currently available through the use of the methods of producing S0 2 sorbent that are presently known in the prior art. It is a further object of the present invention to provide such a new and improved method of producing S0 2 sorbent and of thereafter providing a new and improved method of utilizing such S0 2 sorbent such that through the use thereof a more optimum desulfurization of combustion gases may be had therewith as compared to that which is currently capable of being realized through the use of the methods for effecting the desulfurization of combustion gases that are presently known in the prior art. It is another object of the present invention to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the S0 2 sorbent that is produced from the use of the subject method is limestone particles that have been "deadburned" in order to thereby create therefrom unreactive lime particles. It is still another object of the present invention to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the "deadburning" of the limestone particles is effected by injecting limestone particles, either in the form of coarse grade particles or otherwise, into a conventional solid fuel- fired steam generator such that concomitantly with the generation of steam in the conventional solid fuel-fired steam generator the limestone particles that are injected thereinto are subjected to "deadburning". Another object of the present invention is to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the limestone particles, which are to be subjected to "deadburning" in the conventional solid fuel- fired steam generator, are, unless the limestone particles are already of the desired size, mixed with the solid fuel upstream of a pulverizer for purposes of causing both the limestone particles and the solid fuel to be subjected to pulverization in the pulverizer. A still another object of the present invention is to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the limestone particles that are to be subjected to "deadburning" in the conventional solid fuel-fired steam generator, if not previously mixed with the solid fuel upstream of the pulverizer, are then either caused to be mixed with the solid fuel downstream of the pulverizer and are injected into the conventional solid fuel-fired steam generator in the form of a mixture of limestone particles and solid fuel, or the limestone particles and the solid fuel are each injected separately into the conventional solid fuel-fired steam generator. A further object of the present invention is to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the limestone particles, which are subjected to "deadburning" in the conventional solid fuel-fired steam generator concomitantly with the generation of steam in the conventional solid fuel-fired steam generator, are made to follow a particular path through the conventional solid fuel-fired steam generator so as to avoid a mixing of the limestone particles with sulfur in the conventional solid fuel- fired steam generator. A still further object of the present invention is to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the unreactive lime particles that have been created from the "deadburning" of the limestone particles in the conventional solid fuel-fired steam generator are, after leaving the conventional solid fuel-fired steam generator, separated in a precoliection device from the combustion gases and the finer solid fuel ash, both of which are generated as a result of the combustion of the solid fuel within the conventional solid fuel-fired steam generator. Yet an object of the present invention is to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the separated unreactive lime particles downstream of the precoliection device are reactivated by being subjected to hydration. Yet another object of the present invention is to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the previously unreactive lime particles that have now been reactivated are then utilized in a flue gas desulfurization device for the purpose of effecting therewith the desulfurization of the combustion gases generated as a result of the combustion of the solid fuel in the conventional solid fuel-fired steam generator. Yet still another object of the present invention is to provide such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that it is relatively easy to implement, relatively simple to employ, yet is relatively inexpensive to provide. SUMMARY OF THE PRESENT INVENTION In accordance with the present invention there is provided a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases. The subject method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases comprises the following steps. Limestone particles are provided in the form of coarse grade particles or otherwise. These limestone particles are either mixed with solid fuel upstream of a pulverizer for purposes of causing both the limestone particles and the solid fuel to be subjected to pulverization in the pulverizer, or if the limestone particles are already of the desired size the limestone particles are either caused to be mixed with the solid fuel downstream of the pulverizer or are caused to remain separate from the solid fuel. These limestone particles and the solid fuel are either injected into a conventional solid fuel-fired steam generator in the form of a mixture, or the limestone particles and the solid fuel are each injected separately into the conventional solid fuel-fired steam generator. Concomitantly with the generation of steam in the conventional solid fuel-fired steam generator these limestone particles are subjected to "deadburning" in the conventional solid fuel-fired steam generator thereby creating unreactive lime particles therefrom. Concomitantly with the generation of steam in the conventional solid fuel-fired steam generator these limestone particles while being subjected to "deadburning" therewithin are made to follow a particular path through the conventional solid fuel-fired steam generator so as to avoid mixing of these limestone particles with sulfur in the conventional solid fuel- fired steam generator. After leaving the conventional solid fuel-fired steam generator, the unreactive lime particles that have been created from the "deadburning" of the limestone particles in the conventional solid fuel-fired steam generator are separated in a precoliection device from the combustion gases and the finer solid fuel ash, both of which are generated as a result of the combustion of the solid fuel within the conventional solid fuel-fired steam generator. Downstream of the precoliection device the separated unreactive lime particles are reactivated by being subjected to hydration. Following the reactivation thereof, the previously unreactive lime particles, which have now been reactivated, are then utilized in a flue gas desulfurization device for the purpose of effecting therewith the desulfurization of the combustion gases generated as a result of the combustion of the solid fuel in the conventional solid fuel-fired steam generator. Particularly noteworthy with regard to the subject method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases of the present invention is the fact that heretodate, i.e., prior to the present invention, it had been believed that if limestone was "calcined" in a furnace at too high a temperature, the lime created therefrom would become "deadburned" and, thereafter, unreactive, thus making such lime, which was "deadburned", unsuitable for the desulfurization of combustion gases, i.e., unsuitable for flue gas desulfurization uses. As such, in accordance with the teachings of the prior art, for purposes of the "calcination" thereof in a furnace steps were intentionally taken to ensure that the limestone, which was to be "calcined", would be injected into the furnace at a location whereat both the temperature was low enough to ensure that "deadburning" of the limestone would be avoided and that after the injection of the limestone into the furnace the residence time of the limestone therein would be insufficient to cause such limestone to become "deadburned". This is in sharp contrast to, i.e., is the exact opposite of, the teachings of the present invention wherein the limestone, which is injected into a conventional solid fuel-fired steam generator, is purposely injected thereinto so as to ensure the "deadburning" thereof. Namely, such limestone is deliberately injected into a conventional solid fuel-fired steam generator at a location whereat the temperature is above that which is considered by the prior art to be suitable for "calcination" of limestone and whereat the residence time of the limestone within the conventional solid fuel-fired steam generator exceeds that which is considered by the prior art to be suitable for "calcination" of limestone. BRIEF DESCRIPTION OF THE DRAWINGS Figure 1 is a diagrammatic representation in the nature of a vertical sectional view of a conventional solid fuel-fired steam generator of suitable construction such that limestone particles are capable of being injected thereinto for the purposes of being subjected, concomitantly with the generation of steam within the conventional solid fuel-fired steam generator, to "deadburning" thereby creating unreactive lime particles therefrom in accordance with the method of the present invention; Figure 2 is a diagrammatic representation of a conventional solid fuel-fired steam generator of the type shown in Figure 1 illustrated cooperatively associated with an air heater, a particulate collection device, a stack and a first embodiment of a precoliection device, which are employable in the practice of certain aspects of the method of the present invention; Figure 3 is a diagrammatic representation of a conventional solid fuel-fired steam generator of the type shown in Figure 1 illustrated cooperatively associated with an air heater, a particulate collection device, a stack and a second embodiment of a precoliection device, which are employable in the practice of certain aspects of the method of the present invention; and Figure 4 is a schematic representation of the steps that collectively comprise the method of the present invention. DESCRIPTION OF THE PREFERRED EMBODIMENT Referring now to the drawing, and more particularly to Figure 1 thereof, there is depicted therein a conventional solid fuel-fired steam generator, generally designated by reference numeral 10. Inasmuch as the nature of the construction and the mode of operation of conventional solid fuel-fired steam generators per se are well-known to those skilled in the art, it is not deemed necessary, therefore, to set forth herein a detailed description of the conventional solid fuel-fired steam generator 10 of Figure 1 . Rather, for purposes of obtaining an understanding of a conventional solid fuel-fired steam generator 10, which is capable of being employed in connection with the practice of the method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent for the purpose of effecting therewith the desulfurization of combustion gases in accordance with the present invention, it is deemed to be sufficient that there be presented herein merely a description of the nature of the components of the aforesaid conventional solid fuel-fired steam generator 10, which are made use of in connection with the practice of the method of the present invention. For a more detailed description of the nature of the construction and the mode of operation of the components of the conventional solid fuel-fired steam generator 10, which are not described herein, one may have reference to the prior art, e.g., U.S. Patent No. 4,719,587, which issued January 12, 1988 to F. J. Berte and which is assigned to the same assignee as the present patent application. Referring further to Figure 1 of the drawing, the conventional solid fuel-fired steam generator 10 as illustrated therein includes a burner region, generally designated by the reference numeral 12. As will be described more fully hereinafter, it is within the burner region 12 of the conventional solid fuel-fired steam generator 10 that in a manner well-known to those skilled in this art combustion of the pulverized solid fuel and air is initiated. The hot gases that are produced from combustion of the pulverized solid fuel and air rise upwardly in the conventional solid fuel-fired steam generator 10. During the upwardly movement thereof in the conventional solid fuel-fired steam generator 10, the hot gases in a manner well-known to those skilled in this art give up heat to the fluid passing through the tubes (not shown in the interest of maintaining clarity of illustration in the drawing) that in known fashion line all four of the walls of the conventional solid fuel- fired steam generator 10. Then, the hot gases exit the conventional solid fuel-fired steam generator 10 through the horizontal pass, generally designated by the reference numeral 14, of the conventional solid fuel-fired steam generator 10, which in turn leads to the rear gas pass, generally designated by the reference numeral 16, of the conventional solid fuel-fired steam generator 10. Although not shown in Figure 1 of the drawing in the interest of maintaining clarity of illustration therein, both the horizontal pass 14 and the rear gas pass 1 6 as seen with reference to Figures 2 and 3 of the drawing commonly contain other heat exchange surface, generally designated in each of Figures 2 and 3 of the drawing by the same reference numeral 18, for generating and superheating steam, in a manner well-known to those skilled in this art. Thereafter, the steam commonly is made to flow to a turbine (not shown), which forms one component of a turbine/generator set (not shown), such that the steam provides the motive power to drive the turbine (not shown) and thereby also the generator (not shown), which in known fashion is cooperatively associated with the turbine, such that electricity is thus produced from the generator (not shown). Continuing with the description of the conventional solid fuel- fired steam generator 1 0, as best understood with reference to Figure 1 of the drawing the conventional solid fuel-fire steam generator 10 includes a plurality of housings, each preferably in the form of a main windbox, denoted generally in the drawing by the reference numeral 20. Each of the main windboxes 20 in a manner well-known to those skilled in this art is supported by suitable support means (not shown) in the burner region 1 2 of the conventional solid fuel-fired steam generator 10 such that the longitudinal axis of each of the main windboxes 20 extends substantially in parallel relation to the longitudinal axis of the conventional solid fuel-fired steam generator 10. In known fashion each of the main windboxes 20 includes a plurality of air compartments (not shown in the interest of maintaining clarity of illustration in the drawing) and a plurality of fuel compartments (not shown in the interest of maintaining clarity of illustration in the drawing), preferably arranged in interposed relation with each other. Moreover, an air nozzle (not shown) is supported in mounted relation within each of the air compartments (not shown) such as to be operative for purposes of effecting therewith the injection of the air required for combustion into the burner region 1 2 of the conventional solid fuel-fired steam generator 10. Similarly, a fuel nozzle (not shown) is supported in mounted relation within each of the fuel compartments (not shown) such as to be operative for purposes of effecting therewith the injection into the burner region 12 of the conventional solid fuel-fired steam generator 10 of the solid fuel that is to be combusted therewithin. For a more detailed description of the nature of the construction and the mode of operation of the main windboxes 20, which has not been described herein, one may have reference to the prior art, e.g., U.S. Patent No. 5,31 5,939, which issued May 31 , 1 994 to M. J. Rini et al. and which is assigned to the same assignee as the present patent application. With further regard to the main windboxes 20 of the conventional solid fuel-fired steam generator 10, an air supply means (not shown in the interest of maintaining clarity of illustration in the drawing) is operatively connected to each of the plurality of air compartments (not shown) and more specifically to the air nozzles (not shown), which are supported in mounted relation within the air compartments (not shown) whereby the air supply means (not shown) supplies air thereto and therethrough into the burner region 1 2 of the conventional solid fuel-fired steam generator 10. To this end, the air supply means (not shown) in known fashion includes a fan (not shown) and air ducts (not shown), which are connected in fluid flow relation to the fan (not shown) on the one hand and to the air nozzles (not shown), which are supported in mounted relation within the air compartments (not shown), on the other hand, through separate valves and controls (not shown). Similarly, a pulverized solid fuel supply means, which is illustrated schematically in Figure 1 of the drawing wherein the pulverized solid fuel supply means is denoted generally by the reference numeral 22, is operatively connected to the fuel nozzles (not shown), which are supported in mounted relation within the fuel compartments (not shown), whereby the pulverized solid fuel supply means 22 supplies pulverized solid fuel to the fuel compartments (not shown), and more specifically to the fuel nozzles (not shown) supported in mounted relation therewithin for injection therefrom into the burner region 12 of the conventional solid fuel-fired steam generator 10. To this end, the pulverized solid fuel supply means 22 includes a pulverizer, denoted generally in the drawings by the reference numeral 24, and the pulverized solid fuel ducts, denoted by the reference numeral 26. The pulverizer 24 in a manner well- known to those skilled in the art produces pulverized solid fuel of the desired fineness. Although not shown in the interest of maintaining clarity of illustration in the drawing, the pulverizer 24 is operatively connected to the fan (not shown) of the air supply means (not shown), to which reference has been had hereinbefore, such that air is also supplied from the fan (not shown) of the air supply means (not shown) to the pulverizer 24 whereby the pulverized solid fuel supplied from the pulverizer 24 to the fuel nozzles (not shown) supported in mounted relation within the fuel compartments (not shown) is transported through the pulverized solid fuel ducts 26 in an air stream in a manner, which is well-known to those skilled in the art of pulverization. There will next be set forth herein a description of the manner in which the limestone particles, which are to be subjected to "deadburning" for purposes of creating unreactive lime particles therefrom, are injected into the conventional solid fuel-fired steam generator 10. To this end, as best understood with reference to Figure 1 of the drawing, the conventional solid fuel-fired steam generator 10 in accordance with the present invention has a limestone particle supply means, generally designated by the reference numeral 28, cooperatively associated therewith. The limestone particle supply means 28 includes a suitable storage means, generally designated by the reference numeral 30, from which the limestone particles are preferably supplied, and duct means, denoted by the reference numeral 32, by means of which the limestone particles are transported from the storage means 30 to the desired location. In accordance with the present invention the limestone particles, which are to be injected into the conventional solid fuel-fired steam generator 10 for purposes of effecting therewithin the subjection thereof to "deadburning" for purposes of creating unreactive lime particles therefrom, can be made to follow any one of several different paths in going from the storage means 30 to the point of injection thereof into the conventional solid fuel-fired steam generator 10. Namely, unless the limestone particles that are to be injected into the conventional solid fuel-fired steam generator 10 are already of the desired size, the limestone particles may be mixed with the solid fuel upstream of the pulverizer 24, i.e., the limestone particles, which are not already of the desired size, may, as illustrated by means of solid lines in Figure 1 , be made to flow from the storage means 30 through the duct means 32 to a point, identified in Figure 1 by the reference numeral 34, whereat the limestone particles are made to join with the solid fuel, which as depicted by the arrow that is denoted in Figure 1 by the reference numeral 36 is being supplied to the pulverizer 24. As a result of such joining of the limestone particles with the solid fuel upstream of the pulverizer 24, both the limestone particles and the solid fuel are subjected to pulverization in the pulverizer 24 such that upon leaving the pulverizer 24 both the limestone particles and the solid fuel will be made to embody the fineness desired thereof. On the other hand, if the limestone particles are already of the desired size, the limestone particles, which are to be subjected to "deadburning" in the conventional solid fuel-fired steam generator 10 so as to thereby create unreactive lime particles therefrom, either may be caused to be mixed with the solid fuel downstream of the pulverizer 24, i.e., may be made to flow from the storage means 30 through the duct means 32', the latter being denoted in dotted lines in Figure 1 , to a point identified in Figure 1 by the reference numeral 38 whereat the limestone particles are made to join with the solid fuel, which has undergone pulverization in the pulverizer 24. Or, the limestone particles, which are already of the desired size may, as depicted by the dotted line denoted in Figure 1 by the reference numeral 32", be made to flow from the storage means 30 directly to the conventional solid fuel-fired steam generator 10 such that the limestone particles and the solid fuel are each injected separately into the conventional solid fuel-fired steam generator 10. As will be readily apparent from a reference to Figure 1 of the drawing, regardless of the path that the limestone particles may follow for purposes of being injected into the conventional solid fuel-fired steam generator 10 in order to thereby be subjected to "deadburning" whereby to create unreactive lime particles therefrom, the limestone particles in each case are injected into the conventional solid fuel-fired steam generator 10 such that the limestone particles are exposed to the highest temperatures that are present in the conventional solid fuel-fired steam generator 10. Namely, it is into the burner region 12 of the conventional solid fuel-fired steam generator 10, which as is well-known to those skilled in the art is where the highest temperatures exist within the conventional solid fuel-fired steam generator 10, that the limestone particles are injected regardless of the path that the limestone particles follow after leaving the storage means 30. In addition, since the burner region 1 2 is located, relatively speaking, at the bottom of the conventional solid fuel-fired steam generator 10, the limestone particles by virtue of being injected thereinto, regardless of the path that the limestone particles may follow before being injected thereinto, are also subjected to the greatest residence time within the conventional solid fuel- fired steam generator 10. Finally, mention is made here of the fact that since in terms of the relative density thereof the limestone particles generally are less dense than the solid fuel, the path of flow that the limestone particles and after the "deadburning" thereof the unreactive lime particles thereafter follow naturally in traversing the interior of the conventional solid fuel-fired steam generator 10 is different than the path of flow, which the solid fuel naturally follows in traversing the interior of the conventional solid fuel-fired steam generator 10. As a consequence of this inherent tendency for the limestone particles and the solid fuel to follow different flow paths within the conventional solid fuel-fired steam generator 10, mixing of the limestone particles with sulfur, which originates with the solid fuel, is avoided in the conventional solid fuel-fired steam generator 10. Moreover, once the unreactive lime particles are created from the limestone particles due to the "deadburning" of the latter, any mixing of such unreactive lime particles with sulfur will essentially be to no avail, i.e., essentially no sulfur capture will be effected by the unreactive lime particles by virtue of the unreactive nature of such lime particles. Consideration will next be had herein to Figures 2 and 3 of the drawings. To this end, in each of Figures 2 and 3 of the drawings, there is illustrated a conventional solid fuel-fired steam generator of the same type as the conventional solid fuel-fired steam generator 10, which is depicted in Figure 1 of the drawings. For ease of subsequent reference thereto, the conventional soiid fuel-fired steam generators that are depicted in Figures 2 and 3 of the drawings are each denoted generally by the same reference numeral 10'. With further regard to Figures 2 and 3 of the drawings, as will be readily apparent therefrom the conventional solid fuel-fired steam generator 10' is depicted therein as being cooperatively associated with a conventional air heater, denoted generally in each of Figures 2 and 3 by the reference numeral 40, and a conventional particulate collection device, denoted generally in each of Figures 2 and 3 by the reference numeral 42, and a conventional stack, denoted generally in each of Figures 2 and 3 by the reference numeral 44, and a particular form of precoliection device to which further reference will be had hereinafter. In a manner well-known to those skilled in the art, the combustion gases, which are generated from the combustion of solid fuel within the conventional solid fuel-fired steam generator 10', after leaving the rear gas pass 1 6 of the conventional solid fuel-fired steam generator 10' are made to flow to and through the conventional air heater 40. While flowing through the conventional air heater 40, in known fashion a heat transfer is effected between the hot combustion gases flowing thereto from the rear gas pass 1 6 of the conventional solid fuel-fired steam generator 10' and incoming air that is made to flow through the conventional solid fuel-fired steam generator 10' in the course of being supplied to the conventional solid fuel- fired steam generator 1 0' whereby the hot combustion gases while traversing the conventional air heater 40 give up heat to the incoming air such that the hot combustion gases as a consequence thereof are cooled while the incoming air is heated. From the conventional air heater 40, the combustion gases, as will be readily apparent from a reference to Figures 2 and 3 of the drawings, are made to flow to and through a particular type of precoliection device for a purpose, which will be described herein subsequently. Thereafter, these combustion gases are made to flow to and through a conventional particulate collection device 42. The conventional particulate collection device 42 may be in the form of any conventional type of device suitable for use for purposes of effecting therewith the removal of particulates from combustion gases such as, for example, an electrostatic precipitator, a baghouse, etc., each of which is known in the prior art to be commonly employed for such a purpose. To this end, the conventional particulate collection device 42 in a manner well-known to those skilled in the art is designed to be operative to effect therewith the removal of particulates, which are entrained in the combustion gases, as the combustion gases traverse the conventional particulate collection device 42. The particulates, which are removed from the combustion gases as the combustion gases traverse the conventional particulate collection device 42, are collected and are discharged for the suitable disposal thereof from the conventional particulate collection device 42 through suitable discharge means, identified in Figures 2 and 3 by the reference numeral 46, with which the particulate collection device 42 is suitably provided for this purpose. Once the particulates have been removed from the combustion gases in the conventional particulate collection device 42, the combustion gases are then made to flow to the conventional stack 44 from whence the combustion gases are then discharged to the atmosphere. With further reference to Figures 2 and 3 of the drawings, a description will next be had herein of the precoliection device, which is depicted in each of Figures 2 and 3. To this end, in Figure 2 of the drawings there is depicted a first embodiment of a precoliection device, denoted generally therein by the reference numeral 48. As best understood with reference to Figure 2, the precoliection device 48 is interposed in fluid flow relation between the conventional air heater 40 and the conventional particulate collection device 42. The precoliection device 48 is designed to be operative to effect the separation from the combustion gases of the unreactive lime particles, which have been created from the limestone particles that have been subjected to "deadburning", as the combustion gases are made to flow to and through the precoliection device 48 in the course of their flow from the conventional air heater 40 to the conventional particulate collection device 42. In accordance with the illustration thereof in Figure 2 of the drawings, the first embodiment of precoliection device, i.e., the precoliection device 48, is of the louver type. However, as best understood with reference to Figure 3 of the drawings wherein there is illustrated a second embodiment of precoliection device, i.e., the precoliection device denoted generally therein by the reference numeral 50, rather than being of the louver type as illustrated in Figure 2 of the drawings may, without departing from the essence of the present invention, be of the cyclone type as is the second embodiment of precoliection device, i.e., the precoliection device 50, which is illustrated in Figure 3 of the drawings. There are several advantages to be derived from the utilization, in accordance with the present invention, of a precoliection device, be it the precoliection device 48 that is illustrated in Figure 2 of the drawings or the precoliection device 50 that is illustrated in Figure 3 of the drawings. Namely, by effecting the separation in the precoliection device 48 of Figure 2 or the precoliection device 50 of Figure 3 of the unreactive lime particles, which have been created from the limestone particles that have been subjected to "deadburning", from the combustion gases as the combustion gases are made to traverse either the precoliection device 48 or the precoliection device 50, a process flow is enabled to be formed in this way. Moreover, this process flow consists mainly of unreactive lime particles, which as will be described herein more fully subsequently, may be subjected to hydration for purposes of effecting the reactivation thereof and after being so reactivated may then be utilized in a suitable type of flue gas desulfurization device for purposes of effecting therewith sulfur capture such as to thereby accomplish the desulfurization of combustion gases. The advantages of creating in the aforedescribed manner a separate process flow of the unreactive lime particles is that the reactivation of the unreactive lime particles can be particularly optimized without the necessity of having to handle large amounts of solid fuel ash with which the unreactive lime particles would otherwise be entrained in the combustion gases. In addition, it also makes it possible to effect control over the ratio of lime particles to ash and thus the relative recirculation ratios of lime particles to the flue gas desulfurization devices. Without the creation of such a separate process flow of the lime particles, the ratio of lime particles to ash would be solely determined by the amount of ash that was entrained in the combustion gases, which could be large or small depending on the specific characteristics of the particular type of solid fuel being combusted. As such, it would not be possible to effect control of the relative recirculation ratios of the lime particles to the flue gas desulfurization devices. A description will next be had herein of the steps that collectively comprise the method of the present invention. For this purpose, reference will be had in particular to Figure 4 of the drawings wherein there is illustrated a schematic representation of the steps that collectively comprise the method of the present invention. More specifically, as best understood with reference to Figure 4 of the drawings air, solid fuel and limestone particles, as indicated by the arrow identified in Figure 4 by the reference numeral 52 are injected into a conventional soiid fuel-fired steam generator, which for purpose of this discussion is deemed to be the conventional solid fuel-fired steam generator 10 that is illustrated in Figure 1 of the drawings. From the conventional solid fuel-fired steam generator 10, the pollutant- bearing combustion gases, which have been generated as a consequence of the combustion of the soiid fuel and air within the conventional solid fuel- fired steam generator 10 and in which the unreactive lime particles that have been created from the subjection of the limestone particles to "deadburning" in the conventional soiid fuel-fired steam generator 10, are made to flow to a precoliection device, which for purpose of this discussion is deemed to be the precoliection device 48 that is illustrated in Figure 2 of the drawings. The precoliection device 48 is operative to establish a separate process flow consisting mainly of unreactive lime particles. From the precoliection device 48, this separate process flow as indicated by the arrow identified by the reference numeral 56 in Figure 4 of the drawings is made to flow to a conventional form of hydration means, denoted generally in Figure 4 by the reference numeral 58, whereas the pollutant-bearing combustion gases from which the separate process flow consisting mainly of unreactive lime particles has been established in the precoliection device 48 is made to flow as indicated by the arrow identified in Figure 4 by the reference numeral 60 to flue gas desulfurization means, denoted generally by the reference numeral 62 in Figure 4. The hydration means 58 may take the form of any conventional form of hydration means that is suitable for effecting therein the reactivation of the unreactive lime particles that have been created from the limestone particles that have been subjected to "deadburning" in the conventional solid fuel-fired steam generator 10. Following the reactivation thereof in the hydration means 58, the reactivated lime particles as indicated by the arrow identified in Figure 4 by the reference numeral 64 are reinjected into the pollutant-bearing combustion gases at a point upstream of the flue gas desulfurization means 62 such that sulfur capture may be effected therewith in the flue gas desulfurization means 62. In accordance with the present invention, the flue gas desulfurization means 62 may comprise either a conventional form of dry flue gas desulfurization device or a conventional form of wet flue gas desulfurization device. From the flue gas desulfurization means 62, the pollutant-bearing solids, as indicated by the arrow identified in Figure 4 by the reference numeral 66 are discharged for suitable disposal thereof from the flue gas desulfurization means 62, whereas the remaining combustion gases, as indicated by the arrow identified by the reference numeral 68 are made to flow to the particulate collection device 42. Within the particulate collection device 42, the particulates that remain entrained in the remaining combustion gases are removed therefrom. After removal from the remaining combustion gases in the particulate collection device 42, the removed particulates, as indicated by the arrow identified in Figure 4 by the reference numeral 70, are discharged for suitable disposal thereof from the particulate collection device 42, whereas the now cleaned combustion gases, as indicated by the arrow identified in Figure 4 by the reference numeral 72 are made to flow to the stack 44 from whence the clean combustion gases are then discharged to the atmosphere. Thus, in accordance with the present invention there has been provided a new and improved method of producing S0 2 in a more efficient manner than that which is currently available through the use of the methods of producing S0 2 sorbent that are presently known in the prior art. Besides, there has been provided in accord with the present invention a new and improved method of producing S0 2 sorbent and of thereafter providing a new and improved method of utilizing such S0 2 sorbent such that through the use thereof a more optimum desulfurization of combustion gases may be had therewith as compared to that which is currently capable of being realized through the use of the methods for effecting the desulfurization of combustion gases that are presently known in the prior art. As well, in accordance with the present invention there has been provided such a new and improved method of producing S0 2 sorbent and of effecting therewith the desulfurization of combustion gases, which is characterized in that the S0 2 sorbent that is produced from the use of the subject method is limestone particles that have been "deadburned" in order to thereby create unreactive lime particles therefrom. Moreover, there has been provided in accord with the present invention such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the "deadburning" of the limestone particles is effected by injecting limestone particles, either in the form of coarse grade particles or otherwise, into a conventional solid fuel-fired steam generator such that concomitantly with the generation of steam in the conventional solid fuel-fired steam generator the limestone particles that are injected thereinto are subjected to "deadburning". Also, in accordance with the present invention there has been provided such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the limestone particles, which are to be subjected to "deadburning" in the conventional solid fuel-fired steam generator, are, uniess the limestone particles are already of the desired size, mixed with the solid fuel upstream of a pulverizer for purposes of causing both the limestone particles and the solid fuel to be subjected to pulverization in the pulverizer. Further, there has been provided in accord with the present invention such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the limestone particles that are to be subjected to "deadburning" in the conventional solid fuel-fired steam generator, if not previously mixed with the solid fuel upstream of the pulverizer, are then either caused to be mixed with the solid fuel downstream of the pulverizer and are injected into the conventional solid fuel-fired steam generator in the form of a mixture of limestone particles and solid fuel, or the limestone particles and the solid fuel are each injected separately into the conventional solid fuel-fired steam generator. In addition, in accordance with the present invention there has been provided such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the limestone particles, which are subjected to "deadburning" in the conventional solid fuel-fired steam generator concomitantly with the generation of steam in the conventional solid fuel-fired steam generator, are made to follow a particular path through the conventional solid fuel-fired steam generator so as to avoid a mixing of the limestone particles with sulfur in the conventional solid fuel-fired steam generator. Furthermore, there has been provided in accord with the present invention such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the unreactive lime particles that have been created from the "deadburning" of the limestone particles in the conventional solid fuel-fired steam generator are, after leaving the conventional solid fuel-fired steam generator, separated in a precoliection device from the combustion gases and the finer solid fuel ash, both of which are generated as a result of the combustion of the solid fuel within the conventional solid fuel-fired steam generator. Additionally, in accordance with the present invention there has been provided such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the separated unreactive lime particles downstream of the precoliection device are reactivated by being subjected to hydration. Penultimately, there has been provided such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that the previously unreactive lime particles that have now been reactivated are then utilized in a flue gas desulfurization device for the purpose of effecting therewith the desulfurization of the combustion gases generated as a result of the combustion of the soiid fuel in the conventional solid fuel-fired steam generator. Finally, in accordance with the present invention there has been provided such a new and improved method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases, which is characterized in that it is relatively easy to implement, relatively simple to employ, yet is relatively inexpensive to provide. While several embodiments of our invention have been shown, it will be appreciated that modifications thereof, some of which have been alluded to hereinabove, may still be readily made thereto by those skilled in the art. We, therefore, intend by the appended claims to cover the modifications alluded to herein as well as all the other modifications which fall within the true spirit and scope of our invention.

Claims: What is claimed is: 1 . A method of producing S0 2 sorbent and of thereafter utilizing such S0 2 sorbent to effect therewith the desulfurization of combustion gases comprising the steps of: a. providing a solid fuel-fired steam generator having a burner region; b. injecting solid fuel and combustion air into the burner region of the solid fuel-fired steam generator; c. effecting the combustion of the solid fuel and of the combustion air within the burner region of the solid fuel-fired steam generator to produce therefrom combustion gases; d. effecting the production of steam through a heat transfer from the combustion gases as the combustion gases flow through the soiid fuel-fired steam generator; e. injecting limestone particles into the burner region of the solid fuel-fired steam generator; f. subjecting within the solid fuel-fired steam generator concomitantly with the production of steam therein the limestone particles to "deadburning" thereby creating unreactive lime particles therefrom; g. effecting the flow of the combustion gases produced from the combustion of the solid fuel and of the combustion air within the burner region of the soiid fuel-fired steam generator and the flow of the unreactive lime particles created from the "deadburning" of the limestone particles within the burner region of the solid fuel-fired steam generator from the solid fuel-fired steam generator to a precoliection device; h. effecting within the precoliection device the separation of the unreactive lime particles from the combustion gases to produce a separate process flow consisting mainly of unreactive lime particles; i. effecting the flow of the separate process flow consisting mainly of unreactive lime particles from the precoliection device to a hydration device; j. effecting the reactivation of the unreactive lime particles within the hydration device thereby creating reactive lime particles therefrom by subjecting the unreactive lime particles to hydration within the hydration device; k. effecting the flow of the combustion gases from the precoliection device to a flue gas desulfurization device; I. effecting the flow of the reactive lime particles from the hydration device into the flow path of the combustion gases and therewith to the flue gas desulfurization device; and m. effecting within the flue gas desulfurization device the desulfurization of the combustion gases with the reactive lime particles. 2. The method as set forth in Claim 1 wherein the limestone particles injected into the burner region of the solid fuel-fired steam generator are of coarse grade. 3. The method as set forth in Claim 1 further comprising the step of effecting the pulverization of the solid fuel in a pulverizer prior to the injection of the soiid fuel into the burner region of the soiid fuel-fired steam generator. 4. The method as set forth in Claim 3 further comprising the step of mixing the limestone particles prior to the injection thereof into the burner region of the solid fuel-fired steam generator with the soiid fuel upstream of the pulverizer in order to thereby cause both the limestone particles and the solid fuel to be subjected to pulverization in the pulverizer. 5. The method as set forth in Claim 3 further comprising the step of mixing the limestone particles prior to the injection thereof into the burner region of the solid fuel-fired steam generator with the solid fuel downstream of the pulverizer in order to thereby cause the limestone particles and the solid fuel to be injected into the burner region of the solid fuel-fired steam generator as a mixture. 6. The method as set forth in Claim 1 wherein the precoliection device embodies a plurality of louvers and the separation of the unreactive lime particles from the combustion gases is effected within the precoliection device by causing the unreactive lime particles and the combustion gases to flow through the plurality of louvers. 7. The method as set forth in Claim 1 wherein the precoliection device comprises a cyclone and the separation of the unreactive lime particles from the combustion gases is effected within the precoliection device by causing the unreactive lime particles and the combustion gases to flow through the cyclone. 8. The method as set forth in Claim 1 wherein a dry flue gas desulfurization process is employed to effect the desulfurization of the combustion gases with the reactive lime particles. 9. The method as set forth in Claim 1 wherein a wet flue gas desulfurization process is employed to effect the desulfurization of the combustion gases with the reactive lime particles. 10. The method as set forth in Claim 1 further comprising the step of effecting the flow of the combustion gases from the flue gas desulfurization device to a particulate collection device. 1 1 . The method as set forth in Claim 10 further comprising the step of effecting within the particulate collection device the separation of particulates from the combustion gases. 12. The method as set forth in Claim 1 1 further comprising the step of effecting the discharge from the particulate collection device of the particulates separated therein from the combustion gases. 1 3. The method as set forth in Claim 1 2 further comprising the step of effecting the flow of the combustion gases from the particulate collection device to a stack. 14. The method as set forth in Claim 1 3 further comprising the step of effecting the discharge of the combustion gases from the stack to the atmosphere.

Inventors: AHMAN STEFAN OSCAR HUGO, ANDRUS HERBERT ELLIOT JR, MCCARTNEY MICHAEL SCOTT, PORLE KJELL ERIK GUSTAF, STROMBERG PETER TOBIAS, AHMAN, STEFAN, OSCAR, HUGO, ANDRUS, HERBERT, ELLIOT, JR., MCCARTNEY, MICHAEL, SCOTT, PORLE, KJELL, ERIK, GUSTAF, STROMBERG, PETER, TOBIAS
Applicants: COMBUSTION ENG, COMBUSTION ENGINEERING, INC.
Application year: 1999
Main classification: B01D53
IPC codes: B01D53