US3625164A - Combustion of high-sulfur coal in a fluidized bed reactor - Google Patents
Combustion of high-sulfur coal in a fluidized bed reactor Download PDFInfo
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- US3625164A US3625164A US135981A US3625164DA US3625164A US 3625164 A US3625164 A US 3625164A US 135981 A US135981 A US 135981A US 3625164D A US3625164D A US 3625164DA US 3625164 A US3625164 A US 3625164A
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- 239000003245 coal Substances 0.000 title claims abstract description 58
- 238000002485 combustion reaction Methods 0.000 title claims abstract description 41
- 239000011593 sulfur Substances 0.000 title abstract description 38
- 229910052717 sulfur Inorganic materials 0.000 title abstract description 38
- 238000002309 gasification Methods 0.000 claims abstract description 37
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- 238000000034 method Methods 0.000 claims description 41
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- 238000010438 heat treatment Methods 0.000 abstract description 3
- 238000007796 conventional method Methods 0.000 abstract description 2
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- 239000000203 mixture Substances 0.000 description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 8
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- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 3
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 3
- 229910000019 calcium carbonate Inorganic materials 0.000 description 3
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- 239000000370 acceptor Substances 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- 229910052791 calcium Inorganic materials 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- YAECNLICDQSIKA-UHFFFAOYSA-L calcium;sulfanide Chemical compound [SH-].[SH-].[Ca+2] YAECNLICDQSIKA-UHFFFAOYSA-L 0.000 description 2
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- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 238000006477 desulfuration reaction Methods 0.000 description 2
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- 229910052760 oxygen Inorganic materials 0.000 description 2
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- 150000003464 sulfur compounds Chemical class 0.000 description 2
- 229910001018 Cast iron Inorganic materials 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
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- 229910052918 calcium silicate Inorganic materials 0.000 description 1
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical compound [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 description 1
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- VYMDGNCVAMGZFE-UHFFFAOYSA-N phenylbutazonum Chemical compound O=C1C(CCCC)C(=O)N(C=2C=CC=CC=2)N1C1=CC=CC=C1 VYMDGNCVAMGZFE-UHFFFAOYSA-N 0.000 description 1
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Images
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C10/00—Fluidised bed combustion apparatus
- F23C10/002—Fluidised bed combustion apparatus for pulverulent solid fuel
Definitions
- Primary air which is also the fluidizing medium, enters the gasification zone through the grate.
- the zone is operated adiabatically, under reducing conditions, to yield CaS and an effluent rich in CO.
- the C215 is discharged from the gasification zone by the moving grate and the gaseous effluent, containing entrained desulfurized coal fines, enters the combustion zone where secondary air is added.
- the exotherm of combustion is retrieved in the heat recovery zone, using conventional techniques.
- the flue gas from the reactor contains little sulfur dioxide to pollute the environment.
- the Gas may be processed in several ways to recover elemental sulfur.
- this invention relates to the desulfurization of coal. More particularly, it pertains to a process for the combustion of sulfur-containing coal wherein the sulfur is removed as calcium sulfide and the flue gas, consequently, contains minimal S0,.
- sulfur-containing coal is treated in a two-stage process which minimizes evolution of volatile sulfur compounds.
- sulfur-containing coal is reacted with CaO in a fluid bed gasifier, which operates adiabatically under reducing conditions, to yield CaS and a gas rich in CO.
- the second stage is a conventional boiler in which the off-gas from the first stage and the coal fines entrained therein are delivered to the boiler as fuel. Flue gas from this boiler contains substantially no sulfur dioxide as a pollutant. CaS is withdrawn from the first stage as a valuable byproduct.
- the prior art relative to coal gasification discloses the concept of supporting a fluidized bed on a continuous foraminous moving grate through which the fluidizing gas enters the bed.
- the grate is divided into sections so that air flow can be balanced to compensate for varying bed depth.
- Such a structure is shown, for example, Godel U.S. Pat. Nos. 2,866,696 and 3,302,597.
- the first zone is a fluidized bed gasification zone, wherein the bed is preferably supported on a travelling grate.
- CaO or limestonelike materials capable of yielding CaO
- This zone which is operated under reducing conditions, CaO (or limestonelike materials capable of yielding CaO), which is added along with the carbonaceous fuel, reacts with the sulfur in the fuel to yield CaS.
- Operating conditions are set which maintain the reducing environment and prevent oxidation of the desirable CaS to the undesirable CaSO
- the zone contains a steady state mixture of presized limestone (in stoichiometric excess of that needed to react with the sulfur in the fuel) and solid carbonaceous fuel. Reaction temperatures range from about l,650 F.
- the products of the first zone are both solid and gaseous. Ash, CaS and some fuel are withdrawn by the moving grate which, in effect, scrapes the bottom of the bed to remove larger and/or heavier solids. Elemental sulfur can be readily recovered from the CaS. An off-gas, rich in CO and H rises to the next zone in the reactor carrying with it, elutriated fines of reduced sulfur content, fly ash and small amounts of CaO and CaS.
- Subsequent zones constitute, in effect, a boiler housed in the same reactor shell.
- the heat content of the gases and solids from the first zone is released and recovered.
- a combustion zone which adjoins the gasification zone, secondary air is admitted for the purpose of fully completing the oxidation of both solid and gaseous gasifier effluent.
- the flue gas from the recovery zone consists primarily of water, carbon dioxide and nitrogen. It contains negligible SO, compared to that which would have been present had the original sulfur-containing fuel been burned in a conventional manner.
- Another object of the invention is to provide a method whereby heat values can be recovered from sulfurcontaining fuel with minimal production of environment-contaminating S0
- Another object of the invention is to provide a method of burning high-sulfur coal which utilizes a series of transversely extending longitudinally aligned zones which together perform the functions of a gasifier and a boiler.
- FIG. 1 is a schematic flow diagram of a preferred embodiment of the invention.
- FIG. 2 is a graph illustrating the minimum CO/CO mole ratio which must be maintained in the first zone off-gas, as a function of gasifier temperatures, to produce CaS rather than CaSO DESCRIPTION OF THE PREFERRED EMBODIMENT
- a reactor 10 in which heating values are recovered from coal containing sulfur, in a manner which optimally minimizes efflux of volatile sulfur compounds to the external environment.
- the process of heat recovery from the coal is accomplished within the single apparatus 10, having three sequential contiguous and generally horizontal overlying zones through which the combustion and heat recovery process takes place before flue gas is released through the stack or outlet line 18.
- the sulfurcontaining coal is passed into a gasification zone 12 where initial combustion is carried out in a fluidized bed 39 which is supported by a movable foraminous grate 20, as will be described in detail in the following paragraphs.
- the gaseous products of initial combustion then pass upwardly into a second stage combustion or oxidation zone 14 where secondary air is admitted into the reactor through secondary air inlet 22, as shown.
- the two-stage combusted coal products then pass through a heat recovery zone 16 and finally exit from reactor 10 through the outlet line 18.
- the reactor 10 generally extends in a substantially vertical direction 24 and includes a coal inlet opening 30 passing through lateral wall 32 to gravity direct or feed a mixture of calcium oxide and sulfur-containing coal from an externally located storage reservoir 28 into gasification zone 12.
- the mixture of coal and calcium oxide preferably in the form of limestone, is maintained within the storage reservoir 28 until needed for reaction purposes within the gasification zone 12 of reactor 10.
- the coal stored within the reservoir 28 is ground to predetermined size so as to be easily fluidizable when fed into the gasification zone 12.
- the amount of limestone in the mixture is in excess of that needed to produce calcium sulfide from the sulfur contained in the coal.
- Zone 12 is geometrically defined in a lower surface thereof by the moveable foraminous grate as shown in FIG. 1. Zone 12 extends vertically above the fluidized layer free surface 38 and terminates in a generally horizontal plane surface contiguous to the second stage combustion zone 14.
- the mechanical grate 20 extends on a continuous closed contour track around first and second driving rollers 34 and 36 secured to support members 35 and 37 respectively, which are secured to a suitable wall surface of reactor 10. Rotation of the driving rollers 34 and 36 in a clockwise direction, therefore, provides a substantially inclined transverse or horizontal movement 26 to the bottom of the fluidized bed 39 and transports agglomerates to the chute or conduit 53.
- first driving roller 34 is positioned below second opposing driving roller 36 to define the grate 20 in an inclined plane with respect to the horizontal direction 26.
- One of the rollers 34 or 36 may be driven by a variable speed motor (not shown), whereas the remaining roller may be freely rotatable.
- a plurality of air boxes 40a 40p Between the upper and lower tracks 42, 44 of foraminous grate 20 there are included a plurality of air boxes 40a 40p.
- Primary air is introduced under pressure into plenum 48 through primary air inlet 46, located at a point substantially below foraminous grate 20.
- the high-pressure air passes from plenum 48 in a vertical direction 24 through the plurality of air boxes 40a 40p within grate 20.
- These elements permit pressure regulation of the vertically directed primary air which maintains the contents of gasification zone 12 in fluidized suspension.
- the flow of air is largest through box 40a and least through box 40p, to compensate for the decreasing depth of the fluidized bed 39 above upper track 42. in this manner provision is made for approximating a unit distribution of gas flow throughout the horizontal direction 26 of the grate 20 passage.
- This incorporation of air in the manner described enables the fluidized bed 39 to maintain an approximate uniform degree of fluidization in its transverse dimension with the boundary surface 38 remaining in a substantially horizontal plane
- the movable grate 20 is generally of the standard type, well described in the above-mentioned prior art patents.
- the upper and lower tracks 42, 46 are constructed of cast iron, or some like material, and are formed into a chainlike extension having air passage openings to permit the vertical flow of primary air. Projections or other vertically oriented extensions may be formed on the track surfaces in contact with the bottom of fluidized bed 39 when the inclination plane of the foraminous grate 20 is sufficient to overcome the frictional contact force between the contiguous surfaces.
- the projections prevent sliding of the gathered agglomerates in a direction toward the first driving roller 34 and are found to be of use when the inclined angle is substantially in excess of 30, although the exact angle is a function of the physical properties of the contiguous materials and, as such, may vary over a considerable range.
- coal and calcium oxide are transported to the gasification zone 12 from an externally located storage reservoir 28.
- the incoming mixture may be gravity distributed on the fluidized layer free surface 38 by star feeder or shovel wheel 50 positioned at inlet opening 30 on the lateral wall 32 as shown in FIG. 1.
- the feed may be added directly to the body of the bed.
- the calcium oxide and coal mixture contained in reservoir 28 is premixed in accordance with the predetermined sulfur content of the coal, e.g., approximately a 50 percent excess of stoichiometric amount necessary to effect the reaction resulting in the formation of calcium sulfide and water from calcium oxide and hydrogen sulfide.
- the limestone used in combination with the coal must always be in excess of that necessary to supply CaO in sufficient quantity to react with the sulfur in the coal. Molar excesses of 50 to 200 percent have been found to be preferable with an optimized range between 75 and percent.
- the upper track 42 vertically emerges from the fluidized layer free surface 38 thus carrying the agglomerates from the bottom of fluidized bed 39 into the solid drawoff zone 52.
- the solids comprising a mixture of ash, CaO and CaS are drawn ofl through solids conduit 53 to a sulfur recovering zone (not shown). It is essential that the drawoff occur within the reducing atmosphere of zone 12.
- Solid and gaseous products are combusted in the initial combustion or gasification zone 12 and pass vertically into the second stage combustion zone 14.
- zone 12 produce CaS rather than CaSO the off gas moving intrazone must contain CO/CO in mole ratio shown in FIG. 2.
- secondary air inlets 22 incorporate air into zone 14 to aid in an optimized combustion therein.
- Heat of combustion is recovered within heat recovery zone 16, through utilization of conventional heat exchange equipment and the flue gas leaves the reactor 10 through stack or outlet line 18.
- combustibles may be recycled to the first stage gasification zone 12 within reactor 10.
- Discharge to the external environment or atmosphere through the stack 18, where solids recycle is desired, may be preceded by conventional heat recovery and mechanical and/or electrostatic solids removal systems.
- electrostatic precipitators are particularly effective due to the high conductivity found in carboncontaining solids.
- Typical operation of the embodiment as shown in FIG. 1 is based on l ton, i.e., 2,000 lbs. of coal having a sulfur content of 4.5 weight percent with the gasifier zone 12 operating at a temperature approximating 2,l50 F.
- the influx of the coal and limestone mixture from the storage reservoir 28 to the gasification zone 12 totals about 2,420 lbs.
- the solid material enters at an ambient temperature of approximately 77 F. and its analysis in lbs. and lb./moles is as follows:
- the fluidized bed 39 contains a steady-state mixture of ash, limestone, CaS and coal wherein the size of the limestone is adjusted to avoid excessive elutriation from the bed 39.
- limestone carryover is maintained at minimal quantities, e.g., below 2 percent of the inventory.
- the limestone carryover is minimal if the particulate lime or lime-yielding material is charged having its size range from 6-9 mm. in diameter combined with a superficial gas velocity through the bed 39 of less than 25 ft./sec.; preferably about 14 ft./sec.
- the coal within the storage reservoir 28 is preground so that 99 percent has a diameter size less than 9-10 mm. As gasification proceeds, a given particle is consumed until it is finally entrained and leaves zone 12 and enters the second stage combustion zone 14.
- the maximum size of coal and other solid particles elutriated is a function of the linear velocity in the bed 39. Optimized conditions are achieved when the coal has a residence time in the bed 39 just long enough to substantially reduce its particle size to the point where it is elutriated into the second stage combustion zone 14. A carryover of coal from zone 12 to zone 14 between -20 is usually found. Coal solids which are not reacted in the second stage combustion zone 14 may be ultimately collected in electrostatic precipitators, as previously described, and returned to the first gasification zone 12 through conventional means.
- Solids drawoff begins when the upper track 42 of the moveable grate emerges beyond the level of the fluidized layer free surface 38 and enters drawofi zone 52 where the ratio CO/CO, is as shown in FIG. 2.
- the ratio CO/CO is as shown in FIG. 2.
- FIG. 2 is a graph showing the approximate minimum mole ratio of CO/CO,, as a function of the gasifier zone temperature, necessary to prevent oxidation of CaS to CaSO,.
- Graph contour line 54 represents the boundary line region between the upper region 56, wherein CaS is produced, and the lower region 58, where CaSO, is produced.
- the critical mole ration of CO/CO ranges between approximately 0.87 and 1.2 within a related range of gasifier temperatures extending from l,600 to 2,200 F.
- the critical mole ratio is seen to monotonically increase in value as a function of higher gasifier temperatures, with contour line 54 approximating a linearly rising function after the gasifier has reached a value of about 1,800 F.
- the partial pressures of carbon monoxide and carbon dioxide, within zones 12 and 52 be such that the critical mole ratio of CO/CO, (as defined by boundary line 54 of FIG. 2) is less than the indicated value.
- the value of this ratio is essential and critical to the success of the process of this invention, in order to preserve the sulfur values as sulfide and not permit their conversion to a sulfate.
- This process permits a relatively easy recovery of elemental sulfur from the sulfide, whereas the recovery of elemental sulfur from sulfates may only be accomplished through an expensive reduction process wherein calcium sulfate is reduced to calcium sulfide.
- calcium sulfide is the direct product of the process.
- One method of recovery is to drop the hot solids into water contained in a closed vessel at atmospheric pressure and sparge into the water an appropriate amount of C0,, preferably derived from plant flue gas.
- the reaction converts calcium values to calcium carbonate and evolves H S quantitatively.
- the H S is readily recovered and can be converted to elemental sulfur using the Claus process.
- the ash and calcium carbonate are removed together.
- Another method is to quench the hot solids in a body of water maintained at atmospheric conditions. Under these conditions, 11,5 and water vapor are released and calcium hydroxide and inerts are recovered as solids.
- Still another method, which offers potential for recovery of calcium, while still permitting recovery of sulfur values is to collect the hot solids in water at atmospheric pressure and, subsequently, heat the system to about l2S-200 C. in a pressure vessel. Under these conditions, the sulfide is largely hydrolyzed to soluble calcium hydrosulfide which can be separated from ash and other solids by filtration. If desired, calcium hydrosulfide can be produced at a lower temperature by the addition of H 8. Following filtration, water and H 8 are stripped from the liquid phase and calcium hydroxide slurry recovered. The slurry is sufficiently free of ash so that it can be recycled for ultimate addition to hopper 28.
- the filtrate may be treated with CO; at lower temperature, to release H 8 and a calcium carbonate slurry recovered.
- the slurry is sufficiently free of ash so that it can be recycled for ultimate addition to hopper 28, just as the slurry in the above paragraph.
- the gaseous components which enter the second stage combustion zone 14 comprise 136 lb. moles of CO, 35 lb. moles of H 0.2 lb. moles of 11:0, 0.4 lb. moles of C0 221 lb. moles of N and traces of H 8. Due to the nature of the combustion system, these components cannot be measured directly but are calculated on the basis of the restricted airflow fed to the first stage combustion zone 12.
- the second stage combustion zone 14, includes incorporation of secondary air entering through the inlets 22, which is preferably preheated to achieve maximum second stage combustion.
- Flue gas being emitted from the stack 18 contains approximately 136 lb. moles of CO 35 lb. moles of H 0, 563 lb. moles of N and 0.5 lb. moles of S0,.
- the process as herein detailed therefore performs as if a fuel having 0.8 percent sulfur were being burned conventionally whereas, in actuality, the fuel contained 4.5 percent sulfur.
- the essential success of the process is attributable to the operation of the gasifier 12 under those critical reducing conditions indicated in FIG. 2. Accordingly, the feed of air and coal must be adjusted so that the CO/CO ratio is represented by a point on or above the boundary line 54 shown in FIG. 2.
- a process for burning sulfur-containing coal with minimal pollution of the environment by S0 comprising:
- zones including a lower gasification zone, an upper heat recovery zone and an intermediate combustion zone;
- step (d) 9. The process of claim 8 wherein the amount of limestone fed in step (d) ranges from 50 to 200 mol percent in excess of the stoichiometric quantity.
Abstract
Heating values are recovered from sulfur-containing coal in a reactor which includes a gasification zone, a combustion zone and a heat recovery zone. A fluidized bed of coal and limestone is maintained within the gasification zone, which is supported by a moving foraminous grate. Primary air, which is also the fluidizing medium, enters the gasification zone through the grate. The zone is operated adiabatically, under reducing conditions, to yield CaS and an effluent rich in CO. The CaS is discharged from the gasification zone by the moving grate and the gaseous effluent, containing entrained desulfurized coal fines, enters the combustion zone where secondary air is added. The exotherm of combustion is retrieved in the heat recovery zone, using conventional techniques. The flue gas from the reactor contains little sulfur dioxide to pollute the environment. The CaS may be processed in several ways to recover elemental sulfur.
Description
United States Patent 72] inventor Marshall L. Spector Bellemead, NJ. [21] App]. No. 135,981 [22] Filed Apr. 21, 1971 [45] Patented Dec. 7, 1971 [73] Assignee Air Products and Chemicals, Inc. Allentown, Pa. Continuation-impart of application Ser. No. 60,379, Aug. 3, 1970, now Patent No. 3,599,610, dated Aug. 17, 1971. This application Apr. 21, 1971, Ser. No. 135,981
[54] COMBUSTION OF HIGH-SULFUR COAL IN A FLUlDlZED BED REACTOR 10 Claims, 2 Drawing Figs.
[52] [1.8.01 110/1 J, 110/1 K, 110/28 .1, 122/4 [51] Int. Cl F23d 19/00 [50] Field of Search 122/4 D; 110/1 J, 1 K, 28.]
[5 6] References Cited UNITED STATES PATENTS 3,080,855 3/1963 Lewis 110/1 X 3,320,906 5/1967 Domahidy 1 10/1 3,540,387 ll/197O McLaren et al. 110/1 FOREIGN PATENTS 619,117 4/1961 Canada llO/l Primary Examiner- Kenneth W. Sprague Anorneys-Barry Moyerman and B. Max Klevit ABSTRACT: Heating values are recovered from sulfur-containing coal in a reactor which includes agasification zone, a combustion zone and a heat recovery zone. A fluidized bed of coal and limestone is maintained within the gasification zone, which is supported by a moving foraminous grate. Primary air, which is also the fluidizing medium, enters the gasification zone through the grate. The zone is operated adiabatically, under reducing conditions, to yield CaS and an effluent rich in CO. The C215 is discharged from the gasification zone by the moving grate and the gaseous effluent, containing entrained desulfurized coal fines, enters the combustion zone where secondary air is added. The exotherm of combustion is retrieved in the heat recovery zone, using conventional techniques. The flue gas from the reactor contains little sulfur dioxide to pollute the environment. The Gas may be processed in several ways to recover elemental sulfur.
PATENTED mic Han 3.625; 164
' sum 2 OF 2 Fig. 2
APPROXIMATE MINIMUM MOLE RATIO OF CO/CO NECESSARY IN GASIFICATION ZONE OFF'GAS TO PREVENT OXIDATION THERE IN OF 008 TO C030 Co s0 MOLE RATIO OF 00/00:
I600 I800 2000 am 2200 GASIFIER TEMP. F
INVENTOR. Marshall L.Spector BY 0 0w ATTORNEY COMBUSTION OF HIGH-SULFUR COAL IN A FLUIDIZED BED REACTOR CROSS-REFERENCE TO RELATED APPLICATIONS This application is a continuation-in-part of application Ser. No. 60,379, filed Aug. 3, 1970, now U.S. Pat. No. 3,599,610 issued Aug. 17, 1971.
BACKGROUND OF THE INVENTION 1. Field of the Invention Generally, this invention relates to the desulfurization of coal. More particularly, it pertains to a process for the combustion of sulfur-containing coal wherein the sulfur is removed as calcium sulfide and the flue gas, consequently, contains minimal S0,.
2. Prior Art The prior art is legion and it would indeed be presumptuous to attempt a summary herein which would be both comprehensive and objective.
Combustion of coal in fluidized beds is not new. It is shown, for example, in U.S. Pat. No. 3,437,561. Recent work along these lines, done by the British Coal Utilization Research Association, is described in an article by S. Wright et al. II. of the Institute of Fuel 42, 235-239, June, 1969. There have also been prior attempts to recapture the sulfur content of coal, as calcium sulfate, in the course of single-stage combustion of coal in fluidized bed reactors. These were described, variously, by E. B. Robison et al. in Fluidized Combustion of Coal for Boiler Capital Cost Reduction and Air Pollution Control" 'Preprint 45C, A.I.Ch.E., New York (March, I969) and by C. W. Zielke et al. in Sulfur Removal during Combustion of Solid Fuels in a Fluidized Bed of Dolomite" Reprints A.C.S., Division of Fuel Chemistry, Vol. 13, No. 4, New York (Sept., 1969). One of the most interesting of the prior art processes is the Winkler process in which fine fuel is gasified in a fixed fluidized bed. This process is discussed in Industrial and Engineering Chemistry, Vol. 40, No. 4 (Apr., I948) page 562 et seq.
The recent emphasis on preservation of our environment has now made it extremely desirable to obtain heat values from carbonaceous fuels without polluting the atmosphere with sulfur dioxide. While one obvious solution is to utilize fuels which contain little or no sulfur, such fuels are scarce and relatively expensive. Prior art technology, even that devoted to removal of sulfur from carbonaceous fuels, was more concerned with upgrading the quality of the carbonaceous material than with minimizing the ecological trauma associated with its combustion. The treatment or pretreatment of such materials with various sulfur acceptors or getters" is discussed inter alia in U.S. Pat. Nos. 2,824,047 and 3,387,941. However, in the former, regeneration of the acceptor yields S and, in the latter, sulfur-derived impurities are released in gaseous form. The general technology of attempts to desulfurize fuels undergoing gasification is reviewed in an article by A. M. Squires in Preprints"Division of Fuel Chemistry, A.C.S., Vol. 10, No. 4, pages 20-41 (1966), which discloses, inter alia, the use of dolemite for desulfurization. Said article is incorporated herein by reference.
In the parent applications referenced above, sulfur-containing coal is treated in a two-stage process which minimizes evolution of volatile sulfur compounds. In the first stage, sulfur-containing coal is reacted with CaO in a fluid bed gasifier, which operates adiabatically under reducing conditions, to yield CaS and a gas rich in CO. The second stage is a conventional boiler in which the off-gas from the first stage and the coal fines entrained therein are delivered to the boiler as fuel. Flue gas from this boiler contains substantially no sulfur dioxide as a pollutant. CaS is withdrawn from the first stage as a valuable byproduct.
The prior art relative to coal gasification discloses the concept of supporting a fluidized bed on a continuous foraminous moving grate through which the fluidizing gas enters the bed. Preferably, the grate is divided into sections so that air flow can be balanced to compensate for varying bed depth. Such a structure is shown, for example, Godel U.S. Pat. Nos. 2,866,696 and 3,302,597.
The instant application is a logical outgrowth of these two technologies. In it, the two stages of the parent application are combined in a single reactor which contains within it a gasification zone, a combustion zone and a heat recovery zone. Thus there is no need for separate gasifier and boiler structures. Further, use of the prior art moving grate permits ready removal of ash and CaS from the gasification zone, within which reducing conditions are maintained.
SUMMARY OF THE INVENTION Combustion of sulfur-containing coal is effected in a plurality of zones contained with a single reactor. The first zone is a fluidized bed gasification zone, wherein the bed is preferably supported on a travelling grate. Within this zone, which is operated under reducing conditions, CaO (or limestonelike materials capable of yielding CaO), which is added along with the carbonaceous fuel, reacts with the sulfur in the fuel to yield CaS. Operating conditions are set which maintain the reducing environment and prevent oxidation of the desirable CaS to the undesirable CaSO The zone contains a steady state mixture of presized limestone (in stoichiometric excess of that needed to react with the sulfur in the fuel) and solid carbonaceous fuel. Reaction temperatures range from about l,650 F. to about 2,200 F. The products of the first zone are both solid and gaseous. Ash, CaS and some fuel are withdrawn by the moving grate which, in effect, scrapes the bottom of the bed to remove larger and/or heavier solids. Elemental sulfur can be readily recovered from the CaS. An off-gas, rich in CO and H rises to the next zone in the reactor carrying with it, elutriated fines of reduced sulfur content, fly ash and small amounts of CaO and CaS.
Subsequent zones constitute, in effect, a boiler housed in the same reactor shell. In these stages, the heat content of the gases and solids from the first zone is released and recovered. In a combustion zone, which adjoins the gasification zone, secondary air is admitted for the purpose of fully completing the oxidation of both solid and gaseous gasifier effluent. There is subsequent recovery of heat in a conventional heat recovery zone. The flue gas from the recovery zone consists primarily of water, carbon dioxide and nitrogen. It contains negligible SO, compared to that which would have been present had the original sulfur-containing fuel been burned in a conventional manner.
Accordingly, it is an object of the invention to provide a method whereby heat values can be recovered from sulfurcontaining fuel with minimal production of environment-contaminating S0 Another object of the invention is to provide a method of burning high-sulfur coal which utilizes a series of transversely extending longitudinally aligned zones which together perform the functions of a gasifier and a boiler.
Other objects of the invention will be apparent to those skilled in the art from a consideration of the description which follows, when read in conjunction with the accompanying drawing.
BRIEF DESCRIPTION OF THE DRAWING In the drawing, wherein like reference numerals indicate like parts:
FIG. 1 is a schematic flow diagram of a preferred embodiment of the invention; and
FIG. 2 is a graph illustrating the minimum CO/CO mole ratio which must be maintained in the first zone off-gas, as a function of gasifier temperatures, to produce CaS rather than CaSO DESCRIPTION OF THE PREFERRED EMBODIMENT Referring now to FIG. 1, there is shown a reactor 10 in which heating values are recovered from coal containing sulfur, in a manner which optimally minimizes efflux of volatile sulfur compounds to the external environment. In general, the process of heat recovery from the coal is accomplished within the single apparatus 10, having three sequential contiguous and generally horizontal overlying zones through which the combustion and heat recovery process takes place before flue gas is released through the stack or outlet line 18. The sulfurcontaining coal is passed into a gasification zone 12 where initial combustion is carried out in a fluidized bed 39 which is supported by a movable foraminous grate 20, as will be described in detail in the following paragraphs. The gaseous products of initial combustion then pass upwardly into a second stage combustion or oxidation zone 14 where secondary air is admitted into the reactor through secondary air inlet 22, as shown. The two-stage combusted coal products then pass through a heat recovery zone 16 and finally exit from reactor 10 through the outlet line 18.
The reactor 10 generally extends in a substantially vertical direction 24 and includes a coal inlet opening 30 passing through lateral wall 32 to gravity direct or feed a mixture of calcium oxide and sulfur-containing coal from an externally located storage reservoir 28 into gasification zone 12. The mixture of coal and calcium oxide, preferably in the form of limestone, is maintained within the storage reservoir 28 until needed for reaction purposes within the gasification zone 12 of reactor 10. The coal stored within the reservoir 28 is ground to predetermined size so as to be easily fluidizable when fed into the gasification zone 12. The amount of limestone in the mixture is in excess of that needed to produce calcium sulfide from the sulfur contained in the coal.
The gasification zone 12 is geometrically defined in a lower surface thereof by the moveable foraminous grate as shown in FIG. 1. Zone 12 extends vertically above the fluidized layer free surface 38 and terminates in a generally horizontal plane surface contiguous to the second stage combustion zone 14.
The mechanical grate 20 extends on a continuous closed contour track around first and second driving rollers 34 and 36 secured to support members 35 and 37 respectively, which are secured to a suitable wall surface of reactor 10. Rotation of the driving rollers 34 and 36 in a clockwise direction, therefore, provides a substantially inclined transverse or horizontal movement 26 to the bottom of the fluidized bed 39 and transports agglomerates to the chute or conduit 53. As shown in FIG. 1, first driving roller 34 is positioned below second opposing driving roller 36 to define the grate 20 in an inclined plane with respect to the horizontal direction 26. One of the rollers 34 or 36 may be driven by a variable speed motor (not shown), whereas the remaining roller may be freely rotatable. By manipulation of the flow rate of coal and calcium oxide from storage reservoir 28 as well as the linear speed of the grate 20, the fluidized layer boundary surface plane may be maintained at substantially constant height.
Between the upper and lower tracks 42, 44 of foraminous grate 20 there are included a plurality of air boxes 40a 40p. Primary air is introduced under pressure into plenum 48 through primary air inlet 46, located at a point substantially below foraminous grate 20. The high-pressure air passes from plenum 48 in a vertical direction 24 through the plurality of air boxes 40a 40p within grate 20. These elements permit pressure regulation of the vertically directed primary air which maintains the contents of gasification zone 12 in fluidized suspension. The flow of air is largest through box 40a and least through box 40p, to compensate for the decreasing depth of the fluidized bed 39 above upper track 42. in this manner provision is made for approximating a unit distribution of gas flow throughout the horizontal direction 26 of the grate 20 passage. This incorporation of air in the manner described enables the fluidized bed 39 to maintain an approximate uniform degree of fluidization in its transverse dimension with the boundary surface 38 remaining in a substantially horizontal plane.
The movable grate 20 is generally of the standard type, well described in the above-mentioned prior art patents. The upper and lower tracks 42, 46 are constructed of cast iron, or some like material, and are formed into a chainlike extension having air passage openings to permit the vertical flow of primary air. Projections or other vertically oriented extensions may be formed on the track surfaces in contact with the bottom of fluidized bed 39 when the inclination plane of the foraminous grate 20 is sufficient to overcome the frictional contact force between the contiguous surfaces. The projections prevent sliding of the gathered agglomerates in a direction toward the first driving roller 34 and are found to be of use when the inclined angle is substantially in excess of 30, although the exact angle is a function of the physical properties of the contiguous materials and, as such, may vary over a considerable range.
As has been briefly described, coal and calcium oxide are transported to the gasification zone 12 from an externally located storage reservoir 28. The incoming mixture may be gravity distributed on the fluidized layer free surface 38 by star feeder or shovel wheel 50 positioned at inlet opening 30 on the lateral wall 32 as shown in FIG. 1. Alternatively, the feed may be added directly to the body of the bed. The calcium oxide and coal mixture contained in reservoir 28 is premixed in accordance with the predetermined sulfur content of the coal, e.g., approximately a 50 percent excess of stoichiometric amount necessary to effect the reaction resulting in the formation of calcium sulfide and water from calcium oxide and hydrogen sulfide. In general, the limestone used in combination with the coal must always be in excess of that necessary to supply CaO in sufficient quantity to react with the sulfur in the coal. Molar excesses of 50 to 200 percent have been found to be preferable with an optimized range between 75 and percent.
At or near the second driving roller 36, the upper track 42 vertically emerges from the fluidized layer free surface 38 thus carrying the agglomerates from the bottom of fluidized bed 39 into the solid drawoff zone 52. The solids comprising a mixture of ash, CaO and CaS are drawn ofl through solids conduit 53 to a sulfur recovering zone (not shown). It is essential that the drawoff occur within the reducing atmosphere of zone 12.
Solid and gaseous products are combusted in the initial combustion or gasification zone 12 and pass vertically into the second stage combustion zone 14. In order that zone 12 produce CaS rather than CaSO the off gas moving intrazone must contain CO/CO in mole ratio shown in FIG. 2.
As has been described, secondary air inlets 22 incorporate air into zone 14 to aid in an optimized combustion therein. Heat of combustion is recovered within heat recovery zone 16, through utilization of conventional heat exchange equipment and the flue gas leaves the reactor 10 through stack or outlet line 18. In some instances where there is still a sizeable quantity of solid combustibles in the exiting gas, such combustibles may be recycled to the first stage gasification zone 12 within reactor 10.
Discharge to the external environment or atmosphere through the stack 18, where solids recycle is desired, may be preceded by conventional heat recovery and mechanical and/or electrostatic solids removal systems. In this operation, it has been found that electrostatic precipitators are particularly effective due to the high conductivity found in carboncontaining solids.
Typical operation of the embodiment as shown in FIG. 1 is based on l ton, i.e., 2,000 lbs. of coal having a sulfur content of 4.5 weight percent with the gasifier zone 12 operating at a temperature approximating 2,l50 F. The influx of the coal and limestone mixture from the storage reservoir 28 to the gasification zone 12 totals about 2,420 lbs. The solid material enters at an ambient temperature of approximately 77 F. and its analysis in lbs. and lb./moles is as follows:
Primary air enters the gasifier 12 through air inlet 46 to provide 64 lb. moles of oxygen and 221 lb. moles of nitrogen input into the plenum 48. The fluidized bed 39 contains a steady-state mixture of ash, limestone, CaS and coal wherein the size of the limestone is adjusted to avoid excessive elutriation from the bed 39. In operation, limestone carryover is maintained at minimal quantities, e.g., below 2 percent of the inventory. The limestone carryover is minimal if the particulate lime or lime-yielding material is charged having its size range from 6-9 mm. in diameter combined with a superficial gas velocity through the bed 39 of less than 25 ft./sec.; preferably about 14 ft./sec.
The coal within the storage reservoir 28 is preground so that 99 percent has a diameter size less than 9-10 mm. As gasification proceeds, a given particle is consumed until it is finally entrained and leaves zone 12 and enters the second stage combustion zone 14.
The maximum size of coal and other solid particles elutriated is a function of the linear velocity in the bed 39. Optimized conditions are achieved when the coal has a residence time in the bed 39 just long enough to substantially reduce its particle size to the point where it is elutriated into the second stage combustion zone 14. A carryover of coal from zone 12 to zone 14 between -20 is usually found. Coal solids which are not reacted in the second stage combustion zone 14 may be ultimately collected in electrostatic precipitators, as previously described, and returned to the first gasification zone 12 through conventional means. However, in this milieu, carryover is limited by the desiderata that (a) the temperature of the gasification zone 12 be maintained within the range where the desired ash agglomeration occurs; (b) sulfur content of the coal elutriated into combustion zone 14 is within the generally recognized range for low-sulfur carbon fuels, e.g., lessthan 1 percent by weight of the carbon content of the coal.
Solids drawoff begins when the upper track 42 of the moveable grate emerges beyond the level of the fluidized layer free surface 38 and enters drawofi zone 52 where the ratio CO/CO, is as shown in FIG. 2. By proper adjustment of primary airflow through air boxes 40a 40p (including selective orifices) within grate 20, the material in bed 39 above air box 40p achieves substantially complete gasification. However, of critical consequence is that not so much primary air be passed through the air boxes 40a 40p such as to allow the CO/CO ratio to drop below the line shown in FIG. 2.
FIG. 2, to which reference has previously been made, is a graph showing the approximate minimum mole ratio of CO/CO,, as a function of the gasifier zone temperature, necessary to prevent oxidation of CaS to CaSO,. Graph contour line 54 represents the boundary line region between the upper region 56, wherein CaS is produced, and the lower region 58, where CaSO, is produced. As shown, the critical mole ration of CO/CO ranges between approximately 0.87 and 1.2 within a related range of gasifier temperatures extending from l,600 to 2,200 F. In addition, the critical mole ratio is seen to monotonically increase in value as a function of higher gasifier temperatures, with contour line 54 approximating a linearly rising function after the gasifier has reached a value of about 1,800 F.
At no time during operation may the partial pressures of carbon monoxide and carbon dioxide, within zones 12 and 52, be such that the critical mole ratio of CO/CO, (as defined by boundary line 54 of FIG. 2) is less than the indicated value. The value of this ratio is essential and critical to the success of the process of this invention, in order to preserve the sulfur values as sulfide and not permit their conversion to a sulfate. This process permits a relatively easy recovery of elemental sulfur from the sulfide, whereas the recovery of elemental sulfur from sulfates may only be accomplished through an expensive reduction process wherein calcium sulfate is reduced to calcium sulfide. In the process as herein defined, calcium sulfide is the direct product of the process.
In addition to some unreacted CaO, about 2.3 lb. moles of CaS and 1.6 lb. moles of ash, expressed as calcium silicate, are drawn off through solids conduit 53. Though the material drawn off is primarily calcium sulfide and ash, some unreacted coal may be withdrawn, which may be separated and recycled. The calcium sulfide produced in the process may be utilized as such or as the feed for a process to recover elemental sulfur, using any one of several methods.
One method of recovery is to drop the hot solids into water contained in a closed vessel at atmospheric pressure and sparge into the water an appropriate amount of C0,, preferably derived from plant flue gas. The reaction converts calcium values to calcium carbonate and evolves H S quantitatively. The H S is readily recovered and can be converted to elemental sulfur using the Claus process. In this method, the ash and calcium carbonate are removed together.
Another method is to quench the hot solids in a body of water maintained at atmospheric conditions. Under these conditions, 11,5 and water vapor are released and calcium hydroxide and inerts are recovered as solids.
Still another method, which offers potential for recovery of calcium, while still permitting recovery of sulfur values is to collect the hot solids in water at atmospheric pressure and, subsequently, heat the system to about l2S-200 C. in a pressure vessel. Under these conditions, the sulfide is largely hydrolyzed to soluble calcium hydrosulfide which can be separated from ash and other solids by filtration. If desired, calcium hydrosulfide can be produced at a lower temperature by the addition of H 8. Following filtration, water and H 8 are stripped from the liquid phase and calcium hydroxide slurry recovered. The slurry is sufficiently free of ash so that it can be recycled for ultimate addition to hopper 28.
Alternatively, the filtrate may be treated with CO; at lower temperature, to release H 8 and a calcium carbonate slurry recovered. The slurry is sufficiently free of ash so that it can be recycled for ultimate addition to hopper 28, just as the slurry in the above paragraph.
The gaseous components which enter the second stage combustion zone 14 comprise 136 lb. moles of CO, 35 lb. moles of H 0.2 lb. moles of 11:0, 0.4 lb. moles of C0 221 lb. moles of N and traces of H 8. Due to the nature of the combustion system, these components cannot be measured directly but are calculated on the basis of the restricted airflow fed to the first stage combustion zone 12. The second stage combustion zone 14, includes incorporation of secondary air entering through the inlets 22, which is preferably preheated to achieve maximum second stage combustion.
Flue gas being emitted from the stack 18 contains approximately 136 lb. moles of CO 35 lb. moles of H 0, 563 lb. moles of N and 0.5 lb. moles of S0,. The process as herein detailed, therefore performs as if a fuel having 0.8 percent sulfur were being burned conventionally whereas, in actuality, the fuel contained 4.5 percent sulfur. The essential success of the process is attributable to the operation of the gasifier 12 under those critical reducing conditions indicated in FIG. 2. Accordingly, the feed of air and coal must be adjusted so that the CO/CO ratio is represented by a point on or above the boundary line 54 shown in FIG. 2.
While a preferred embodiment of the invention has been described, many modifications and variations will be apparent to those knowledgeable with respect to the design and operation of fluidized bed gasifiers. Accordingly, the scope of the invention is to be limited only by a reasonable interpretation of the appended claims.
What is claimed is:
l. A process for burning sulfur-containing coal with minimal pollution of the environment by S0 comprising:
a. establishing a plurality of generally horizontal overlying zones within a vertically extending reactor, said zones including a lower gasification zone, an upper heat recovery zone and an intermediate combustion zone;
b. maintaining a bed of particulate coal and limestone within said gasification zone;
0. fluidizing said bed with a stream of primary air;
d. feeding said bed with fluidizable size sulfur-containing coal and with an amount of particulate limestone in excess of that needed to produce CaS from the sulfur contained in the coal;
. reacting carbon with oxygen in said bed to yield CO;
adjusting the feed of primary air and coal to produce and maintain a reducing environment within said gasification zone, as reflected by the CO/CO, ratio in the gaseous effluent therefrom, said ratio having a value above the minimum represented by the curve in FIG. 2, whereby oxidation of CaS to CaSO is prevented; and
g. withdrawing CaS from the gasification zone as a solid and evolving from said zone, as a gaseous effluent, a mixture comprising CO and H in which are elutriated coal fines having a sulfur content less than that of the coal originally fed to the gasification zone.
2. The process of claim 1 wherein said fluidized bed is maintained on a moving foraminous grate and the fluidizing air enters the bed through the grate.
3. The process of claim 2 wherein said grate moves transversely and upwardly, discharging ash and CaS at its higher elevation.
4. The process of claim 3 wherein different quantities of primary air are fed through different portions of said grate so that, despite the varying depth of bed across the transverse extent of the grate, the linear velocity of fluidizing air flowing therethrough is maintained substantially uniform.
5. The process of claim 1 which includes the additional steps of:
h. adding secondary air to said combustion zone to oxidize the effluent from said gasification zone with a consequent release of heat;
i. recovering substantially all of the combustion zone exotherm in said heat recovery zone; and
j. venting from the heat recovery zone a flue gas containing minimal quantities of S0,.
6. The process of claim 5 wherein said fluidized bed is maintained on a moving foraminous grate and the fluidizing air enters the bed through the grate.
7. The process of claim 6 wherein said grate moves transversely and upwardly, discharging ash and CaS at its higher elevation.
8. The process of claim 7 wherein different quantities of primary air are fed through different portions of said grate so that, despite the varying depth of bed across the transverse extent of the grate, the linear velocity of fluidizing air flowing therethrough is maintained substantially uniform.
9. The process of claim 8 wherein the amount of limestone fed in step (d) ranges from 50 to 200 mol percent in excess of the stoichiometric quantity.
10. The process of claim 9 wherein about 99 percent of the coal fed to the gasification zone has a size less than l0 mm.
mg UNITED STATES PATENT OFFICE CERTIFICATE OF CORRECTION Patent No. 3, 5, m December 7, 1971 Inventor(s) Marshall L. Specter It is certified that error appears in the above-identified patent and that said Letters Patent are hereby corrected as shown below:
Column 2, line 16 "with" should read "--within--" Column 5, line 27 after "zone 1 insert "--of--" Column 5, line 27 after "5-20 insert Signed and sealed this 30th day of May 1972.
(SEAL) Attest:
EDWARD M.FLETCHER, JR. Attesting Officer ROBERT GOTTSCHALK Commissioner of Patents
Claims (9)
- 2. The process of claim 1 wherein said fluidized bed is maintained on a moving foraminous grate and the fluidizing air enters the bed through the grate.
- 3. The process of claim 2 wherein said grate moves transversely and upwardly, discharging ash and CaS at its higher elevation.
- 4. The process of claim 3 wherein different quantities of primary air are fed through different portions of said grate so that, despite the varying depth of bed across the transverse extent of the grate, the linear velocity of fluidizing air flowing therethrough is maintained substantially uniform.
- 5. The process of claim 1 which includes the additional steps of: h. adding secondary air to said combustion zone to oxidize the effluent from said gasification zone with a consequent release of heat; i. recovering substantially all of the combustion zone exotherm in said heat recovery zone; and j. venting from the heat recovery zone a flue gas containing minimal quantities of SO2.
- 6. The process of claim 5 wherein said fluidized bed is maintained on a moving foraminous grate and the fluidizing air enters the bed through the grate.
- 7. The process of claim 6 wherein said grate moves transversely and upwardly, discharging ash and CaS at its higher elevation.
- 8. The process of claim 7 wherein different quantities of primary air are fed through different portions of said grate so that, despite the varying depth of bed across the transverse extent of the grate, the linear velocity of fluidizing air flowing therethrough is maintained substantially uniform.
- 9. The process of claim 8 wherein the amount of limestone fed in step (d) ranges from 50 to 200 mol percent in excess of the stoichiometric quantity.
- 10. The process of claim 9 wherein about 99 percent of the coal fed to the gasification zone has a size less than 10 mm.
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US3913315A (en) * | 1971-05-17 | 1975-10-21 | Foster Wheeler Energy Corp | Sulfur recovery from fluidized bed which heats gas in a closed circuit gas turbine |
US3944486A (en) * | 1973-01-15 | 1976-03-16 | The Lummus Company | Process for treating sulfide-containing materials |
US3848549A (en) * | 1973-05-11 | 1974-11-19 | Phillips Petroleum Co | Two-stage smokeless incinerator with fluidized bed first stage |
US3861331A (en) * | 1973-07-20 | 1975-01-21 | Kureha Chemical Ind Co Ltd | Moving bottom incinerator |
US4165717A (en) * | 1975-09-05 | 1979-08-28 | Metallgesellschaft Aktiengesellschaft | Process for burning carbonaceous materials |
FR2323101A1 (en) * | 1975-09-05 | 1977-04-01 | Metallgesellschaft Ag | PROCESS FOR THE COMBUSTION OF MATERIALS CONTAINING CARBON |
US4060588A (en) * | 1975-12-22 | 1977-11-29 | Pullman Incorporated | Process for removing sulfur-containing gases from waste gases |
DE2612198A1 (en) * | 1976-03-23 | 1977-09-29 | Georg Raschka Fa Dipl Ing | Digested sludge feeder into furnace - throws crushed material over drying parabolic trajectory before reaching fluidised bed |
FR2376362A1 (en) * | 1977-01-03 | 1978-07-28 | Wormser Eng | CHEMICAL REACTOR FOR THE COMBUSTION AND DESULFURATION OF COAL |
US4135885A (en) * | 1977-01-03 | 1979-01-23 | Wormser Engineering, Inc. | Burning and desulfurizing coal |
FR2389831A1 (en) * | 1977-05-02 | 1978-12-01 | Appa Thermal Exchanges Ltd | |
US4211186A (en) * | 1977-05-02 | 1980-07-08 | Flameless Furnaces Limited | Fluidized bed combusters |
EP0001358A1 (en) * | 1977-09-23 | 1979-04-04 | Exxon Research And Engineering Company | Method and apparatus for burning a solid, semi-solid and/or fluid fuel in a fluidized bed |
US4303477A (en) * | 1979-06-25 | 1981-12-01 | Babcock Krauss-Maffei Industrieanlagen Gmbh | Process for the pyrolysis of waste materials |
US4359005A (en) * | 1979-06-25 | 1982-11-16 | Energy Incorporated | Fluidized bed incineration of waste |
US4342732A (en) * | 1980-07-17 | 1982-08-03 | Smith Robert H | Sludge fixation and stabilization |
US4321242A (en) * | 1980-09-30 | 1982-03-23 | United States Steel Corporation | Low sulfur content hot reducing gas production using calcium oxide desulfurization with water recycle |
US4381718A (en) * | 1980-11-17 | 1983-05-03 | Carver George P | Low emissions process and burner |
US4346064A (en) * | 1980-12-12 | 1982-08-24 | Dorr-Oliver Incorporated | Decontamination of combustion gases in fluidized bed incinerators |
FR2528543A1 (en) * | 1982-06-15 | 1983-12-16 | Fives Cail Babcock | METHOD OF COMBUSTION OF FLUIDIZED BED OF POOR FUELS, ESPECIALLY HOT OR BITUMINOUS SCHISTES, AND INSTALLATION FOR CARRYING OUT SAID METHOD |
EP0099281A1 (en) * | 1982-06-15 | 1984-01-25 | FIVES-CAIL BABCOCK, Société anonyme | Process for the combustion in a fluidized bed of low grade fuels, especially coal or oil shales |
US4465022A (en) * | 1982-07-19 | 1984-08-14 | Virr Michael J | Fluidized bed retrofit boiler |
US4553487A (en) * | 1983-09-02 | 1985-11-19 | Waste-Tech Services, Inc. | Removal of tramp material from fluid bed vessels |
US4576102A (en) * | 1983-09-02 | 1986-03-18 | Waste-Tech Services, Inc. | Removal of tramp material from fluid bed vessels |
FR2575272A1 (en) * | 1984-12-20 | 1986-06-27 | Fives Cail Babcock | Flue gas desulphurisation |
US4579070A (en) * | 1985-03-01 | 1986-04-01 | The M. W. Kellogg Company | Reducing mode circulating fluid bed combustion |
US4624192A (en) * | 1986-03-20 | 1986-11-25 | Mansfield Carbon Products | Fluidized bed combuster process |
US4771712A (en) * | 1987-06-24 | 1988-09-20 | A. Ahlstrom Corporation | Combustion of fuel containing alkalines |
US5005528A (en) * | 1990-04-12 | 1991-04-09 | Tampella Keeler Inc. | Bubbling fluid bed boiler with recycle |
US5239945A (en) * | 1991-11-13 | 1993-08-31 | Tampella Power Corporation | Apparatus to reduce or eliminate combustor perimeter wall erosion in fluidized bed boilers or reactors |
US5635147A (en) * | 1994-03-26 | 1997-06-03 | Metallgesellschaft Aktiengesellschaft | Process of treating the gasification residue formed by the gasification of solid fuels in a fluidized bed |
US20060034743A1 (en) * | 2004-08-16 | 2006-02-16 | Premier Chemicals, Llc | Reduction of coal-fired combustion emissions |
US7276217B2 (en) | 2004-08-16 | 2007-10-02 | Premier Chemicals, Llc | Reduction of coal-fired combustion emissions |
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