US3640016A - Desulfurization of coal - Google Patents
Desulfurization of coal Download PDFInfo
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- US3640016A US3640016A US811654A US3640016DA US3640016A US 3640016 A US3640016 A US 3640016A US 811654 A US811654 A US 811654A US 3640016D A US3640016D A US 3640016DA US 3640016 A US3640016 A US 3640016A
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- 239000003245 coal Substances 0.000 title claims abstract description 61
- 238000006477 desulfuration reaction Methods 0.000 title description 12
- 230000023556 desulfurization Effects 0.000 title description 12
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims abstract description 41
- 229910052717 sulfur Inorganic materials 0.000 claims abstract description 40
- 239000011593 sulfur Substances 0.000 claims abstract description 40
- 238000000034 method Methods 0.000 claims abstract description 36
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims abstract description 12
- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims abstract description 12
- 239000000463 material Substances 0.000 claims description 25
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 16
- 239000002245 particle Substances 0.000 claims description 16
- 239000007787 solid Substances 0.000 claims description 15
- 229910000287 alkaline earth metal oxide Inorganic materials 0.000 claims description 13
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 claims description 8
- 239000001569 carbon dioxide Substances 0.000 claims description 8
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 8
- 239000007789 gas Substances 0.000 claims description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 7
- 239000010459 dolomite Substances 0.000 claims description 5
- 229910000514 dolomite Inorganic materials 0.000 claims description 5
- 239000006227 byproduct Substances 0.000 claims description 4
- 150000001875 compounds Chemical class 0.000 claims description 4
- 239000011362 coarse particle Substances 0.000 claims description 3
- 238000002156 mixing Methods 0.000 claims description 3
- 230000003647 oxidation Effects 0.000 claims description 3
- 238000007254 oxidation reaction Methods 0.000 claims description 3
- 238000001354 calcination Methods 0.000 claims description 2
- 230000001351 cycling effect Effects 0.000 claims description 2
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 claims description 2
- 238000004064 recycling Methods 0.000 claims description 2
- 230000001172 regenerating effect Effects 0.000 claims description 2
- 230000008929 regeneration Effects 0.000 claims description 2
- 238000011069 regeneration method Methods 0.000 claims description 2
- 239000011343 solid material Substances 0.000 claims description 2
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 abstract description 23
- 229910052739 hydrogen Inorganic materials 0.000 abstract description 23
- 239000001257 hydrogen Substances 0.000 abstract description 23
- 230000003009 desulfurizing effect Effects 0.000 abstract description 6
- 239000002802 bituminous coal Substances 0.000 abstract description 3
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 16
- 235000011941 Tilia x europaea Nutrition 0.000 description 16
- 239000004571 lime Substances 0.000 description 16
- 238000006243 chemical reaction Methods 0.000 description 15
- 239000000203 mixture Substances 0.000 description 11
- 235000019738 Limestone Nutrition 0.000 description 5
- 239000006028 limestone Substances 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 4
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 3
- 239000011575 calcium Substances 0.000 description 3
- 125000001741 organic sulfur group Chemical group 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 229910000019 calcium carbonate 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
- 235000011116 calcium hydroxide Nutrition 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 2
- 239000000292 calcium oxide Substances 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 238000010951 particle size reduction Methods 0.000 description 2
- 239000007858 starting material Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- YZCKVEUIGOORGS-UHFFFAOYSA-N Hydrogen atom Chemical compound [H] YZCKVEUIGOORGS-UHFFFAOYSA-N 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 239000000809 air pollutant Substances 0.000 description 1
- 231100001243 air pollutant Toxicity 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005243 fluidization Methods 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 238000005984 hydrogenation reaction Methods 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- ZLNQQNXFFQJAID-UHFFFAOYSA-L magnesium carbonate Chemical compound [Mg+2].[O-]C([O-])=O ZLNQQNXFFQJAID-UHFFFAOYSA-L 0.000 description 1
- 239000001095 magnesium carbonate Substances 0.000 description 1
- 229910000021 magnesium carbonate Inorganic materials 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- NIFIFKQPDTWWGU-UHFFFAOYSA-N pyrite Chemical compound [Fe+2].[S-][S-] NIFIFKQPDTWWGU-UHFFFAOYSA-N 0.000 description 1
- 229910052683 pyrite Inorganic materials 0.000 description 1
- 239000011028 pyrite Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000012216 screening Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000004449 solid propellant Substances 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- YALHCTUQSQRCSX-UHFFFAOYSA-N sulfane sulfuric acid Chemical compound S.OS(O)(=O)=O YALHCTUQSQRCSX-UHFFFAOYSA-N 0.000 description 1
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Classifications
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L9/00—Treating solid fuels to improve their combustion
- C10L9/02—Treating solid fuels to improve their combustion by chemical means
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L9/00—Treating solid fuels to improve their combustion
- C10L9/02—Treating solid fuels to improve their combustion by chemical means
- C10L9/04—Treating solid fuels to improve their combustion by chemical means by hydrogenating
Definitions
- ABSTRACT [51] Int. Cl. ..Cl0l 5/00 5s 1 Field of Search ..23/209.9, 66, 131, 225; A method for desulfuflzmg coal by reactmg sulfur-contammg 201/17; 44/1 bituminous coal with hydrogen in the presence of a hydrogen sulfide getter at a temperature about 600-800 F.
- the sulfur content in coal can be broadly divided into three classes: pyritic, organic and sulfate.
- the last named occurs only in weathered coal, as CaSO and can be neglected essentially when dealing with freshly mined coal.
- the percentage of sulfur as pyritic sulfur also increases.
- pyritic sulfur constitutes the bulk of the total sulfur.
- chemical equilibrium calculations indicate that the organic sulfur in the coal should be more readily hydrogenated than the pyritic sulfur.
- Pyrites are typically represented by the formula FeS x being positive.
- the removal of the x portion of the sulfur is relatively easy.
- certain pyrite ore gives off the first sulfur directly upon heating as elemental sulfur vapor.
- attention is focused on the FeS portion.
- FeS+H Fe+H S 1 indicate that even at temperatures as high as 1,300 E, the equilibrium partial pressure ratio of hydrogen sulfide to hydrogen are still so low that a tremendous recycle of hydrogen is necessary. At equilibrium conversion some 400,000 s.c.f. of hydrogen have to be recirculated to reduce the sulfur in one ton of coal from 4 to 0.5 percent. Subsequent removal of H 8 from the hydrogen stream is uneconomical even when considering byproduct sulfur credit. To go to higher temperatures would completely devolatilize the coal without reducing the hydrogen recycle appreciably.
- our invention is based on the fact that the hydrogen reduction of FeS by itself proceeds according to reaction (I) which at 800 F., for example, permits a ratio of hydrogen sulfide to hydrogen of 0.00004 at equilibrium, requiring a recycle of 99.996 percent of the hydrogen.
- reaction (I) which at 800 F., for example, permits a ratio of hydrogen sulfide to hydrogen of 0.00004 at equilibrium, requiring a recycle of 99.996 percent of the hydrogen.
- a getter such as CaO
- CaO-H'I l-FeS rt CaS+Fe+H O 2 which at 800 F., permits a ratio of steam to hydrogen of 3 at equilibrium, requiring a recycle of only 25 percent of the hydrogen.
- the CaS produced may by hydrolyzed with steam as follows:
- the H 8 produced can be reacted to form elemental sul'fur by processes well known in the art.
- the Claus process operates on the overall reaction:
- the Ca(OH) or Ca CO produced can be dehydrated or calcined, respectively, to produce lime for recycle.
- the coal and lime are then fed into the desulfurizer 4 which may be a reactor of any conventional type having a reaction chamber and means to inject gas into it.
- a fluidized bed may be used and would be particularly advantageous for good temperature control.
- the material in the fluidized bed may comprise fine coal particles with coarse particles of lime raining down through the bed, thus permitting subsequent separation of lime. and coal particles by screening.
- An altemative is a fluidized bed of coal and lime of essentially the same size, the mixture being separated later by differences in density.
- a third possible arrangement is a fluidized packed bed" wherein small coal particles are fluidized in the interstices of a fixed bed of large pieces of lime.
- any reactor arrangement wherein the coal and lime particles are placed in a relatively close degree of juxtaposition permitting hydrogen gas to flow therethrough can be used in our method. The process is effected at substantially atmospheric pressure and at temperatures between about 600 and 800 F.
- Steam-laden hydrogen gas exiting from the reactor is directed through heat exchanger 5, and condenser 6, to remove water vapor and then recycled with makeup hydrogen from supply to the desulfurizer.
- the reacted lime-coal mixture is removed from the desulfurizer and the coal and lime fractions are separated in a separator device 7 by techniques, well known in the art, which utilize either the size or the density difference between the materials.
- the unreacted lime-CaS mixture is then regenerated in a regenerator 8, wherein steam and CO are fed through the mixture to effect reactions (6) or (7) as above described.
- the resultant H 8 gas is then sent to sulfur recovery 9, where e.g. elemental sulfur is produced by well-known techniques such as the Claus process.
- EXAMPLE 1 A mixture containing equal volumes of coal and calcined limestone in the size range of minus 16 to plus 80 mesh was reacted at 750 F. with hydrogen in a fluidized bed reactor.
- the reactor was a 2-inch diameter stainless steel cylinder about 6 feet long.
- Flow rate of hydrogen through the coallimestone mixture was 53 s.c.f./hour (1.5 linear feet/sec).
- the coal employed as the starting material contained 1.92 percent pyritic sulfur, 1.78 percent organic sulfur and 0.18 percent sulfate sulfur. All percentages are based on the weight of coal. Analysis of the coal after the treatment showed substantially no pyritic sulfur. The organic sulfur content was reduced by about 34 percent.
- the sulfate content was also substantially reduced, this item is not particularly significant in view of the low percentage present in the starting material.
- No hydrogen sulfide was detected in the effluent gas, indicating that substantially all hydrogen sulfide has reacted with the lime.
- the pyritic sulfur is the chief contributor to the total sulfur content of coals which are to be treated for desulfurization. ln that respect, the method of the presentinvention is especially effective.
- EXAMPLE 2 A sample of calcined limestone which had previously been reacted with hydrogen sulfide until it contained 15.6 percent sulfur by weight was regenerated as follows: a sample of such sulfur-containing limestone was placed in an Erlenmeyer flask. The sample was then covered with water. Carbon dioxide was bubbled through the mixture for 3 hours and H 8 was evolved in accordance with reaction (7) above.
- EXAMPLE 3 A sample of a caking bituminous coal containing 3.51 percent by weight of sulfur was treated by passing hydrogen over the sample at atmospheric pressure for 1 hour at a temperature between 700 and 800 F., and then for 2 hours at 800 F. The sulfur content of the coal after the treatment was found to be about 3.06 percent by weight. This example shows that the presence of the getter is necessary in order to reduce the sulfur content of the coal to an acceptable level.
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Abstract
A method for desulfurizing coal by reacting sulfur-containing bituminous coal with hydrogen in the presence of a hydrogen sulfide ''''getter'''' at a temperature about 600-800* F.
Description
v I United States Patent [151 3,640,016 Lee et al. Feb. 8, 1972 [54] DESULFURIZATION 0F COAL [56] References Cited [72] Inventors: Bernard Shing-shu Lee, Lincolnwood; UNITED STATES PATENTS Frank C. Schora, Jr., Palatine, both of ill. 2,726,148 12/1955 McKinley et al ..44/1 1 Asslsnw Institute of Gas Techlmhgy 2,824,047 2/1958 Gorin et al ..201/17 22 Filed; 2 19 9 3,130,133 4/1964 Loevenstein .23/209.9 X PP 811,654 OTHER PUBLICATIONS Guntermann et al. Chemical Abstracts" Vol 62, Apr. Related US. Application Data Q JVQ 89172 d [63] Continuation-impart of Ser. No. 579,923, Sept. I6,
1966, abandoned, Primary ExaminerEdward J. Meros Attorney-Molinare, Allegretti, Newitt and Witcoff [52] US. Cl ..44/1, 23/209.9, 23/225,
2 [57] ABSTRACT [51] Int. Cl. ..Cl0l 5/00 5s 1 Field of Search ..23/209.9, 66, 131, 225; A method for desulfuflzmg coal by reactmg sulfur-contammg 201/17; 44/1 bituminous coal with hydrogen in the presence of a hydrogen sulfide getter at a temperature about 600-800 F.
7 Claims, 1 Drawing Figure DESULFURIZATION or COAL CROSS-REFERENCES TO RELATED APPLICATION This is a continuation-in-part of our parent application, Ser. No. 579,923, filed Sept. 16, 1966, for Desulfurization of Coal," now abandoned. BACKGROUND OF THE INVEN- TION This invention relates to a novel method for desulfurizing coal at low temperatures to produce desulfurized coal useful as fuel, and, in addition, elemental sulfur as byproduct. Desulfurized coal made by our method provides a fuel product which greatly reduces the emission of air pollutants and increases the market for coal, especially high-sulfur coal.
By way of background, the sulfur content in coal can be broadly divided into three classes: pyritic, organic and sulfate. The last named occurs only in weathered coal, as CaSO and can be neglected essentially when dealing with freshly mined coal. As total sulfur content of the coal increases, the percentage of sulfur as pyritic sulfur also increases. In high-sulfur coals, pyritic sulfur constitutes the bulk of the total sulfur. In a desulfurization scheme by hydrogenation such as ours, chemical equilibrium calculations indicate that the organic sulfur in the coal should be more readily hydrogenated than the pyritic sulfur. Thus when dealing with high-sulfur coals as candidates for desulfurization treatment, one must cope with pyritic sulfur as the chief contributor to total sulfur.
Pyrites are typically represented by the formula FeS x being positive. The removal of the x portion of the sulfur is relatively easy. In fact, certain pyrite ore gives off the first sulfur directly upon heating as elemental sulfur vapor. Thus for process considerations, attention is focused on the FeS portion.
Various thermodynamic studies of the reaction:
FeS+H Fe+H S 1 indicate that even at temperatures as high as 1,300 E, the equilibrium partial pressure ratio of hydrogen sulfide to hydrogen are still so low that a tremendous recycle of hydrogen is necessary. At equilibrium conversion some 400,000 s.c.f. of hydrogen have to be recirculated to reduce the sulfur in one ton of coal from 4 to 0.5 percent. Subsequent removal of H 8 from the hydrogen stream is uneconomical even when considering byproduct sulfur credit. To go to higher temperatures would completely devolatilize the coal without reducing the hydrogen recycle appreciably.
There have been attempts to desulfurize coal by oxidation. However, such processes consume a substantial portion of the coal without reducing the sulfur content sufficiently. Altematively, desulfurization by hydrogen reduction alone, as pointed out above, has consistently been limited by equilibrium conversion even at high temperatures as well as by tremendous hydrogen recycle problems.
There have also been proposed desulfurization processes wherein ammonia is added to sulfur-containing coal and the sulfur converted to gaseous products by nascent hydrogen produced in the decomposition of the ammonia. However, such processes still suffer from the adverse H -H S equilibrium considerations above noted.
This problem has been further complicated by the fact that most of the coal having a high sulfur content, which therefore requires some treatment to remove a portion of the sulfur therefrom, is a bituminous variety which is also known as the caking coal. As indicated in an American Society of Mechanical Engineers publication, No. 66-PWR-3, entitled The Search for Low-Sulfur Coal by Harry Perry and Joseph A. DeCarlo, engineers with the Bureau of Mines, U.S. Department of Interior, on the coal reserves in the United States, practically all of the coal containing more than 1.5 percent sulfur by weight are of the bituminous or caking coal variety. Unfortunately, some of the available methods for desulfurization of carbonaceous solid fuels are specifically not applicable to the caking type of coal. Thus, there is a present need for a process which is capable of desulfurizing the type of coal which contains large amounts of sulfur.
SUMMARY OF THE INVENTION AND DESCRIPTION OF THE PREFERRED EMBODIMENT We have now invented a new method for desulfurizing caking coal which specifically removes the equilibrium limitation in reaction (1) by hydrogenating in the presence of a getter. The getter chemically combines with the hydrogen sulfide formed. Introducing the getter" strongly shifts the equilibrium conversion toward greater hydrogen utilization by per-. mitting more desulfurization to take place. Examples of cheap and effective getter" is lime, calcined dolomite, or other alkaline earth metal oxides. In the following discussions lime is used as the example with the understanding that the others are just as suitable.
It is thus the object of this invention to provide a novel process for desulfurizing coal by hydrogcnating sulfur in the coal in the presence of a getter for H 8 whereby the unfavorable equilibrium condition in converting FeS to H 5 is overcome.
Broadly speaking, our invention is based on the fact that the hydrogen reduction of FeS by itself proceeds according to reaction (I) which at 800 F., for example, permits a ratio of hydrogen sulfide to hydrogen of 0.00004 at equilibrium, requiring a recycle of 99.996 percent of the hydrogen. With a getter such as CaO, the desulfurization proceeds according to:
CaO-H'I l-FeS rt CaS+Fe+H O 2 which at 800 F., permits a ratio of steam to hydrogen of 3 at equilibrium, requiring a recycle of only 25 percent of the hydrogen.
In the 600800 F. range, at the higher temperatures by colrtrolling the partial pressure of water vapor, operation is according to equation (2) and no hydrated lime is formed according to (3).
At low temperatures, equations (2) and (3 )yield:
2CaO+FeS+H CaS-l-Ca( OH) +Fe 4 At intermediate temperatures, the surface of the lime particles may be reacted with water vapor to form hydrated lime. Then further reaction is by:
Ca(OH) -l-FeS+H CaS+Fel-2H O s; This equation permits a steam-to-hydrogen partial pressure ratio of 2.5 at 800 F. Thus, in the 600 to 800 F. range, it is possible to achieve good steam-to-hydrogen partial pressure ratios so that the hydrogen can be recycled after simple condensation of the water. In this temperature range, devolatilization of the coal would be limited, and the desulfurized product would have similar combustion characteristics as the raw coal.
From an economic standpoint, it is necessary to reuse the lime or other alkaline earth oxide getter material. To regenerate lime, the CaS produced may by hydrolyzed with steam as follows:
CaS+2H O Ca(OH) +H S (6) With steam, the above reaction proceeds sufi'rciently to the right at low temperatures for feasible operations. To increase the rate of reaction Equation (6), the preferred method of hydrolysis of CaScan be accomplished in the presence of carbon dioxide according to:
CaS+H O+CO CaCO +H S 7 In either case, the H 8 produced can be reacted to form elemental sul'fur by processes well known in the art. For example, the Claus process operates on the overall reaction:
2H S-l0 2S+2H O (3) The Ca(OH) or Ca CO produced can be dehydrated or calcined, respectively, to produce lime for recycle.
The drawing shows a schematic flow diagram of one embodiment of our method. Other arrangements of the equipment shown in the drawing will be apparent to those skilled in the art. Raw coal from storage is dried, crushed and sized in suitable particle size reduction equipment 1 to obtain a particle size suitable for fluidization, typically minus one-fourth inch. Particle size is not critical but should be chosen depending upon reactor volume and configuration and gas flow rates. Limestone or other source of alkaline earth metal oxide material, such as dolomite, is also dried, crushed and sized in suitable apparatus 2 to approximately the same particle size as the coal and fed to the calciner 3 to produce the oxide. The particle size reduction equipment shown diagrammatically at l and 2 and calciner 3 form no part of the invention per se and may be conventional equipment well in the art.
The coal and lime are then fed into the desulfurizer 4 which may be a reactor of any conventional type having a reaction chamber and means to inject gas into it.
A fluidized bed may be used and would be particularly advantageous for good temperature control. The material in the fluidized bed may comprise fine coal particles with coarse particles of lime raining down through the bed, thus permitting subsequent separation of lime. and coal particles by screening. An altemative is a fluidized bed of coal and lime of essentially the same size, the mixture being separated later by differences in density. A third possible arrangement is a fluidized packed bed" wherein small coal particles are fluidized in the interstices of a fixed bed of large pieces of lime. Broadly speaking, any reactor arrangement wherein the coal and lime particles are placed in a relatively close degree of juxtaposition permitting hydrogen gas to flow therethrough can be used in our method. The process is effected at substantially atmospheric pressure and at temperatures between about 600 and 800 F.
Steam-laden hydrogen gas exiting from the reactor is directed through heat exchanger 5, and condenser 6, to remove water vapor and then recycled with makeup hydrogen from supply to the desulfurizer.
The reacted lime-coal mixture is removed from the desulfurizer and the coal and lime fractions are separated in a separator device 7 by techniques, well known in the art, which utilize either the size or the density difference between the materials. The unreacted lime-CaS mixture is then regenerated in a regenerator 8, wherein steam and CO are fed through the mixture to effect reactions (6) or (7) as above described. The resultant H 8 gas is then sent to sulfur recovery 9, where e.g. elemental sulfur is produced by well-known techniques such as the Claus process.
The regenerated calcium carbonate from 8 is then fed to the calciner 3, along with makeup limestone feed. The carbon dioxide from 3 is used as feed for the lime regenerator.
Although the above description of our method discusses use of lime or calcium oxide, it should be understood that other alkaline earth metal oxides or oresv containing alkaline earth metal oxides are equally effective. For example, dolomite which, as well known in the art, is a mixture of calcium carbonate and. magnesium carbonate is a particularly useful material when calcined to produce CaO-MgO.
The following pilot plant data shows a specific embodiment of our invention which is intended in no way to limit the scope thereof:
EXAMPLE 1 A mixture containing equal volumes of coal and calcined limestone in the size range of minus 16 to plus 80 mesh was reacted at 750 F. with hydrogen in a fluidized bed reactor. The reactor was a 2-inch diameter stainless steel cylinder about 6 feet long. Flow rate of hydrogen through the coallimestone mixture was 53 s.c.f./hour (1.5 linear feet/sec). The coal employed as the starting material contained 1.92 percent pyritic sulfur, 1.78 percent organic sulfur and 0.18 percent sulfate sulfur. All percentages are based on the weight of coal. Analysis of the coal after the treatment showed substantially no pyritic sulfur. The organic sulfur content was reduced by about 34 percent. Although the sulfate content was also substantially reduced, this item is not particularly significant in view of the low percentage present in the starting material. No hydrogen sulfide was detected in the effluent gas, indicating that substantially all hydrogen sulfide has reacted with the lime. As indicated at the beginning of this application, the pyritic sulfur is the chief contributor to the total sulfur content of coals which are to be treated for desulfurization. ln that respect, the method of the presentinvention is especially effective.
EXAMPLE 2 A sample of calcined limestone which had previously been reacted with hydrogen sulfide until it contained 15.6 percent sulfur by weight was regenerated as follows: a sample of such sulfur-containing limestone was placed in an Erlenmeyer flask. The sample was then covered with water. Carbon dioxide was bubbled through the mixture for 3 hours and H 8 was evolved in accordance with reaction (7) above.
EXAMPLE 3 A sample of a caking bituminous coal containing 3.51 percent by weight of sulfur was treated by passing hydrogen over the sample at atmospheric pressure for 1 hour at a temperature between 700 and 800 F., and then for 2 hours at 800 F. The sulfur content of the coal after the treatment was found to be about 3.06 percent by weight. This example shows that the presence of the getter is necessary in order to reduce the sulfur content of the coal to an acceptable level.
The invention has been described in detail with reference to particular and preferred embodiments thereof, but it will be understood that variations and modifications can be made within the spirit and scope of the invention as described hereinabove and as defined in the appended claims.
What is claimed is:
l. A method of desulfurizing caking coal without substantial caking, devolatilization and conversion to coke or char, which comprises the steps of:
a. mixing a solid getter material with sulfur-containing caking coal, said getter and said caking coal being in particulate form,
b. passing hydrogen gas through said particulate getter-caking coal mixture to form a fluidized bed of said particulate mixtureand to maintain the particulate integrity thereof,
c. maintaining said mixture at a temperature in the range of from about 600 to 800 F. and at substantially atmospheric pressure, to form a nongaseous sulfide by reactions with said getter and said hydrogen, and
d. separating said nongaseous sulfide and unreacted getter material from said mixture to recover therefrom particulate, uncaked coal having a substantial amount of sulfur removed therefrom without substantial devolatilization.
2. Method of claim 1 wherein said solid getter material is an alkaline earth metal oxide or a compound of alkaline earth metal oxides.
3. Method of claim 2 wherein said solid getter material is calcined dolomite.
4. Method of claim 1 wherein coarse particles of solid getter material are dropped through a fluidized bed of coal particles, thereby keeping the solid material and coal particles separate.
5. Method of claim 1 wherein said fluidized bed is a fluidized packed bed with small coal particles being fluidized in the interstices of a fixed bed of larger solid getter material particles.
6. Method of claim 1 which includes the added steps of:
a. regenerating getter material from said nongaseous sulfide and recovering a sulfur-containing byproduct, and
b. recycling said regenerated getter material to said mixing step.
7. Method of claim 6 wherein said solid getter material is an alkaline earth metal oxide or a compound of alkaline earth metal oxides, and wherein said regeneration includes the steps of:
a. reacting said nongaseous sulfide with carbon dioxide and water to produce hydrogen sulfide-rich gas and regenerated solid getter material,
b. recovering elemental sulfur by oxidation of said hydrogen sulfide-rich gas,
c. calcining said regenerated solid getter material to produce oxide and carbon dioxide, and
d. cycling said carlzion dioxide to said step of reacting said nongaseous sulfide.
Claims (6)
- 2. Method of claim 1 wherein said solid getter material is an alkaline earth metal oxide or a compound of alkaline earth metal oxides.
- 3. Method of claim 2 wherein said solid getter material is calcined dolomite.
- 4. Method of claim 1 wherein coarse particles of solid getter material are dropped through a fluidized bed of coal particles, thereby keeping the solid material and coal particles separate.
- 5. Method of claim 1 wherein said fluidized bed is a fluidized packed bed with small coal particles being fluidized in the interstices of a fixed bed of larger solid getter material particles.
- 6. Method of claim 1 which includes the added steps of: a. regenerating getter material from said nongaseous sulfide and recovering a sulfur-containing byproduct, and b. recycling said regenerated getter material to said mixing step.
- 7. Method of claim 6 wherein said solid getter material is an alkaline earth metal oxide or a compound of alkaline earth metal oxides, and wherein said regeneration includes the steps of: a. reacting said nongaseous sulfide with carbon dioxide and water to produce hydrogen sulfide-rich gas and regenerated solid getter material, b. recovering elemental sulfur by oxidation of said hydrogen sulfide-rich gas, c. calcining said regenerated solid getter material to produce oxide and carbon dioxide, and d. cycling said carbon dioxide to said step of reacting said nongaseous sulfide.
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
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US81165469A | 1969-03-28 | 1969-03-28 |
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US3640016A true US3640016A (en) | 1972-02-08 |
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Application Number | Title | Priority Date | Filing Date |
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US811654A Expired - Lifetime US3640016A (en) | 1969-03-28 | 1969-03-28 | Desulfurization of coal |
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Cited By (26)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3768988A (en) * | 1971-07-19 | 1973-10-30 | Trw Inc | Removal of pyritic sulfur from coal using solutions containing ferric ions |
US3779722A (en) * | 1972-02-23 | 1973-12-18 | D Tatum | Process for desulfurizing fuel |
US3909213A (en) * | 1973-12-17 | 1975-09-30 | Ethyl Corp | Desulfurization of coal |
US3970434A (en) * | 1974-10-07 | 1976-07-20 | The United States Of America As Represented By The United States Energy Research And Development Administration | Process for reducing sulfur in coal char |
US4059060A (en) * | 1976-03-29 | 1977-11-22 | Ford, Bacon & Davis, Incorporated | Method and apparatus for coal treatment |
US4080176A (en) * | 1975-11-24 | 1978-03-21 | Shell Oil Company | Process for the beneficiation of solid fuel |
US4104129A (en) * | 1973-10-26 | 1978-08-01 | United States Steel Corporation | Low temperature carbonization and desulfurization of coal under elevated pressures |
US4133867A (en) * | 1974-04-25 | 1979-01-09 | Occidental Petroleum Corporation | Counter-current process with a hydrodesulfurization of solid carbonaceous materials |
US4148613A (en) * | 1977-12-27 | 1979-04-10 | Atlantic Richfield Company | Process for preparing sulfur-containing coal or lignite for combustion |
US4152119A (en) * | 1977-08-01 | 1979-05-01 | Dynecology Incorporated | Briquette comprising caking coal and municipal solid waste |
US4226601A (en) * | 1977-01-03 | 1980-10-07 | Atlantic Richfield Company | Process for reducing sulfur contaminant emissions from burning coal or lignite that contains sulfur |
US4259085A (en) * | 1977-01-27 | 1981-03-31 | Dravo Corporation | Pelletized fixed sulfur fuel |
US4280817A (en) * | 1978-10-10 | 1981-07-28 | Battelle Development Corporation | Solid fuel preparation method |
US4305726A (en) * | 1979-12-21 | 1981-12-15 | Brown Jr George E | Method of treating coal to remove sulfur and ash |
US4359451A (en) * | 1978-09-05 | 1982-11-16 | Occidental Research Corporation | Desulfurization of carbonaceous materials |
US4377391A (en) * | 1978-06-15 | 1983-03-22 | Cottell Eric Charles | Production of fuel |
US4383917A (en) * | 1980-09-15 | 1983-05-17 | University Of Utah | Apparatus for classifying airborne particulate matter |
US4391609A (en) * | 1981-10-30 | 1983-07-05 | The United States Of America As Represented By The Administrator Of The National Aeronautics And Space Administration | Hydrodesulfurization of chlorinized coal |
US4412842A (en) * | 1979-04-26 | 1983-11-01 | Eric Charles Cottell | Coal beneficiation process |
US4522626A (en) * | 1980-06-26 | 1985-06-11 | Mobil Oil Corporation | Process for treating high-sulfur caking coals to inactivate the sulfur and eliminate caking tendencies thereof |
US4661240A (en) * | 1979-06-08 | 1987-04-28 | Alberta Research Council | Low sulfur coke using dispersed calcium |
US4824441A (en) * | 1987-11-30 | 1989-04-25 | Genesis Research Corporation | Method and composition for decreasing emissions of sulfur oxides and nitrogen oxides |
US4886519A (en) * | 1983-11-02 | 1989-12-12 | Petroleum Fermentations N.V. | Method for reducing sox emissions during the combustion of sulfur-containing combustible compositions |
WO1991004310A1 (en) * | 1989-09-20 | 1991-04-04 | Petroferm Inc. | Method for reducing sox emissions during the combustion of sulfur-containing combustible compositions |
US5037450A (en) * | 1990-04-12 | 1991-08-06 | University Of Cincinnati | Method and apparatus for desulfurizing and denitrifying coal |
USRE36983E (en) * | 1983-11-02 | 2000-12-12 | Petroferm Inc. | Pre-atomized fuels and process for producing same |
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Cited By (26)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3768988A (en) * | 1971-07-19 | 1973-10-30 | Trw Inc | Removal of pyritic sulfur from coal using solutions containing ferric ions |
US3779722A (en) * | 1972-02-23 | 1973-12-18 | D Tatum | Process for desulfurizing fuel |
US4104129A (en) * | 1973-10-26 | 1978-08-01 | United States Steel Corporation | Low temperature carbonization and desulfurization of coal under elevated pressures |
US3909213A (en) * | 1973-12-17 | 1975-09-30 | Ethyl Corp | Desulfurization of coal |
US4133867A (en) * | 1974-04-25 | 1979-01-09 | Occidental Petroleum Corporation | Counter-current process with a hydrodesulfurization of solid carbonaceous materials |
US3970434A (en) * | 1974-10-07 | 1976-07-20 | The United States Of America As Represented By The United States Energy Research And Development Administration | Process for reducing sulfur in coal char |
US4080176A (en) * | 1975-11-24 | 1978-03-21 | Shell Oil Company | Process for the beneficiation of solid fuel |
US4059060A (en) * | 1976-03-29 | 1977-11-22 | Ford, Bacon & Davis, Incorporated | Method and apparatus for coal treatment |
US4226601A (en) * | 1977-01-03 | 1980-10-07 | Atlantic Richfield Company | Process for reducing sulfur contaminant emissions from burning coal or lignite that contains sulfur |
US4259085A (en) * | 1977-01-27 | 1981-03-31 | Dravo Corporation | Pelletized fixed sulfur fuel |
US4152119A (en) * | 1977-08-01 | 1979-05-01 | Dynecology Incorporated | Briquette comprising caking coal and municipal solid waste |
US4148613A (en) * | 1977-12-27 | 1979-04-10 | Atlantic Richfield Company | Process for preparing sulfur-containing coal or lignite for combustion |
US4377391A (en) * | 1978-06-15 | 1983-03-22 | Cottell Eric Charles | Production of fuel |
US4359451A (en) * | 1978-09-05 | 1982-11-16 | Occidental Research Corporation | Desulfurization of carbonaceous materials |
US4280817A (en) * | 1978-10-10 | 1981-07-28 | Battelle Development Corporation | Solid fuel preparation method |
US4412842A (en) * | 1979-04-26 | 1983-11-01 | Eric Charles Cottell | Coal beneficiation process |
US4661240A (en) * | 1979-06-08 | 1987-04-28 | Alberta Research Council | Low sulfur coke using dispersed calcium |
US4305726A (en) * | 1979-12-21 | 1981-12-15 | Brown Jr George E | Method of treating coal to remove sulfur and ash |
US4522626A (en) * | 1980-06-26 | 1985-06-11 | Mobil Oil Corporation | Process for treating high-sulfur caking coals to inactivate the sulfur and eliminate caking tendencies thereof |
US4383917A (en) * | 1980-09-15 | 1983-05-17 | University Of Utah | Apparatus for classifying airborne particulate matter |
US4391609A (en) * | 1981-10-30 | 1983-07-05 | The United States Of America As Represented By The Administrator Of The National Aeronautics And Space Administration | Hydrodesulfurization of chlorinized coal |
US4886519A (en) * | 1983-11-02 | 1989-12-12 | Petroleum Fermentations N.V. | Method for reducing sox emissions during the combustion of sulfur-containing combustible compositions |
USRE36983E (en) * | 1983-11-02 | 2000-12-12 | Petroferm Inc. | Pre-atomized fuels and process for producing same |
US4824441A (en) * | 1987-11-30 | 1989-04-25 | Genesis Research Corporation | Method and composition for decreasing emissions of sulfur oxides and nitrogen oxides |
WO1991004310A1 (en) * | 1989-09-20 | 1991-04-04 | Petroferm Inc. | Method for reducing sox emissions during the combustion of sulfur-containing combustible compositions |
US5037450A (en) * | 1990-04-12 | 1991-08-06 | University Of Cincinnati | Method and apparatus for desulfurizing and denitrifying coal |
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