CN112708477A - Method for increasing combustion heat value of blast furnace gas and simultaneously removing organic sulfur and inorganic sulfur - Google Patents
Method for increasing combustion heat value of blast furnace gas and simultaneously removing organic sulfur and inorganic sulfur Download PDFInfo
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- CN112708477A CN112708477A CN202110005131.9A CN202110005131A CN112708477A CN 112708477 A CN112708477 A CN 112708477A CN 202110005131 A CN202110005131 A CN 202110005131A CN 112708477 A CN112708477 A CN 112708477A
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- 238000000034 method Methods 0.000 title claims abstract description 56
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 title claims abstract description 37
- 125000001741 organic sulfur group Chemical group 0.000 title claims abstract description 35
- 229910052717 sulfur Inorganic materials 0.000 title claims abstract description 29
- 239000011593 sulfur Substances 0.000 title claims abstract description 28
- 238000002485 combustion reaction Methods 0.000 title claims abstract description 18
- 239000007789 gas Substances 0.000 claims abstract description 91
- 239000003054 catalyst Substances 0.000 claims abstract description 41
- 238000006477 desulfuration reaction Methods 0.000 claims abstract description 20
- 230000023556 desulfurization Effects 0.000 claims abstract description 20
- 239000000571 coke Substances 0.000 claims abstract description 15
- 230000009471 action Effects 0.000 claims abstract description 10
- 238000006460 hydrolysis reaction Methods 0.000 claims description 24
- 230000007062 hydrolysis Effects 0.000 claims description 22
- 238000001035 drying Methods 0.000 claims description 19
- 238000005470 impregnation Methods 0.000 claims description 19
- 229910052760 oxygen Inorganic materials 0.000 claims description 19
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 18
- 239000001301 oxygen Substances 0.000 claims description 18
- 238000002791 soaking Methods 0.000 claims description 16
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 15
- 230000003197 catalytic effect Effects 0.000 claims description 14
- 239000000428 dust Substances 0.000 claims description 13
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 11
- 229910000041 hydrogen chloride Inorganic materials 0.000 claims description 11
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 claims description 11
- 229910052976 metal sulfide Inorganic materials 0.000 claims description 9
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 7
- 238000006298 dechlorination reaction Methods 0.000 claims description 7
- 238000005984 hydrogenation reaction Methods 0.000 claims description 6
- 239000002808 molecular sieve Substances 0.000 claims description 6
- 238000007254 oxidation reaction Methods 0.000 claims description 6
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims description 6
- 150000000703 Cerium Chemical class 0.000 claims description 4
- 229910052799 carbon Inorganic materials 0.000 claims description 4
- 150000001868 cobalt Chemical class 0.000 claims description 4
- 230000003301 hydrolyzing effect Effects 0.000 claims description 3
- 159000000003 magnesium salts Chemical class 0.000 claims description 3
- 150000001879 copper Chemical class 0.000 claims description 2
- 150000002505 iron Chemical class 0.000 claims description 2
- 150000002751 molybdenum Chemical class 0.000 claims description 2
- XAEFZNCEHLXOMS-UHFFFAOYSA-M potassium benzoate Chemical compound [K+].[O-]C(=O)C1=CC=CC=C1 XAEFZNCEHLXOMS-UHFFFAOYSA-M 0.000 claims description 2
- 150000003467 sulfuric acid derivatives Chemical class 0.000 claims 2
- 230000000382 dechlorinating effect Effects 0.000 claims 1
- 238000002156 mixing Methods 0.000 claims 1
- 238000006243 chemical reaction Methods 0.000 abstract description 26
- 230000008569 process Effects 0.000 abstract description 14
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 abstract description 11
- 239000001257 hydrogen Substances 0.000 abstract description 10
- 229910052739 hydrogen Inorganic materials 0.000 abstract description 10
- 230000000694 effects Effects 0.000 abstract description 4
- 230000009467 reduction Effects 0.000 abstract description 2
- 239000006227 byproduct Substances 0.000 abstract 1
- 239000002912 waste gas Substances 0.000 abstract 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 26
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 26
- QGJOPFRUJISHPQ-UHFFFAOYSA-N Carbon disulfide Chemical compound S=C=S QGJOPFRUJISHPQ-UHFFFAOYSA-N 0.000 description 25
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 23
- 239000003546 flue gas Substances 0.000 description 23
- 230000003009 desulfurizing effect Effects 0.000 description 16
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 15
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 11
- JJWKPURADFRFRB-UHFFFAOYSA-N carbonyl sulfide Chemical compound O=C=S JJWKPURADFRFRB-UHFFFAOYSA-N 0.000 description 10
- 239000007788 liquid Substances 0.000 description 10
- 239000000203 mixture Substances 0.000 description 9
- 239000007787 solid Substances 0.000 description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 9
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 8
- 239000003795 chemical substances by application Substances 0.000 description 8
- YIXJRHPUWRPCBB-UHFFFAOYSA-N magnesium nitrate Chemical compound [Mg+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O YIXJRHPUWRPCBB-UHFFFAOYSA-N 0.000 description 8
- 230000008929 regeneration Effects 0.000 description 7
- 238000011069 regeneration method Methods 0.000 description 7
- 238000001914 filtration Methods 0.000 description 6
- WFLYOQCSIHENTM-UHFFFAOYSA-N molybdenum(4+) tetranitrate Chemical compound [N+](=O)([O-])[O-].[Mo+4].[N+](=O)([O-])[O-].[N+](=O)([O-])[O-].[N+](=O)([O-])[O-] WFLYOQCSIHENTM-UHFFFAOYSA-N 0.000 description 6
- 150000003839 salts Chemical class 0.000 description 6
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 5
- 238000003723 Smelting Methods 0.000 description 5
- 229910000831 Steel Inorganic materials 0.000 description 5
- 239000003463 adsorbent Substances 0.000 description 5
- 238000004064 recycling Methods 0.000 description 5
- 239000010959 steel Substances 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 229910001868 water Inorganic materials 0.000 description 5
- 238000010521 absorption reaction Methods 0.000 description 4
- VGBWDOLBWVJTRZ-UHFFFAOYSA-K cerium(3+);triacetate Chemical compound [Ce+3].CC([O-])=O.CC([O-])=O.CC([O-])=O VGBWDOLBWVJTRZ-UHFFFAOYSA-K 0.000 description 4
- OPQARKPSCNTWTJ-UHFFFAOYSA-L copper(ii) acetate Chemical compound [Cu+2].CC([O-])=O.CC([O-])=O OPQARKPSCNTWTJ-UHFFFAOYSA-L 0.000 description 4
- 239000008367 deionised water Substances 0.000 description 4
- 229910021641 deionized water Inorganic materials 0.000 description 4
- 229910052742 iron Inorganic materials 0.000 description 4
- VCJMYUPGQJHHFU-UHFFFAOYSA-N iron(3+);trinitrate Chemical compound [Fe+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O VCJMYUPGQJHHFU-UHFFFAOYSA-N 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- 230000003647 oxidation Effects 0.000 description 4
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 4
- TYJJADVDDVDEDZ-UHFFFAOYSA-M potassium hydrogencarbonate Chemical compound [K+].OC([O-])=O TYJJADVDDVDEDZ-UHFFFAOYSA-M 0.000 description 4
- 239000003034 coal gas Substances 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- 238000005406 washing Methods 0.000 description 3
- 230000001174 ascending effect Effects 0.000 description 2
- UFMZWBIQTDUYBN-UHFFFAOYSA-N cobalt dinitrate Chemical compound [Co+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O UFMZWBIQTDUYBN-UHFFFAOYSA-N 0.000 description 2
- 229910001981 cobalt nitrate Inorganic materials 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 239000010949 copper Substances 0.000 description 2
- 238000005338 heat storage Methods 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- YWXYYJSYQOXTPL-SLPGGIOYSA-N isosorbide mononitrate Chemical compound [O-][N+](=O)O[C@@H]1CO[C@@H]2[C@@H](O)CO[C@@H]21 YWXYYJSYQOXTPL-SLPGGIOYSA-N 0.000 description 2
- 239000011777 magnesium Substances 0.000 description 2
- 229910000027 potassium carbonate Inorganic materials 0.000 description 2
- 230000001172 regenerating effect Effects 0.000 description 2
- 239000000779 smoke Substances 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 159000000009 barium salts Chemical class 0.000 description 1
- 159000000007 calcium salts Chemical class 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- ARUVKPQLZAKDPS-UHFFFAOYSA-L copper(II) sulfate Chemical class [Cu+2].[O-][S+2]([O-])([O-])[O-] ARUVKPQLZAKDPS-UHFFFAOYSA-L 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 125000004122 cyclic group Chemical group 0.000 description 1
- 238000004134 energy conservation Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 230000002779 inactivation Effects 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 150000002603 lanthanum Chemical class 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 230000002101 lytic effect Effects 0.000 description 1
- 150000002696 manganese Chemical class 0.000 description 1
- 238000002715 modification method Methods 0.000 description 1
- 230000001706 oxygenating effect Effects 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000002035 prolonged effect Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000012492 regenerant Substances 0.000 description 1
- GGCZERPQGJTIQP-UHFFFAOYSA-N sodium;9,10-dioxoanthracene-2-sulfonic acid Chemical compound [Na+].C1=CC=C2C(=O)C3=CC(S(=O)(=O)O)=CC=C3C(=O)C2=C1 GGCZERPQGJTIQP-UHFFFAOYSA-N 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 239000002904 solvent Substances 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
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/002—Removal of contaminants
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/002—Removal of contaminants
- C10K1/003—Removal of contaminants of acid contaminants, e.g. acid gas removal
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/002—Removal of contaminants
- C10K1/003—Removal of contaminants of acid contaminants, e.g. acid gas removal
- C10K1/004—Sulfur containing contaminants, e.g. hydrogen sulfide
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/02—Dust removal
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/34—Purifying combustible gases containing carbon monoxide by catalytic conversion of impurities to more readily removable materials
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Industrial Gases (AREA)
- Catalysts (AREA)
Abstract
The invention relates to a method for improving the combustion heat value of blast furnace gas and simultaneously removing organic sulfur and inorganic sulfur, aiming at the low heat value and the desulfurization requirement of the blast furnace gas, a certain amount of coke oven gas with high heat value is introduced into the blast furnace gas to improve the heat value of the blast furnace gas so as to achieve the purposes of resource utilization and process cost reduction; in addition, the hydrogen in the coke oven gas can be used as a hydrogen source to carry out the hydro-conversion reaction on the organic sulfur (COS and CS) in the blast furnace gas under the action of a catalyst2) Conversion to inorganic sulfur (H)2S), finally, inorganic sulfur is removed through a desulfurization catalyst; the method has the advantages of no generation of waste gas and byproducts, low operation cost, good desulfurization effect and very high practical application prospect.
Description
Technical Field
The invention relates to a method for improving the combustion heat value of blast furnace gas and simultaneously removing organic sulfur and inorganic sulfur, belonging to the technical field of industrial waste gas purification.
Background
In order to reduce the energy consumption of enterprises, the blast furnace gas can be used as fuel for steel plants after being purified. Height ofNon-combustible component (as N) in the coal gas component2And CO2Mainly) is more (about 70 percent) and the calorific value is low (3500 kJ/m)3Left and right). The coke oven gas which is also present in steel plants is mainly composed of hydrogen (56%) and methane (27%), and the calorific value is as high as 18250kJ/m3. The heat value of the coke oven gas is much higher than that of the blast furnace gas with the same volume. In general, blast furnace gas having a low calorific value is not easily burned, and in order to increase the thermal effect of combustion, the blast furnace gas must be preheated in addition to air. Therefore, when blast furnace gas is used for heating, one half of the heat storage chambers of the ascending air flow of the combustion system is used for preheating air, and the other half of the heat storage chambers of the ascending air flow of the combustion system is used for preheating gas. Therefore, in order to achieve better combustion of the blast furnace gas, enterprises invest certain capital for preheating the blast furnace gas, which is contrary to the concept of resource utilization of the blast furnace gas.
With the increasing environmental protection requirements of iron and steel enterprises, the iron making process becomes an important link for energy conservation and emission reduction, and blast furnace gas generated in the iron and steel smelting process is used as an important pollutant in the iron and steel smelting industry, wherein the blast furnace gas contains organic sulfur (COS and CS)2、C4H4S, etc.), inorganic sulfur (H)2S) and the like, and the existence of the harmful gases seriously restricts the resource utilization of the blast furnace gas. COS and H2S is the main component of pollutants in blast furnace gas, and accounts for more than 95%, so the research on the removal technology of the two substances is particularly critical.
Patent CN201610971597.3 discloses "a modified activated carbon, a modification method and its use", in which the activated carbon modified by saturated copper sulfate solution is used as an activated carbon column, and hydrogen sulfide in gas is adsorbed by the activated carbon column. However, the method needs water-carrying treatment of the dried modified activated carbon, and a large amount of wastewater is generated in the process, so that the cost of industrial application is increased.
The patent CN201710791711.9 discloses a method for recycling hydrogen sulfide and carbonyl sulfide based on molten salt resource, which comprises the steps of heating liquid functional molten salt to 450-750 ℃, and then adding carbon powder into the heated liquid functional molten salt; then introducing hydrogen sulfide and carbonyl sulfide gas into molten salt to be fully contacted and then absorbed by reaction; after the gas is stopped to be introduced, calcium salt or barium salt is supplemented into the molten salt system after the reaction, the mixture is stirred and mixed, and then sulfide generated by the standing precipitation reaction is led out of the molten salt system at high temperature for recycling. The reaction has high requirement on temperature, secondary pollutants such as waste water, solid waste and the like can be generated in the reaction process, and the process cost is indirectly increased.
COS removal can be generally divided into a dry method and a wet method; the dry method mainly includes a hydroconversion method, a hydrolysis conversion method, an oxidation conversion method, and the like. Wet removal of carbonyl sulfide can be classified into physical absorption, chemical absorption and physical-chemical methods, such as organic amine solvent absorption, liquid-phase catalytic hydrolysis conversion, and the like. Because of the poor activity of the organic sulfur, although the traditional solution absorption method and the solid adsorption method can remove a certain amount of organic sulfur, the conversion process has good hydrolysis effect on the organic sulfur, but the requirement of fine desulfurization cannot be met.
Disclosure of Invention
Aiming at the problems in the prior art, the invention provides a method for improving the combustion heat value of blast furnace gas and simultaneously removing organic sulfur and inorganic sulfur with low cost and high efficiency2And S together realize the removal of hydrogen sulfide gas under the action of a desulfurization catalyst.
The method comprises the following steps:
(1) improving the heat value of blast furnace gas: the method is characterized in that the coke oven gas with a certain volume is introduced into the blast furnace gas by utilizing the characteristics of high proportion of combustible components and high heat value of the coke oven gas, so that the volume ratio of the coke oven gas to the blast furnace gas is 6: 1-12: 1, the combustible components in the blast furnace gas are improved to increase the heat value, the process cost during the combustion of the blast furnace gas is reduced, and the proportion of hydrogen in the blast furnace gas is correspondingly improved after the coke oven gas is introduced;
(2) dust removal, deoxidation and dechlorination: carrying out dust removal, deoxidation and dechlorination on the mixed gas in the step (1) to remove dust, oxygen and chlorine in the gas; to protect the hydrolytic agent from waterThe poisoning and inactivation of the lytic agent are realized, the service life is prolonged, and the corrosion to the pipeline and the TRT blade is reduced, so that the influence of the substances on the subsequent process is eliminated; after dust removal, the dust concentration in the flue gas is 5mg/m3The following; after deoxidation and dechlorination, the concentrations of oxygen and hydrogen chloride are respectively reduced to 0.05% and 10mg/m3The following;
(3) conversion of organic sulfur to inorganic sulfur: by using H in coal gas2O and H produced by the introduction of coke oven gas2Under the action of an organic sulfur hydrolysis catalyst, organic sulfur in the mixed gas is subjected to catalytic hydrolysis reaction and hydrogenation conversion reaction at 100-200 ℃ to generate inorganic sulfur, the introduction of hydrogen improves the conversion efficiency of the inorganic sulfur, the conversion rate is stably maintained at more than 95%, and CO gas is generated in the hydrogenation conversion process at the same time, so that the recycling of coal gas is facilitated; the reaction principle equation of the step is as follows: COS + H2→H2S+CO;COS+H2O→H2S+CO2;CS2+H2O→H2S+CO2;
(4) Cooling and oxygenating by a heat exchanger: hydrolyzing the mixed gas to convert organic sulfur (COS, CS)2) Then, reducing the temperature of the mixed gas to 80-150 ℃ by using a heat exchanger;
(5) inorganic sulfur removal: adding a certain amount of oxygen into the mixed gas before the mixed gas is sent into a hydrogen sulfide removal tower, so that the oxygen content is controlled to be 0.05-0.8%; under the action of desulfurizing agent, the original H in the gas2S and H converted in step (3)2S is subjected to catalytic oxidation reaction at 80-150 ℃ to generate elemental sulfur, metal sulfide and sulfate, the elemental sulfur, the metal sulfide and the sulfate are adsorbed on a catalyst, and the total sulfur content in the purified gas is 20mg/m3The following; the reaction principle equation of the step is as follows: h2S+O2→S+H2O;H2S+MO→MS+H2O;H2S + O + MO → sulfate + H2O (M is a metal supported by the catalyst);
(6) and (3) regeneration of a desulfurizing agent: and (5) after the desulfurization catalyst in the step (5) is deactivated, regenerating by a chemical method, and realizing the recycling of the desulfurizer.
The organic sulfur hydrolysis catalyst is prepared from active carbon, alumina and moleculesOne of the sieves is taken as a carrier, and one or more solutions of molybdenum salt, potassium salt, magnesium salt, cerium salt, cobalt salt, magnesium salt and aluminum salt are taken as impregnants; the impregnant (M) is added into the carrier in one time or in several times according to the equal volume impregnation methodX:MCarrier= 1-10%; x is a metal loaded by the catalyst), soaking for 6-24 h at 20-60 ℃, filtering, drying the solid for 6-12 h at 80-120 ℃, and roasting for 2-5 h at 300-400 ℃ to obtain the organic sulfur hydrolysis catalyst.
The desulfurization catalyst takes one of active carbon, alumina and molecular sieve as a carrier, takes one or more of copper salt, cerium salt, iron salt, cobalt salt, manganese salt, lanthanum salt and silver salt as impregnant, and the impregnant (M) is added to the carrier in one step or in several steps according to the equal volume impregnation methodX:MCarrier= 1-10%; x is a metal loaded by the catalyst), soaking for 6-24 h at 20-60 ℃, filtering, drying for 6-12 h at 80-120 ℃, and roasting for 2-5 h at 300-400 ℃ to obtain the desulfurization catalyst.
The catalyst regeneration is to take potassium hydroxide or sodium hydroxide solution with the mass concentration of 2-10% as regeneration liquid, put the deactivated desulfurization catalyst into the regeneration liquid to be soaked for 2-5 hours for 2-5 times until the color of the impregnation liquid is colorless, and then wash away the regeneration liquid on the surface of the desulfurizer by deionized water at the temperature of 15-40 ℃; and drying the mixture for 6 to 15 hours at the temperature of between 80 and 120 ℃ to obtain the regenerated desulfurizer.
The invention has the advantages that:
(1) according to the method, the coke oven gas is introduced into the blast furnace gas, so that the heat value of the blast furnace gas is improved, and hydrogen required by tail gas treatment is brought to the blast furnace gas; the process and the tail gas treatment cost are reduced, and the resource utilization is realized to a certain extent;
(2) the method comprises adding organic sulfur (COS, CS) by selecting appropriate catalyst2) Conversion to inorganic sulfur (H)2S), then, the sulfur is converted into elemental sulfur, sulfate and metal sulfide through a fine desulfurization catalyst; so that COS and H in the tail gas emission2The content of S is reduced to 20.0mg/m3Simultaneously, the fine desulfurization catalyst is regenerated, thereby not only eliminating the environmental pollution caused by the exhaust gas discharged into the air, but also improving the resource benefitA rate of utilization;
(3) the method of the invention is simple, the investment is low, and the operating cost is low.
Drawings
FIG. 1 is a schematic flow chart of the method of the present invention.
Detailed Description
The present invention is further illustrated in detail by the following figures and examples, but the scope of the present invention is not limited to the above description, and the deoxidation and dechlorination processes in examples 1 to 4 use a conventional adsorption method to remove oxygen and hydrogen chloride from the mixed gas by using a commercially available deoxidation and dechlorination adsorbent.
Example 1
1. Adding a molybdenum nitrate solution into a carrier by using activated carbon as the carrier and a molybdenum nitrate solution as an impregnation solution according to an isometric impregnation method, wherein M isMo:MCarrier= 5%; soaking at 20 deg.C for 20h, filtering, drying the solid at 80 deg.C for 6h, and roasting at 300 deg.C for 5h to obtain organic sulfur hydrolysis catalyst A;
2. respectively adding ferric nitrate and cobalt nitrate solution into a carrier by using alumina as the carrier and a solution containing ferric nitrate and cobalt nitrate as an impregnation solution according to an isometric impregnation method, wherein M isFe+MCo:MCarrier=5%,MFe:MCo1:1, soaking at room temperature for 12h, filtering, drying the solid at 80 ℃ for 6h, and then roasting at 300 ℃ for 5h to prepare a desulfurization catalyst A;
3. in volume ratio VBlast furnace:VCoke ovenIntroducing coke oven gas into blast furnace gas in a ratio of =6:1, and measuring and calculating the smoke gas amount of mixed gas to be 4000m3The concentration of COS in the flue gas is 130mg/m3Carbon disulfide 10mg/m3Hydrogen sulfide 40mg/m3The oxygen concentration is 0.5%, the hydrogen concentration is 8.6%, and the hydrogen chloride concentration is 50mg/m3The flue gas temperature is 130 ℃, and the dust concentration is 400mg/m3The calorific value is 5000kJ/m3;
4. As shown in figure 1, the mixed flue gas is firstly dedusted by a bag-type deduster, and the dust concentration is reduced to 4mg/m3(ii) a Before entering the catalytic hydrolysis process, fixed bed adsorbent is deoxidized and dechlorinated, oxygen is addedThe concentration of hydrogen chloride is reduced to 0.03 percent and 8mg/m respectively3Then the mixture is sent into a desulfurizing tower 1 filled with organic sulfur hydrolysis catalyst, carbonyl sulfur and carbon disulfide are converted into hydrogen sulfide through hydrogenation conversion and catalytic hydrolysis under the condition that the temperature is 130 ℃, and the total conversion efficiency reaches 95 percent; the converted flue gas is sent into a desulfurizing tower 2 filled with a desulfurizing catalyst to purify hydrogen sulfide after the temperature of the converted flue gas is reduced to 100 ℃ through a heat exchanger, meanwhile, oxygen is added into the mixed gas, the concentration of the oxygen is increased to 0.1%, and the hydrogen sulfide is catalytically oxidized and converted into elemental sulfur, metal sulfide and sulfate under the action of the desulfurizing catalyst; the total sulfur content in the purified flue gas is 15mg/m3(ii) a Then the purified flue gas is sent into a smelting furnace for combustion; soaking the deactivated desulfurizer in 5wt% sodium hydroxide solution for 3 times until the sodium hydroxide solution is colorless, washing the regenerated solution on the surface of the desulfurizer with deionized water at 20 ℃, drying at 80 ℃ for 14h, and controlling the total sulfur discharge amount to be 20mg/m after 3 times of cyclic regeneration3The following.
Example 2
1. Adding a molybdenum nitrate solution into a carrier by using a ZSM-5 molecular sieve as the carrier and a molybdenum nitrate solution and a potassium carbonate solution as impregnation solutions according to an isometric impregnation method, wherein M isMo:MCarrier= 5%; soaking at room temperature for 8h, filtering, drying the solid at 100 deg.C for 8h, and adding the dried solid into potassium carbonate solution according to the equal volume soaking method, wherein M isK:MCarrier= 3%; soaking at 30 ℃ for 15h, drying the filtered solid at 90 ℃ for 8h, and roasting at 350 ℃ for 4h to obtain an organic sulfur hydrolysis catalyst B;
2. respectively adding copper acetate and cerium acetate solution to a carrier by using a 3A molecular sieve as the carrier and a solution containing copper acetate and cerium acetate as impregnation liquid according to an isometric impregnation method, wherein M isCu+MCe:MCarrier=5%,MFe:MCo1:1, soaking at 30 ℃ for 15h, filtering, drying the solid at 80 ℃ for 6h, and then roasting at 350 ℃ for 4h to prepare a desulfurization catalyst B;
3. in volume ratio VBlast furnace:VCoke ovenIntroducing coke oven gas into blast furnace gas in a ratio of =8: 1; warp beamThe smoke gas amount of the mixed gas is measured and calculated to be 5000m3The concentration of COS in the flue gas is 135mg/m3The carbon disulfide concentration is 8mg/m3Hydrogen sulfide concentration of 45mg/m3The oxygen concentration is 0.8%, the hydrogen concentration is 7.6%, and the hydrogen chloride concentration is 35mg/m3The flue gas temperature is 150 ℃, and the dust concentration is 500mg/m3The heat value is 5700kJ/m3;
4. The mixed flue gas is firstly dedusted by a bag-type deduster, and the dust concentration is reduced to 3mg/m3(ii) a Before entering the catalytic hydrolysis process, fixed bed adsorbent is deoxidized and dechlorinated, and the concentrations of oxygen and hydrogen chloride are respectively reduced to 0.04 percent and 10mg/m3Then the mixture is sent into a desulfurizing tower 1 filled with organic sulfur hydrolysis catalyst, carbonyl sulfur and carbon disulfide are converted into hydrogen sulfide through hydrogenation conversion and catalytic hydrolysis under the condition that the temperature is 150 ℃, and the total conversion efficiency reaches 98 percent; the converted flue gas is cooled to 120 ℃ through a heat exchanger, and then is sent into a desulfurizing tower 2 filled with a desulfurizing catalyst to purify hydrogen sulfide, and the hydrogen sulfide is converted into elemental sulfur, metal sulfide and sulfate through catalytic oxidation under the action of a desulfurizing agent; the total sulfur content in the purified flue gas is 10mg/m3(ii) a Then the purified flue gas is sent into a smelting furnace for combustion; soaking the mixture for 4 times after soaking the mixture by using 5wt% of potassium hydroxide solution until the potassium hydroxide solution is colorless, washing the regeneration solution on the surface of a desulfurizing agent by using 30 ℃ deionized water, drying the mixture for 14 hours at 80 ℃, and controlling the total sulfur discharge amount to be 20mg/m after 3 times of circulating and regenerating the desulfurization catalyst3The following.
Example 3
1. Adding magnesium nitrate solution into the carrier by using alumina as a carrier and magnesium nitrate and potassium carbonate as impregnation liquid according to an equal-volume impregnation method, wherein M isMg:MCarrier=3%, standing at room temperature for 12h, drying at 100 deg.C for 12h, and adding the dried solid into potassium carbonate solution by isovolumetric immersion method, wherein M isK:MCarrier= 1%; standing at 55 ℃ for 7h, drying at 100 ℃ for 12h, and roasting at 300 ℃ for 3h to obtain an organic sulfur hydrolysis catalyst C;
2. 5A molecular sieve is taken as a carrier, cerium acetate is taken as a steeping fluid, and the volume is equal to that of the carrierImpregnation by adding a solution of cerium acetate to the support, wherein MMg:MCarrier= 3%; standing at 55 ℃ for 24h, drying at 100 ℃ for 12h, and roasting at 400 ℃ for 2h to obtain a desulfurization catalyst C;
3. according to volume ratio VBlast furnace:VCoke oven=10:1, introducing coke oven gas into blast furnace gas, and measuring and calculating flue gas amount of mixed gas to be 8000m3The concentration of COS in the flue gas is 125mg/m3The carbon disulfide concentration is 5mg/m3The concentration of hydrogen sulfide is 35mg/m3The oxygen concentration is 0.7%, the hydrogen concentration is 6.2%, and the hydrogen chloride concentration is 40mg/m3The flue gas temperature is 180 ℃, and the dust concentration is 550mg/m3The calorific value is 5000kJ/m3;
4. The mixed flue gas is firstly dedusted by a bag-type deduster, and the dust concentration is reduced to 3mg/m3(ii) a Before entering the catalytic hydrolysis process, fixed bed adsorbent is deoxidized and dechlorinated, and the concentrations of oxygen and hydrogen chloride are respectively reduced to 0.03 percent and 7 mg/m3Then the mixture is sent into a desulfurizing tower 1 filled with organic sulfur hydrolysis catalyst, carbonyl sulfur and carbon disulfide are converted into hydrogen sulfide through hydrogenation conversion and catalytic hydrolysis under the condition that the temperature is 180 ℃, and the total conversion efficiency reaches 96 percent; the converted flue gas is cooled to 120 ℃ through a heat exchanger, and then is sent into a desulfurizing tower 2 filled with a desulfurizing catalyst to purify hydrogen sulfide, and the hydrogen sulfide is converted into elemental sulfur, metal sulfide and sulfate through catalytic oxidation under the action of a desulfurizing agent; the total sulfur content in the purified flue gas is 10mg/m3(ii) a Then the purified flue gas is sent into a smelting furnace for combustion; soaking the desulfurizer in 8wt% sodium hydroxide solution for 5 times until the sodium hydroxide solution is colorless, washing the regenerant on the surface of the desulfurizer with deionized water at 20 ℃, drying the desulfurizer at 80 ℃ for 14 hours, and recycling the desulfurization catalyst for 3 times to control the total sulfur emission to be 20mg/m3The following.
Example 4
1. Taking alumina as a carrier and magnesium nitrate, potassium carbonate and molybdenum nitrate as impregnation liquid, sequentially adding a magnesium nitrate solution, a potassium carbonate solution and a molybdenum nitrate solution into the carrier according to an equal-volume impregnation method, adding one solution each time, standing for 6 hours,drying at 100 deg.C for 8 hr until the last solution is added; wherein M isMg+MK+MMo:MCarrier=4%,MMg:MK:MMoSoaking at 40 ℃ for 12h, drying at 100 ℃ for 24h, and roasting at 350 ℃ for 4h to obtain the organic sulfur hydrolysis catalyst, wherein the ratio is 1:1: 2;
2. adding copper acetate solution into carrier by using 10X molecular sieve as carrier and copper acetate as impregnation liquid according to equal volume impregnation method, wherein M isCu:MCarrier=5%, soaking at 40 ℃ for 12h, drying at 100 ℃ for 24h, and roasting at 350 ℃ for 4h to obtain the desulfurization catalyst;
3. mixed gas (V) for simulating blast furnace gas and coke oven gas prepared in laboratoryBlast furnace:VCoke oven=12: 1) gas flow is 500mL/min, and COS concentration in the flue gas is 115mg/m3The carbon disulfide concentration is 5mg/m3Hydrogen sulfide concentration of 30mg/m3The oxygen concentration is 0.6%, the hydrogen concentration is 5.7%, and the hydrogen chloride concentration is 45mg/m3CO concentration of 20% CO2The concentration is 20 percent, and the methane concentration is 3 percent;
4. oxygen concentration and hydrogen chloride were reduced to 0.02% and 5mg/m, respectively, by deoxidation and dechlorination with adsorbents in a fixed bed before organic sulfur conversion was carried out3Then sending the mixture into a fixed bed filled with an organic sulfur hydrolysis catalyst, and converting carbonyl sulfur and carbon disulfide into hydrogen sulfide at the temperature of 200 ℃, wherein the total conversion efficiency reaches 99%; then, the mixed gas is cooled by a cooling bottle and is sent into a fixed bed filled with a desulfurization catalyst, the reaction temperature is 120 ℃, and hydrogen sulfide is converted into elemental sulfur, metal sulfide and sulfate by catalytic oxidation under the action of a desulfurizing agent; the total sulfur content in the purified flue gas is 5mg/m3。
Claims (4)
1. A method for improving the combustion heat value of blast furnace gas and simultaneously removing organic sulfur and inorganic sulfur is characterized in that: mixing blast furnace gas and coke oven gas according to the volume ratio of 6-12: 1, dedusting, deoxidizing and dechlorinating the mixed gas, and enabling organic sulfur in the mixed gas to pass through catalytic hydrolysis reaction and hydrogenation conversion reaction at 100-200 ℃ under the action of an organic sulfur hydrolysis catalystGenerating inorganic sulfur, hydrolyzing the mixed gas to convert organic sulfur, reducing the temperature of the mixed gas to 80-150 ℃ by using a heat exchanger, introducing oxygen into the mixed gas to ensure that the oxygen content is 0.05-0.8% by volume, and under the action of a desulfurization catalyst, adding H in the mixed gas2S is subjected to catalytic oxidation reaction at 80-150 ℃ to generate elemental sulfur, metal sulfides and sulfates, and the elemental sulfur, the metal sulfides and the sulfates are adsorbed on a catalyst, so that the purpose of improving the combustion heat value of blast furnace gas and simultaneously removing organic sulfur and inorganic sulfur is achieved.
2. The method for increasing the combustion heat value of blast furnace gas while removing organic sulfur and inorganic sulfur according to claim 1, wherein: the dust concentration after dust removal is less than 5mg/m3(ii) a After deoxidation and dechlorination, the concentrations of oxygen and hydrogen chloride are reduced to 0.05% and 10mg/m respectively3The following.
3. The method for increasing the combustion heat value of blast furnace gas while removing organic sulfur and inorganic sulfur according to claim 1, wherein: the organic sulfur hydrolysis catalyst is prepared by using one of active carbon, alumina and molecular sieve as a carrier and one or more of molybdenum salt, potassium salt, magnesium salt, cerium salt and cobalt salt as an impregnant through the steps of impregnation by an equal-volume impregnation method, drying and roasting.
4. The method for increasing the combustion heat value of blast furnace gas while removing organic sulfur and inorganic sulfur according to claim 1, wherein: the desulfurization catalyst is prepared by taking one of active carbon, alumina and molecular sieve as a carrier and one or more of copper salt, cerium salt, iron salt and cobalt salt as an impregnant through soaking, drying and roasting by an equal volume soaking method.
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