CN113930264A - Improved organic sulfur desulfurizer and use method thereof for blast furnace gas desulfurization - Google Patents

Improved organic sulfur desulfurizer and use method thereof for blast furnace gas desulfurization Download PDF

Info

Publication number
CN113930264A
CN113930264A CN202111114858.7A CN202111114858A CN113930264A CN 113930264 A CN113930264 A CN 113930264A CN 202111114858 A CN202111114858 A CN 202111114858A CN 113930264 A CN113930264 A CN 113930264A
Authority
CN
China
Prior art keywords
blast furnace
oxide
furnace gas
desulfurizer
organic sulfur
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202111114858.7A
Other languages
Chinese (zh)
Inventor
田黎霞
何俊良
刘建英
徐成华
杨皓
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Chengdu University of Information Technology
Original Assignee
Chengdu University of Information Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Chengdu University of Information Technology filed Critical Chengdu University of Information Technology
Priority to CN202111114858.7A priority Critical patent/CN113930264A/en
Publication of CN113930264A publication Critical patent/CN113930264A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10KPURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
    • C10K1/00Purifying combustible gases containing carbon monoxide
    • C10K1/20Purifying combustible gases containing carbon monoxide by treating with solids; Regenerating spent purifying masses
    • C10K1/205Methods and apparatus for treating the purifying masses without their regeneration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1456Removing acid components
    • B01D53/1468Removing hydrogen sulfide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1493Selection of liquid materials for use as absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/26Drying gases or vapours
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/508Sulfur oxides by treating the gases with solids
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/81Solid phase processes
    • B01D53/82Solid phase processes with stationary reactants
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10KPURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
    • C10K1/00Purifying combustible gases containing carbon monoxide
    • C10K1/002Removal of contaminants
    • C10K1/003Removal of contaminants of acid contaminants, e.g. acid gas removal
    • C10K1/004Sulfur containing contaminants, e.g. hydrogen sulfide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/204Carbon monoxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/30Alkali metal compounds
    • B01D2251/304Alkali metal compounds of sodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/30Alkali metal compounds
    • B01D2251/306Alkali metal compounds of potassium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20738Iron
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/30Silica
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/80Type of catalytic reaction
    • B01D2255/808Hydrolytic
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/302Sulfur oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/304Hydrogen sulfide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/308Carbonoxysulfide COS

Abstract

The patent relates to an improved organic sulfur desulfurizer and a use method thereof for blast furnace gas desulfurization, belonging to the field of energy conservation and environmental protection. The desulfurizer adopts ferric oxide and silicon dioxide hydrogel raw materials to prepare a silicon-oxygen-iron framework structure, sodium oxide-potassium oxide with the molar ratio of 0.1-5% is loaded on the surface of the silicon-oxygen-iron framework, the desulfurizer is heated to 150-280 ℃, the desulfurizer is used as a reducing agent after being dehydrated by blast furnace gas, carbon monoxide reduces ferric oxide into ferrous oxide, the concentration of carbon monoxide at an inlet and an outlet in the blast furnace gas is basically unchanged, and activation is completed; the desulfurizing agent is cooled and used for organic sulfur conversion and absorption of blast furnace gas at 100-150 ℃, sodium oxide-potassium oxide is used as an organic sulfur hydrolysis conversion active center, and ferrous oxide is used as a hydrogen sulfide absorbent.

Description

Improved organic sulfur desulfurizer and use method thereof for blast furnace gas desulfurization
Technical Field
The invention relates to the field of energy conservation and environmental protection, and discloses a method for solving the problems that the existing desulfurizer is low in sulfur capacity, high in production cost and capable of discharging waste water and waste residues in the production process.
Background
The blast furnace gas is a byproduct containing CO and CO in the iron-making process of iron and steel enterprises2、N2、H2Of low calorific value combustible gas. Raw blast furnace gas also contains a large amount of dust and sulfides, which are mainly divided into organic sulfur and inorganic sulfur, and the organic sulfur accounts for a higher proportion than the inorganic sulfur. The main components of the organic sulfur comprise carbonyl sulfide, carbon disulfide, thioether mercaptan, thiophene and the like, and the carbonyl sulfide is taken as the main component; the inorganic sulfur mainly contains hydrogen sulfide, sulfur dioxide, etc. The emission of sulfur dioxide in flue gas of blast furnace gas after untreated combustion exceeds the standard. Therefore, the blast furnace gas needs to be purified to remove dust and sulfides carried in the gas before combustion and power generation.
In the existing blast furnace gas purification process, the dust removal link is a dry dust removal process which replaces the traditional wet process. In the aspect of sulfide removal, a wet scrubbing device is arranged behind a TRT device in the mature method at present. The method can effectively remove inorganic sulfur such as H in blast furnace gas2S,SO2,SO3But the organic sulfur in the blast furnace gas can not be removed, resulting in SO in the flue gas after combustion2The discharge is not up to standard, and the moisture carried by the wet desulphurization can enter subsequent pipeline equipment to cause corrosion. The removal of organic sulfur, especially COS, is an important link of blast furnace gas fine desulfurization, and the currently effective solution is to convert COS into H through catalytic hydrolysis2And removing the S.
CN111334341A of Maguangwei and the like of Shandong Zhongzhou blue environmental protection science and technology Limited company announces a desulfurization method of blast furnace gas, and mainly solves the technical problems that in the prior art, sulfide and dust in blast furnace gas purification cannot be completely removed, so that a gas pipeline is easy to corrode, and sulfur dioxide emission after the blast furnace gas is combusted exceeds the standard. The method comprises the following steps: a. blast furnace gas from a blast furnace enters a dry dedusting unit, and a material flow I is formed after dedusting; b. the material flow I enters an organic sulfur conversion device filled with a medium-temperature hydrolysis catalyst, the catalyst is a microcrystalline material catalyst, and the material flow I is subjected to catalytic conversion to form a material flow II; c. the material flow II enters a TRT power generation unit to generate power to form a material flow III; d. the material flow III enters a desulfurizing tower and forms a material flow IV after being absorbed by active carbon or an iron oxide fine desulfurizing agent; e. the material flow IV enters a subsequent blast furnace gas use workshop section, so that the problem is better solved, and the method can be used for industrial production of blast furnace gas purification. The method adopts medium-temperature hydrolysis for organic sulfur, and the hydrolysis agent is easy to inactivate, short in service life and high in price.
CN112940795A of Lixianwei et al, Hubei Huateler purification science and technology, Inc., Baoshan iron and Steel, Inc., announced an iron-based desulfurizer for blast furnace gas, wherein the desulfurizer comprises the following main raw materials: 30-50wt% of ferrous sulfate, 20-30wt% of calcium hydroxide, 10-40wt% of carbide slag, 5-15wt% of fly ash and 5-15wt% of sawdust. The solid reacts in the kneading and forming process to generate a desulfurizer precursor, and then the desulfurizer precursor is naturally oxidized into a finished desulfurizer product. The desulfurizer prepared by the method has high sulfur capacity, working sulfur capacity of 35-45wt%, saturated sulfur capacity of 60-70wt%, simple preparation process, no waste water and waste residue in the production process, low production cost and suitability for large-scale production. The process has no significant conversion to organic sulfur.
CN1102619648A of Jianellong, Fuzhou university, and the like, announces a copper-cobalt-based catalyst for organic sulfur hydrolysis removal and a preparation method thereof, wherein the copper-doped cobaltosic oxide catalyst is prepared by combining a hydrothermal auxiliary coprecipitation synthesis method with high-temperature roasting. The prepared copper-cobalt-based catalyst has high crystallinity, is nano-flaky, mainly takes mesopores, has high ion diffusion rate and has high catalytic hydrolysis performance on carbonyl sulfide. When the reaction temperature is 70 ℃, the conversion rate of COS reaches up to 100 percent, and the method is suitable for low-temperature catalytic hydrolysis desulfurization of carbonyl sulfide-containing gases such as blast furnace gas, natural gas and the like. The method adopts low-temperature hydrolysis for organic sulfur, and the working temperature of the hydrolysis agent is higher than 100 ℃, so that the method is easy to inactivate, short in service life and high in price.
At present, the desulfurization of blast furnace gas generally adopts organic sulfur hydrolytic agent to convert COS into H2S, then using a desulfurizing agent to react H2And (4) S absorption. Blast furnace gas de-H2S is usually activated carbon desulfurizer or ferric oxide desulfurizer. The biggest problems of the method are that the hydrolysis catalyst is high in manufacturing cost and is quickly deactivated because the hydrolysis catalyst is easy to block pores and deactivate. The original skeleton structure can not be regenerated and reused.
Disclosure of Invention
The improved organic sulfur desulfurizer is used in blast furnace gas desulfurization and is prepared with ferric oxide and silica hydrogel as material and through a Si-O-Fe skeleton structure. Loading sodium oxide-potassium oxide with a molar ratio of 0.1-5% on the surface of a silicon-oxygen-iron framework, heating a desulfurizer to 150-280 ℃ for dehydration, using the dehydrated blast furnace gas as a reducing agent, reducing iron oxide by carbon monoxide to obtain ferrous oxide until the concentration of carbon monoxide at an inlet and an outlet in the blast furnace gas is basically unchanged, and completing activation; cooling the desulfurizer, and using the cooled desulfurizer for conversion and absorption of organic sulfur in blast furnace gas at 100-150 ℃, wherein sodium oxide-potassium oxide is used as an organic sulfur hydrolysis conversion active center, and ferrous oxide is used as a hydrogen sulfide absorbent. The desulfurizer has the capabilities of hydrolysis conversion and hydrogen sulfide absorption, is low in cost, can be directly used for sintering the ferrosilicon pellets after being absorbed and saturated by the desulfurizer, is suitable for being used as a ferrosilicon pellet sintering raw material, is combined with calcium carbonate, potassium oxide and sodium to be solidified, and does not generate dangerous waste.
Detailed Description
Example 1:
the desulfurizer adopts ferric oxide and silicon dioxide hydrogel raw materials to prepare a silicon-oxygen-iron framework structure. Sodium oxide-potassium oxide with the molar ratio of 0.1% is loaded on the surface of the silicon-oxygen-iron framework, the desulfurizer is heated to 150 ℃, the desulfurizer is used as a reducing agent after being dehydrated by blast furnace gas, carbon monoxide reduces iron oxide into ferrous oxide until the concentration of carbon monoxide at an inlet and an outlet in the blast furnace gas is basically unchanged, and activation is completed; cooling the desulfurizing agent, and using the cooling agent for conversion and absorption of organic sulfur in blast furnace gas at 120 ℃, wherein sodium oxide-potassium oxide is used as an organic sulfur hydrolysis conversion active center, and ferrous oxide is used as a hydrogen sulfide absorbent.
Example 2:
the desulfurizer adopts ferric oxide and silicon dioxide hydrogel raw materials to prepare a silicon-oxygen-iron framework structure. Loading sodium oxide-potassium oxide with a molar ratio of 3% on the surface of a silicon-oxygen-iron framework, heating a desulfurizer to 200 ℃, using the dehydrated blast furnace gas as a reducing agent, reducing iron oxide into ferrous oxide by carbon monoxide until the concentration of carbon monoxide at an inlet and an outlet in the blast furnace gas is basically unchanged, and completing activation; cooling the desulfurizing agent, and using the cooling agent for conversion and absorption of organic sulfur in blast furnace gas at 120 ℃, wherein sodium oxide-potassium oxide is used as an organic sulfur hydrolysis conversion active center, and ferrous oxide is used as a hydrogen sulfide absorbent.
Example 3:
the desulfurizer adopts ferric oxide and silicon dioxide hydrogel raw materials to prepare a silicon-oxygen-iron framework structure. Loading sodium oxide-potassium oxide with a molar ratio of 5% on the surface of a silicon-oxygen-iron framework, heating a desulfurizer to 280 ℃, using the dehydrated blast furnace gas as a reducing agent, reducing iron oxide into ferrous oxide by carbon monoxide until the concentration of carbon monoxide at an inlet and an outlet in the blast furnace gas is basically unchanged, and completing activation; cooling the desulfurizing agent, and using the cooling agent for conversion and absorption of organic sulfur in blast furnace gas at 120 ℃, wherein sodium oxide-potassium oxide is used as an organic sulfur hydrolysis conversion active center, and ferrous oxide is used as a hydrogen sulfide absorbent.
The invention combines the current blast furnace gas desulfurization process flow in the steel industry to invent an improved organic sulfur desulfurizer, the desulfurizer has the capabilities of hydrolysis conversion and hydrogen sulfide absorption, the desulfurizer is cheap, can be directly used for sintering ferrosilicon pellets after being absorbed and saturated, and does not generate dangerous waste.

Claims (1)

1. An improved organic sulfur desulfurizer and a use method thereof for blast furnace gas desulfurization, wherein the desulfurizer adopts ferric oxide and silicon dioxide hydrogel raw materials to prepare a silicon-oxygen-iron framework structure, sodium oxide-potassium oxide with a molar ratio of 0.1-5% is loaded on the surface of the silicon-oxygen-iron framework, the desulfurizer is heated to 150-280 ℃, the desulfurizer is used as a reducing agent after being dehydrated by blast furnace gas, carbon monoxide reduces ferric oxide into ferrous oxide, and activation is completed until the concentration of carbon monoxide at an inlet and an outlet in the blast furnace gas is basically unchanged; the desulfurizing agent is cooled and used for organic sulfur conversion and absorption of blast furnace gas at 100-150 ℃, sodium oxide-potassium oxide is used as an organic sulfur hydrolysis conversion active center, and ferrous oxide is used as a hydrogen sulfide absorbent.
CN202111114858.7A 2021-09-23 2021-09-23 Improved organic sulfur desulfurizer and use method thereof for blast furnace gas desulfurization Pending CN113930264A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111114858.7A CN113930264A (en) 2021-09-23 2021-09-23 Improved organic sulfur desulfurizer and use method thereof for blast furnace gas desulfurization

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111114858.7A CN113930264A (en) 2021-09-23 2021-09-23 Improved organic sulfur desulfurizer and use method thereof for blast furnace gas desulfurization

Publications (1)

Publication Number Publication Date
CN113930264A true CN113930264A (en) 2022-01-14

Family

ID=79276461

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111114858.7A Pending CN113930264A (en) 2021-09-23 2021-09-23 Improved organic sulfur desulfurizer and use method thereof for blast furnace gas desulfurization

Country Status (1)

Country Link
CN (1) CN113930264A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115738599A (en) * 2022-11-23 2023-03-07 攀钢集团攀枝花钢铁研究院有限公司 Simultaneous absorption of NO x And preparation method of CO complexing denitration liquid

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115738599A (en) * 2022-11-23 2023-03-07 攀钢集团攀枝花钢铁研究院有限公司 Simultaneous absorption of NO x And preparation method of CO complexing denitration liquid

Similar Documents

Publication Publication Date Title
CN102303883B (en) Method for preparing calcium oxide and sulfur by double-atmosphere fluidized roasting of desulfurated gypsum
CN101249373B (en) Flue gas desulfurization agent preparation method
CN101280227B (en) Medium-high temperature gas desulfurizer and preparation thereof
CN109482049B (en) Dry desulfurization, denitrification and purification integrated process for coke oven flue gas
CN103318846B (en) Method for obtaining sulfur from sulfur compounds in coal chemical plant and electric power plant
CN112593034B (en) Dry-method cooperative deacidification system and method for blast furnace clean gas
CN111334339A (en) Fine desulfurization method for blast furnace gas
CN106379868A (en) Method for preparing sulfuric acid by burning sulfur-containing waste liquid
CN111334341A (en) Method for desulfurizing blast furnace gas
CN110893312A (en) Novel high-efficiency desulfurizer and preparation method thereof
CN105169943A (en) Integrated system for coke oven flue gas desulfurization and denitrification and waste heat recovery
CN103007718A (en) Wet redox, desulfuration and resource utilization method for flue gas
CN113930264A (en) Improved organic sulfur desulfurizer and use method thereof for blast furnace gas desulfurization
CN101979130B (en) Method for removing hydrogen sulfide from industrial gas in recycling way
CN202864915U (en) Sulfur recovery and tail gas treatment device
CN101502747A (en) Flue gas integrated desulphurization and denitrification catalyst
CN201832541U (en) Smoke gas contaminant remover of sintering machine
KR101048425B1 (en) Desulfuring catalyst and method for preparing the same
CN109499344B (en) Calcium/magnesium-based wet desulphurization and calcium sulfite/magnesium sulfite resource utilization system and process
CN112574788B (en) Method for purifying blast furnace gas
CN102635873A (en) Method for capturing and circulating carbon dioxide in ordinary power plant boiler
JP2010215802A (en) Dry gas purification facility and coal gasification combined power generation facility
CN1133732C (en) Desulfurizing agent of zinc ferrite for high-temp gas and its preparing process
CN216155799U (en) Blast furnace gas desulfurization ultra-clean system
CN115340887B (en) Blast furnace gas fine desulfurization and sulfur recycling process

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination