[go: up one dir, main page]

CN117563556A - Renewable load-type desulfurizing agent and preparation method thereof - Google Patents

Renewable load-type desulfurizing agent and preparation method thereof Download PDF

Info

Publication number
CN117563556A
CN117563556A CN202410060773.2A CN202410060773A CN117563556A CN 117563556 A CN117563556 A CN 117563556A CN 202410060773 A CN202410060773 A CN 202410060773A CN 117563556 A CN117563556 A CN 117563556A
Authority
CN
China
Prior art keywords
desulfurizing agent
agent
sulfur
surfactant
pore
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.)
Granted
Application number
CN202410060773.2A
Other languages
Chinese (zh)
Other versions
CN117563556B (en
Inventor
张晓红
黄咏峰
丁腾
蒋化
陈莎
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.)
Beijing Beida Pioneer Technology Co ltd
Original Assignee
Beijing Beida Pioneer Technology Co ltd
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 Beijing Beida Pioneer Technology Co ltd filed Critical Beijing Beida Pioneer Technology Co ltd
Priority to CN202410060773.2A priority Critical patent/CN117563556B/en
Publication of CN117563556A publication Critical patent/CN117563556A/en
Application granted granted Critical
Publication of CN117563556B publication Critical patent/CN117563556B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3202Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the carrier, support or substrate used for impregnation or coating
    • B01J20/3204Inorganic carriers, supports or substrates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • B01J20/3234Inorganic material layers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/345Regenerating or reactivating using a particular desorbing compound or mixture
    • B01J20/3458Regenerating or reactivating using a particular desorbing compound or mixture in the gas phase
    • 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
    • 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
    • C10K1/26Regeneration of the purifying material contains also apparatus for the regeneration of the purifying material
    • 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
    • C10K1/32Purifying combustible gases containing carbon monoxide with selectively adsorptive solids, e.g. active carbon

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Analytical Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Combustion & Propulsion (AREA)
  • Inorganic Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention relates to a renewable load-type desulfurizing agent and a preparation method thereof, wherein the renewable load-type desulfurizing agent comprises the following raw materials in parts by mass: 100 parts of active carbon and 150-250 parts of impregnating solution, wherein the impregnating solution comprises metal nitrate, surfactant, pore-forming agent starch and strength enhancer nano SiO 2 The method comprises the steps of carrying out a first treatment on the surface of the The renewable supported desulfurization agent is activated carbon leachingSoaking in the soaking solution, taking out, drying, and calcining under inert atmosphere. The desulfurizing agent has high adsorption efficiency on sulfide in waste gas, has good regeneration performance, regenerates the desulfurizing agent by adopting a small amount of purified industrial gas at high temperature in situ, realizes the recycling of the desulfurizing agent and the sulfur-containing industrial gas, and has strong hydrogen sulfide adsorption capability. The method of the invention is simple, low in investment and low in operation cost.

Description

Renewable load-type desulfurizing agent and preparation method thereof
Technical Field
The invention belongs to the technical field of environmental protection, and particularly relates to a renewable load type desulfurizing agent and a preparation method thereof.
Background
The steel production mainly takes a long process, and a large amount of blast furnace gas is generated in the blast furnace ironmaking process. The yield of blast furnace gas is about 1500-2000Nm per ton of iron 3 The main component is CO 2 (16~22%)、CO(18~24%)、H 2 (0.5~2.5%)、 N 2 (56-63%)、C x H y (2-4%), and also dust, moisture, small amounts of chlorides and small amounts of sulfur-containing species, wherein the sulfur-containing species are in the form of COS, H 2 S is mainly the concentration of 80-220 mg/m 3 Heat value 3000-4000kJ/Nm 3 The tapping temperature is 100-160 ℃. The blast furnace gas is usually sent to a hot blast stove, a heating furnace, a boiler, a gas unit and the like in a fuel mode for combustion, and sulfide in the blast furnace gas can be burnt to form SO 2 Is discharged into the air.
Currently, four blast furnace gas desulfurization methods are industrially applied in China, and the first method is hydrolysis and active carbon dry desulfurization technology; the second is hydrolysis + wet desulfurization technology; the third is NSAD (Nature Sulfur Autotrophic Denitrifi-cation) desulfurization technology; the fourth is the microcrystalline adsorption desulfurization technique. The active carbon dry desulfurization technology has the defects of large filling amount of desulfurizing agent, frequent replacement of the desulfurizing agent, treatment of the desulfurizing agent and the like. Both NSAD and microcrystalline adsorption desulfurization technologies are renewable dry desulfurization technologies, and have the defects of short service life, high running cost and the like due to higher regeneration temperature and difficult regeneration. The existing desulfurizing agent can not meet the actual industrial application requirements, and the development of a novel renewable solid desulfurizing agent with high desulfurizing efficiency, speed and selectivity is still one of the targets of gas desulfurization technology.
University of Zhejiang CN100560185C discloses a renewable load type desulfurizing agent and a preparation method thereof. The ionic polymer is loaded on the porous solid material, and the desulfurizing agent has the advantages of high absorption rate, good selectivity and large absorption capacity; the regeneration is easy, and the water purifier can be recycled for multiple times; the mechanical strength is high, and the mechanical strength and the absorption performance of the water vapor are not affected after the water vapor is absorbed to a certain extent; the desorption tolerance temperature is high. However, the preparation cost is high, the preparation process is complex, and the polymerization process needs 6-12 hours. The China academy of sciences Shanxi coal chemistry institute CN1102424C discloses a method for regenerating a copper series desulfurizing agent, which comprises the steps of heating the sulfur-absorbed and saturated copper series desulfurizing agent to 300-500 ℃ in an ammonia-containing gas atmosphere with a space velocity of 700-1200h -1 The regeneration time is 30-60 minutes. The invention has the advantages of simple regeneration process, easy operation, no reduction of activity of the desulfurizer after regeneration, no strong exothermic reaction during secondary desulfurization, no pre-oxidation treatment after regeneration, direct use for desulfurization, convenient storage and transportation of liquid ammonia, and low comprehensive desulfurization cost. However, this method has a high regeneration temperature and a high device cost. CN100376310C provides a method for regenerating vanadium-carbon-based desulfurizing agent: the sulfur-absorbing V/AC composite desulfurizing agent containing transition metal is filled into a regeneration reactor and H is used 2 The gas is used as a reducing agent, a transition metal catalyst is added into a vanadium-carbon-based composite desulfurizing agent containing transition metal or a vanadium-carbon desulfurizing agent without transition metal, and a closed circulation gas circuit is adopted for regeneration. Solid sulfur is obtained in the process, so that the subsequent treatment is avoided. The regenerated recycle gas can be reused. CN101664689B relates to a method for preparing active carbon desulfurizing agent by using a hybrid fresnel method and a method thereof. Mixing cupric oxide or basic cupric carbonate and pulverized coal or charcoal powder with a certain amount of water, adding tar, rolling, extruding to form strips, drying, and activating to obtain the final product. The active carbon desulfurizer prepared by the method has more developed pore system and specific surface area exceeding 1000m than the active carbon desulfurizer prepared by the impregnation method 2 And/g, the desulfurizing agent is activated by water vapor, the activation temperature is 850 ℃, and the activation time is 180 minutes.
CN102500323B provides a modified active carbon desulfurizing agent and its preparation method and useA method for treating hydrogen sulfide waste gas. The modified active carbon desulfurizing agent is obtained by impregnating active carbon with an active agent mixed solution comprising phenol, acetone, sodium carbonate, ferric nitrate and an organic solvent, and then drying and roasting. The modified active carbon desulfurizing agent of the invention converts hydrogen sulfide in waste gas into sulfur dioxide under normal temperature and pressure by utilizing the adsorption and catalytic oxidation action, and then is converted into SO in water phase by washing 4 2- And is removed. Avoiding the defect that the desulfurizing agent needs to be periodically desorbed and regenerated due to the blockage caused by saturated adsorption and the generation of elemental sulfur. Compared with the common active carbon desulfurization process, the process has the advantages of high hydrogen sulfide removal rate, long service life of the desulfurizing agent, low operation cost, simple operation and management and the like. Chinese patent CN1415402A uses ZnO-TiO as main component 2 -Al 2 O 3 Can be used as desulfurizing agent of H 2 S and organic sulfur are removed simultaneously, but the sulfur removal agent is required to be used at a high temperature of 180-320 ℃ and has high requirements on application conditions. CN1186841a proposes a modified activated carbon for desulfurizing waste gas at normal temperature, which can be used for purifying chemical raw material gases such as synthetic ammonia, petroleum and natural gas, but mainly aims at organic sulfides (such as CS 2 ) Has good absorption effect on inorganic sulfides (such as sulfur H) 2 S) the treatment effect of the gas is poor, and the modified activated carbon is used as a desulfurizing agent to remove hydrogen sulfide in the waste gas, so that the hydrogen sulfide is required to be periodically desorbed, regenerated, cleaned or replaced, and the defects of continuous reduction of the hydrogen sulfide removal rate along with the prolonging of the service time of the desulfurizing agent, short service life of the desulfurizing agent, high operation cost, complex operation management and the like exist.
The desulfurizing agent has the defects of high desulfurizing agent preparation cost, long preparation flow, low sulfur capacity, complex desulfurizing agent regeneration process, high regeneration temperature, poor inorganic sulfide hydrogen sulfide treatment effect, short service life and the like. The invention aims to provide a renewable and industrially applicable blast furnace gas desulfurizing agent and an application method thereof. The desulfurizing agent is subjected to chemical adsorption on hydrogen sulfide generated after hydrolysis of blast furnace gas at a lower temperature, and is regenerated at a high temperature by using part of purified blast furnace gas after adsorption saturation, and contains a large amount of carbonyl sulfide and hydrogen sulfideIs combusted in the sintering section to convert hydrogen sulfide and carbonyl sulfide into SO 2 And then desulfurization treatment is carried out.
Disclosure of Invention
The invention aims to provide a renewable supported metal oxide desulfurizer, and the active substances on the supported metal oxide desulfurizer can be one or two of copper oxide, zinc oxide, ferric oxide and manganese oxide, and the addition of the active substances improves the thermal stability of the desulfurizer, and the adsorbent has higher desulfurization performance due to the synergistic effect of the metal oxides. The invention adopts the compound surfactant, the pore-forming agent and the strength enhancer, and enhances the mechanical strength of the carrier while keeping the specific surface area and the pore structure of the carrier increased. The desulfurizing agent obtained by the invention adopts the principle of temperature swing adsorption, is adsorbed at low temperature, and is regenerated by partially purified blast furnace gas at high temperature in situ, so that the recycling of the desulfurizing agent is realized, the hydrogen sulfide adsorption capability is strong, the regeneration system is simple, and the physical loss of the adsorbent is avoided. The running cost is far lower than that of disposable adsorbents.
In order to achieve the above purpose, the present invention adopts the following technical scheme:
the renewable supported desulfurizing agent comprises the following raw materials in parts by mass: 100 parts of active carbon and 150-250 parts of impregnating solution, wherein the impregnating solution comprises metal nitrate, surfactant, pore-forming agent starch and strength enhancer nano SiO 2 The method comprises the steps of carrying out a first treatment on the surface of the The renewable load type desulfurizing agent is obtained by dipping active carbon in dipping liquid, taking out, drying and calcining under inert atmosphere; the metal nitrate is selected from Fe (NO) 3 ) 3 、Cu(NO 3 ) 2 、Mn(NO 3 ) 2 、Zn(NO 3 ) 2 At least one of them.
Further, the ratio of the activated carbon to the impregnating solution satisfies the isovolumetric impregnation method, that is, the activated carbon is impregnated in the impregnating solution of saturated adsorption amount of the activated carbon.
Further, the specific surface area of the activated carbon is 250-350 m 2 Per gram, pore volume of 0.25-0.3. 0.3 cm 3 /g, pore diameter 5.5-6nm; the watchThe surfactant is selected from nonionic surfactant and/or anionic surfactant, the nonionic surfactant is selected from at least one of fatty alcohol polyoxyethylene ether, nonylphenol polyoxyethylene ether, polyoxyethylene ether sorbitol fatty acid ester and laurinol polyoxyethylene ether, the anionic surfactant is selected from at least one of sodium dodecyl benzene sulfonate and sodium dodecyl sulfate, and the strength enhancer is nano SiO 2 The particle size of (2) is 200-400nm.
Further, in the impregnating solution, the solvent is at least one selected from methanol, ethanol and isopropanol, the molar concentration of metal nitrate is 1-2M, the mass concentration of the surfactant is 20-30 g/L, the mass concentration of the pore-forming agent is 40-50g/L, and the mass concentration of the strength enhancer is 20-30 g/L.
Preferably, the impregnating solution also comprises 0.01-0.02M La (NO) 3 ) 3 And 0.05-0.08M Co (NO) 3 ) 2 . The inventor has unexpectedly found that the desulfurization effect of the obtained load type desulfurizing agent is not changed by adding a small amount of lanthanum and cobalt into the impregnating solution, but the regeneration capability of the load type desulfurizing agent is obviously improved, the load type desulfurizing agent circulates for 100 times after regeneration, the sulfur capacity and the sulfur capacity after the first regeneration are little attenuated, and the load type desulfurizing agent has excellent desulfurizing agent regeneration capability; more importantly, the regeneration of the desulfurizing agent can achieve good regenerating effect of the desulfurizing agent by using a small amount of regeneration process gas at a lower temperature. The inventors have also found that the best regeneration capacity improvement can be achieved only by compounding lanthanum and cobalt, so that other rare earth metals such as Ce and Y are added in the same molar amount; or other transition metals with the same molar quantity are added to replace Co, and the effect of improving the regeneration capability of the desulfurizing agent by adding La and Co cannot be achieved. The invention also provides a preparation method of the renewable load type desulfurizing agent, which comprises the following steps:
(S1) dispersing metal nitrate, a surfactant, a pore-forming agent and a strength enhancer in an alcohol solvent, and fully mixing to obtain an impregnating solution;
and (S2) under the ultrasonic and stirring conditions, soaking the activated carbon in the soaking solution, filtering, drying to obtain a carrier loaded with the active metal compound, and roasting in an inert atmosphere to obtain the modified activated carbon desulfurizing agent.
Further, in the step (S1), the activated carbon is subjected to alkali treatment, specifically: adding active carbon into a solution containing sodium hydroxide/potassium carbonate/potassium hydroxide at 60-80 ℃ for alkali washing, and then drying at 60-80 ℃.
Further, in the step (S2), the impregnation is carried out at 20-40 ℃ for 10-15 hours; drying is not particularly limited, such as oven drying, vacuum drying; roasting for 2-4 hours at 240-300 ℃ in an inert atmosphere; the inert atmosphere is nitrogen and/or argon; the roasting is carried out for 3-5 hours at 240-300 ℃.
Further, in the step (S2), 0.01-0.02M La (NO) is added in the preparation of the impregnating solution 3 ) 3 And 0.05-0.08M Co (NO) 3 ) 2 . In the impregnating solution, the molar concentration of metal nitrate is 1-2M, the mass concentration of surfactant is 20-30 g/L, the mass concentration of pore-forming agent is 40-50g/L, and the concentration of strength enhancer is 20-30 g/L.
Further, in step (S2), the conditions of sonication and stirring are well known in the art, such as stirring speeds of 500-800rpm and ultrasonic frequencies of 100-160kHz.
The invention also provides a method for desulfurizing industrial gas, which comprises the following steps: and (3) carrying out adsorption desulfurization on the sulfur-containing industrial gas by the renewable load-type desulfurizing agent.
Further, the sulfur-containing industrial gas is an industrial waste gas containing hydrogen sulfide and carbon monoxide, such as blast furnace gas, coke oven gas, and converter gas. The desulfurizing agent of the invention carries out desulfurization treatment on industrial waste gas containing hydrogen sulfide and carbon monoxide, and the desulfurizing agent which is saturated by adsorption can be regenerated by adopting the gas after desulfurization and purification, namely, the regenerated gas is from the gas after purification treatment, and the introduction of the regenerated process gas is not needed. The sulfur-containing industrial gas contains 100-300 mg/m 3 H 2 S,15-30 vol% CO; such as blast furnace gas, which contains 100-300 mg/m 3 H 2 S,15-30 vol%CO 2 15-30 vol% CO,1-3 vol% H 2 The balance being N 2 And inevitablyImpurities; h in purified industrial gas 2 S and COS (carbonyl sulfide) contents lower than 10 mg/m 3
Further, the adsorption temperature is 50-80 ℃, such as 55 ℃, 60 ℃, 65 ℃, 70 ℃, 75 ℃; the adsorption airspeed is 500-3000h -1 Such as 1500h -1 、2000h -1 、2500h -1
The invention also provides a regeneration method of the desulfurizing agent, which adopts the principle of temperature swing adsorption and comprises the following steps: regenerating the desulfurizing agent with saturated adsorption at 120-180 ℃ by using industrial gas after desulfurization and purification, wherein the purified industrial gas H 2 S and COS contents lower than 10 mg/m 3 The volume of the purified sulfur-containing industrial gas used in the regeneration is 3-5% of the volume of the sulfur-containing industrial gas saturated by the desulfurizing agent. For example, the sulfur-containing industrial gas is blast furnace gas. The determination method of adsorption saturation is well known in the art, such as detecting H in tail gas 2 S and COS contents, to H 2 The total content of S and COS exceeds 10 mg/m 3 After that, adsorption saturation was considered to be reached.
The desulfurizer prepared by the invention has excellent regeneration capability, can complete regeneration by adopting less purified blast furnace gas (3-5% of the volume of the blast furnace gas which enables the desulfurizer to reach adsorption saturation) at a lower temperature (120-180 ℃), can complete regeneration by using a small amount of desulfurized industrial gas without additional preparation, avoids energy loss of high-temperature regeneration, and simultaneously reduces physical loss of the desulfurizer and the defect of needing a large amount of regenerated process gas. The sulfur adsorption capacity of the regenerated desulfurizing agent is about two thirds of that of the fresh desulfurizing agent before regeneration, but basically the same sulfur adsorption capacity can be maintained after 100 regeneration cycles. The desulfurizing agent has the advantages of simple regeneration process, low cost, basically no reduction of the regenerated 100 times of sulfur capacity, and extremely strong low-cost desulfurizing process in industry. The desulfurizing agent is suitable for desulfurizing sulfur-containing gas containing carbonyl sulfide and hydrogen sulfide, and converts the hydrogen sulfide and the carbonyl sulfide into SO 2 Then desulfurization treatment is carried out, and the regenerated gas is purified blast furnace gas after desulfurization, thereby realizing desulfurizing agent and gasAnd (5) recycling.
The invention has the following beneficial effects:
1. the carrier is prepared by taking the coal activated carbon with wide sources as the raw material, and the loaded alkaline substance can react with hydrogen sulfide, so that the chemical adsorption effect of the activated carbon is obviously improved; the active carbon is loaded with activated metal to adsorb sulfur atoms in sulfide, so that the sulfur atoms are reserved on the adsorbent, and the active carbon has high adsorption efficiency on sulfide in waste gas; the compound surfactant, the pore-forming agent and the strength enhancer are adopted, so that the mechanical strength of the carrier is enhanced while the specific surface area and the pore structure of the carrier are increased.
2. The desulfurizing agent obtained by the invention has good regeneration performance, adopts the principle of temperature swing adsorption, is adsorbed at low temperature, adopts a small amount of purified sulfur-containing industrial gas, such as blast furnace gas after desulfurization purification, to regenerate the desulfurizing agent at high temperature in situ, realizes the recycling of the desulfurizing agent and the sulfur-containing industrial gas, and has strong hydrogen sulfide adsorption capability. The method of the invention is simple, low in investment and low in operation cost.
Drawings
FIG. 1 is a graph showing the distribution of the pore diameters of the desulfurizing agent obtained in example 1;
FIG. 2 is a graph showing the sulfur capacity of the desulfurizing agent obtained in example 1 after the circulating regeneration.
Detailed Description
In order to make the objects, technical solutions and advantages of the present invention more apparent, the technical solutions of the present invention will be described in detail below. The following examples facilitate a better understanding of the present invention, but are not intended to limit the same. The experimental methods in the following examples are conventional methods unless otherwise specified.
The BET of the activated carbon used in the examples of the present invention was 317m 2 Per gram, average pore volume 0.27cm 3 And/g, average pore size 5.75nm.
Example 1
Preparing a desulfurizing agent:
(S1) taking active carbon as a carrier, taking sodium hydroxide as an impregnating solution, and adding 0.1mol/L sodium hydroxide solution into the carrier according to an isovolumetric impregnation method; soaking for 20h at 20 ℃, filtering, and drying the solid at 80 ℃ for 6h to obtain alkali-treated activated carbon;
(S2) 43.53g of Fe (NO) 3 ) 3 2.5g of compound surfactant (compound of fatty alcohol polyoxyethylene ether and sodium dodecyl benzene sulfonate according to the mass ratio of 1:1), 4g of pore-forming agent starch and 2.5g of strength enhancer SiO 2 Dispersing in 100mL of solvent methanol, and fully mixing to obtain an impregnating solution, wherein the concentration of metal Fe ions is 1.8 mol/L;
(S3) according to the isovolumetric impregnation method, 10g of the alkali-treated activated carbon obtained in the step (S1) is impregnated in 19.5g of the impregnation liquid obtained in the step (S2) under the conditions of 120 kHz ultrasonic and 600 rpm stirring at room temperature for 12 hours, the solid is dried for 6 hours at 80 ℃ after filtration, and then baked for 3 hours at 300 ℃ under the nitrogen atmosphere, so as to obtain the desulfurizing agent 1, ICP test, fe 2 O 3 The content was 9.3%.
FIG. 1 is a graph showing the distribution of the most probable pore diameter of the desulfurizing agent prepared in example 1, wherein the most probable pore diameter is about 3.9nm, and the adsorbent has smaller pore diameter and is beneficial to the dispersion of active components.
Adsorption and regeneration:
adsorption process: blast furnace gas composition: 200 mg/m 3 H 2 S,20 vol%CO 2 20 vol% CO, the rest of N 2 The mixture enters an adsorption tube from top to bottom for adsorption under normal pressure, the adsorption temperature is controlled at 60 ℃, and the adsorption airspeed is about 2000 h -1 Monitoring H in tail gas using Fu Li gas chromatograph 2 S and COS contents, to H 2 The total content of S and COS exceeds 10 mg/m 3 Adsorption saturation is described later, and adsorption is stopped.
The regeneration process comprises the following steps: introducing the gas subjected to the adsorption desulfurization purification from bottom to top for regeneration, wherein the gas consumption after the adsorption desulfurization purification is 3% of the adsorption saturation volume of the desulfurizing agent, and the regeneration airspeed is about 200h -1 And (3) the regeneration temperature is 150 ℃, the tail gas is connected with the GC, the content change of sulfide is monitored, the temperature is reduced to 60 ℃ after the regeneration is finished, and the steps are repeated for a plurality of adsorption-regeneration cycles, so that the change of sulfur capacity and the regeneration condition are obtained. FIG. 2 is a graph showing the sulfur capacity change of 100 experiments on the desulfurizing agent obtained in example 1.
Example 2
The other conditions were the same as in example 1, except that in step (S2), the metal nitrate Fe (NO 3 ) 3 Replaced by equimolar amount of Cu (NO) 3 ) 2
Example 3
The other conditions were the same as in example 1, except that in step (S2), the metal nitrate Fe (NO 3 ) 3 Replaced by equimolar amount of Zn (NO 3 ) 2
Example 4
The other conditions were the same as in example 1, except that in step (S2), the metal nitrate Fe (NO 3 ) 3 Replaced by equimolar amount of Cu (NO) 3 ) 2 、Fe(NO 3 ) 3 Mixed solution, wherein Cu: molar ratio of fe=1:1.
Example 5
The other conditions were the same as in example 1 except that in step (S2), 0.02M La (NO 3 ) 3 And 0.05M Co (NO 3 ) 2
Example 6
The other conditions were the same as in example 1 except that in step (S2), 0.01M La (NO 3 ) 3 And 0.08M Co (NO) 3 ) 2
Example 7
The other conditions were the same as in example 1 except that in step (S2), 0.07M La (NO 3 ) 3
Example 8
The other conditions were the same as in example 1 except that in step (S2), 0.07M Co (NO 3 ) 2
Example 9
The other conditions were the same as in example 1 except that in step (S2), 0.02M of Y (NO) was added to the preparation of the impregnation liquid 3 ) 3 And 0.05M Co (NO 3 ) 2
The following performance tests were conducted on the desulfurizing agents obtained in the above examples, and the results are shown in Table 1 below.
1. Mechanical strength: and referring to the abrasion resistance and compressive strength of the 3 rd part of the test method of the coal particle activated carbon for GBT 30202.3-2013 desulfurization and denitrification.
An intelligent ZQJ-II particle strength tester (manufactured by Dalian intelligent tester), national chemical catalyst detection center (national chemical catalyst detection center) was used. Randomly taking 20 composite adsorbent microspheres to test the compressive strength, and taking an average value.
Abrasion resistance = value of sample mass remaining on the sieve layer after test/value of sample mass before test x 100%
2. Sulfur capacity:
wherein:sulfur capacity, unit is mg/g;
Vthe unit is mL/min for the air inlet flow;
tthe unit is min for adsorption penetration time;
Cis H in the raw material gas 2 S concentration in mg/m 3
mThe mass of the desulfurizing agent is expressed in g.
TABLE 1 desulfurizing agent Performance test results
FIG. 2 is a graph showing the sulfur capacity of the desulfurizing agent obtained in example 1 after the circulating regeneration. It can be seen that the sulfur capacity of the regenerated desulfurizing agent can reach more than 60% of that of the fresh desulfurizing agent, and after 100 regeneration cycles, the sulfur capacity can also be basically maintained as that of the first regeneration.
As can be seen from Table 1, the intensity and abrasion rate of the desulfurizing agent prepared by the method are obviously higher than those of the desulfurizing agent prepared by the conventional method, thus greatly prolonging the service life of the desulfurizing agent and reducing the use cost of the desulfurizing agent. The inventors have also unexpectedly found that,adding small amount of La (NO) into the soaking solution 3 ) 3 And Co (NO) 3 ) 2 The regeneration capacity of the desulfurizing agent can be obviously improved, and the sulfur capacity of the regenerated desulfurizing agent is improved. Whereas equimolar La (NO) 3 ) 3 Or Co (NO) 3 ) 2 Either La is replaced by other rare earth metals or Co is replaced by other transition metals, the purpose of improving the regeneration capacity of the desulfurizing agent cannot be effectively achieved. The method shows that a certain synergistic compounding effect exists between La and Co.

Claims (10)

1. The regenerable supported desulfurizing agent is characterized by comprising the following raw materials in parts by mass: 100 parts of active carbon and 150-250 parts of impregnating solution, wherein the impregnating solution comprises metal nitrate, surfactant, pore-forming agent starch and strength enhancer nano SiO 2 The method comprises the steps of carrying out a first treatment on the surface of the The renewable load type desulfurizing agent is obtained by dipping active carbon in dipping liquid, taking out, drying and calcining under inert atmosphere; the metal nitrate is selected from Fe (NO) 3 ) 3 、Cu(NO 3 ) 2 、Mn(NO 3 ) 2 、Zn(NO 3 ) 2 At least one of them.
2. The regenerable supported desulfurization agent of claim 1, wherein said activated carbon has a specific surface area of 250-350 m 2 Per gram, pore volume of 0.25-0.3. 0.3 cm 3 /g, pore diameter 5.5-6nm; the surfactant is selected from nonionic surfactant and/or anionic surfactant, the nonionic surfactant is selected from at least one of fatty alcohol polyoxyethylene ether, nonylphenol polyoxyethylene ether, polyoxyethylene ether sorbitol fatty acid ester and laurinol polyoxyethylene ether, the anionic surfactant is selected from at least one of sodium dodecyl benzene sulfonate and sodium dodecyl sulfate, and the strength enhancer is nano SiO 2 The particle size of (2) is 200-400nm.
3. The regenerable supported desulfurization agent of claim 1, wherein the impregnating solution comprises at least one solvent selected from the group consisting of methanol, ethanol and isopropanol, wherein the molar concentration of metal nitrate is 1-2M, the mass concentration of surfactant is 20-30 g/L, the mass concentration of pore-forming agent is 40-50g/L, and the mass concentration of strength enhancer is 20-30 g/L, based on total metal.
4. The regenerable supported desulfurization agent of claim 1, wherein said impregnating solution further comprises 0.01-0.02M La (NO 3 ) 3 And 0.05-0.08M Co (NO) 3 ) 2
5. The method for producing a regenerable supported desulfurization agent as claimed in any one of claims 1 to 4, comprising the steps of:
(S1) dispersing metal nitrate, a surfactant, a pore-forming agent and a strength enhancer in an alcohol solvent, and fully mixing to obtain an impregnating solution;
and (S2) under the ultrasonic and stirring conditions, soaking the activated carbon in the soaking solution, filtering, drying to obtain a carrier loaded with the active metal compound, and roasting in an inert atmosphere to obtain the modified activated carbon desulfurizing agent.
6. The method according to claim 5, wherein in step (S1), the activated carbon is subjected to alkali treatment, specifically: adding active carbon into a solution containing sodium hydroxide/potassium carbonate/potassium hydroxide at 60-80 ℃ for alkali washing, and then drying at 60-80 ℃.
7. The method according to claim 5, wherein in the step (S2), the impregnation is carried out at 20 to 40℃for 10 to 15 hours; the roasting is carried out for 3-5 hours at 240-300 ℃.
8. The process according to claim 5, wherein in the step (S2), 0.01 to 0.02M of La (NO) is added to the impregnation solution 3 ) 3 And 0.05-0.08M Co (NO) 3 ) 2 The method comprises the steps of carrying out a first treatment on the surface of the In the impregnating solution, the molar concentration of the metal nitrate is 1-2M and the mass concentration of the surfactant is 20 percent based on the total metal30 The mass concentration of the pore-forming agent is 40-50g/L, and the concentration of the strength enhancer is 30-40 g/L.
9. A method for desulfurizing industrial gas, comprising the steps of: adsorption desulfurization of sulfur-containing industrial gas by the regenerable supported desulfurization agent of any one of claims 1-4.
10. The method of claim 9, further comprising the step of regenerating the desulfurizing agent: regenerating the desulfurizing agent with saturated adsorption at 120-180 ℃ by using sulfur-containing industrial gas after desulfurization and purification;
the sulfur-containing industrial gas contains 100-300 mg/m 3 H 2 S,15-30 vol% CO, H in the purified industrial gas 2 S and carbonyl sulfur content below 10 mg/m 3
The volume of the purified industrial gas used in the regeneration is 3-5% of the volume of the sulfur-containing industrial gas saturated by the desulfurizing agent.
CN202410060773.2A 2024-01-16 2024-01-16 Renewable load-type desulfurizing agent and preparation method thereof Active CN117563556B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202410060773.2A CN117563556B (en) 2024-01-16 2024-01-16 Renewable load-type desulfurizing agent and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202410060773.2A CN117563556B (en) 2024-01-16 2024-01-16 Renewable load-type desulfurizing agent and preparation method thereof

Publications (2)

Publication Number Publication Date
CN117563556A true CN117563556A (en) 2024-02-20
CN117563556B CN117563556B (en) 2024-04-02

Family

ID=89864798

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202410060773.2A Active CN117563556B (en) 2024-01-16 2024-01-16 Renewable load-type desulfurizing agent and preparation method thereof

Country Status (1)

Country Link
CN (1) CN117563556B (en)

Citations (25)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02107313A (en) * 1988-10-14 1990-04-19 Tokyo Gas Co Ltd Method for removing sulfur compounds and desulfurization agent used in the method
US5057473A (en) * 1990-04-12 1991-10-15 The United States Of America As Represented By The Administrator Of The National Aeronautics And Space Administration Regenerative Cu La zeolite supported desulfurizing sorbents
JPH05161845A (en) * 1991-12-12 1993-06-29 Nippon Shokubai Co Ltd Regenerating method for adsorbent
JP2008138153A (en) * 2006-11-09 2008-06-19 Idemitsu Kosan Co Ltd Desulfurization method, desulfurization apparatus, apparatus for producing reformed gas for fuel cell, and fuel cell system
US20080271602A1 (en) * 2007-05-01 2008-11-06 Auburn University Doped supported zinc oxide sorbents for regenerable desulfurization applications
WO2009113445A1 (en) * 2008-03-10 2009-09-17 独立行政法人産業技術総合研究所 Adsorbent desulfurizer for liquid phases
CN101735861A (en) * 2009-12-11 2010-06-16 太原理工大学 Zinc oxide medium and high temperature coal gas fine desulfurizer and preparation method
WO2010139104A1 (en) * 2009-05-31 2010-12-09 北京三聚环保新材料股份有限公司 Renewable and reusable desulfurizer and preparation method and regeneration method thereof
CN102357364A (en) * 2011-09-05 2012-02-22 青岛科技大学 Preparation of activated carbon-based catalyst used for selective reduction desulphurization of flue gas
CN102500323A (en) * 2011-11-02 2012-06-20 北京天灏柯润环境科技有限公司 Modified active carbon desulfurizer and preparation method thereof and treatment method of hydrogen sulfide waste gas
CN102794156A (en) * 2012-09-07 2012-11-28 中国石油大学(华东) Preparation of adsorbing-oxidizing coupling desulfurizing agent
JP2013199534A (en) * 2012-03-23 2013-10-03 Idemitsu Kosan Co Ltd Method for producing desulfurized gaseous fuel
CN104923158A (en) * 2015-06-04 2015-09-23 海南科技职业学院 Preparation method of desulfurization catalyst for oil products
CN105056882A (en) * 2015-07-20 2015-11-18 昆明理工大学 Preparation method of modified charcoal-based adsorbent for removing hydrogen sulfide
CN105289476A (en) * 2015-11-19 2016-02-03 上海化工研究院 Metal-modified 13X molecular sieve desulphurization adsorbent and its preparation method and use
US20160175806A1 (en) * 2014-12-17 2016-06-23 University Of Connecticut Adsorptive desulfurization
CN105903324A (en) * 2016-05-18 2016-08-31 天津普瑞特净化技术有限公司 Copper oxide loaded active carbon desulfurizing agent and preparation process thereof
CN106669670A (en) * 2015-11-11 2017-05-17 中国石油化工股份有限公司 Preparation method of flue gas desulfurization agent
CN107398253A (en) * 2017-08-02 2017-11-28 上海润琦化工科技有限公司 A kind of catalytic cracking fuel gas sulfur transferring assistant and preparation method thereof
CN108854434A (en) * 2017-05-15 2018-11-23 中国石油化工股份有限公司 A kind of processing method and processing device of refinery VOCs exhaust gas
CN109012016A (en) * 2018-07-25 2018-12-18 南京工业大学 Regeneration method for claus tail gas adsorption desulfurizer
CN111905521A (en) * 2020-08-18 2020-11-10 宁波中科远东催化工程技术有限公司 Coke oven gas desulfurization process and system
CN112058273A (en) * 2020-08-26 2020-12-11 中国科学院山西煤炭化学研究所 A kind of blast furnace gas desulfurization catalyst and its preparation method and application
CN113289583A (en) * 2021-07-01 2021-08-24 浙江工业大学 Active carbon desulfurizer loaded with metal oxide as well as preparation method and application thereof
CN113952931A (en) * 2021-12-01 2022-01-21 通化鑫鸿新材料有限公司 Supported desulfurizer and preparation method and application thereof

Patent Citations (25)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02107313A (en) * 1988-10-14 1990-04-19 Tokyo Gas Co Ltd Method for removing sulfur compounds and desulfurization agent used in the method
US5057473A (en) * 1990-04-12 1991-10-15 The United States Of America As Represented By The Administrator Of The National Aeronautics And Space Administration Regenerative Cu La zeolite supported desulfurizing sorbents
JPH05161845A (en) * 1991-12-12 1993-06-29 Nippon Shokubai Co Ltd Regenerating method for adsorbent
JP2008138153A (en) * 2006-11-09 2008-06-19 Idemitsu Kosan Co Ltd Desulfurization method, desulfurization apparatus, apparatus for producing reformed gas for fuel cell, and fuel cell system
US20080271602A1 (en) * 2007-05-01 2008-11-06 Auburn University Doped supported zinc oxide sorbents for regenerable desulfurization applications
WO2009113445A1 (en) * 2008-03-10 2009-09-17 独立行政法人産業技術総合研究所 Adsorbent desulfurizer for liquid phases
WO2010139104A1 (en) * 2009-05-31 2010-12-09 北京三聚环保新材料股份有限公司 Renewable and reusable desulfurizer and preparation method and regeneration method thereof
CN101735861A (en) * 2009-12-11 2010-06-16 太原理工大学 Zinc oxide medium and high temperature coal gas fine desulfurizer and preparation method
CN102357364A (en) * 2011-09-05 2012-02-22 青岛科技大学 Preparation of activated carbon-based catalyst used for selective reduction desulphurization of flue gas
CN102500323A (en) * 2011-11-02 2012-06-20 北京天灏柯润环境科技有限公司 Modified active carbon desulfurizer and preparation method thereof and treatment method of hydrogen sulfide waste gas
JP2013199534A (en) * 2012-03-23 2013-10-03 Idemitsu Kosan Co Ltd Method for producing desulfurized gaseous fuel
CN102794156A (en) * 2012-09-07 2012-11-28 中国石油大学(华东) Preparation of adsorbing-oxidizing coupling desulfurizing agent
US20160175806A1 (en) * 2014-12-17 2016-06-23 University Of Connecticut Adsorptive desulfurization
CN104923158A (en) * 2015-06-04 2015-09-23 海南科技职业学院 Preparation method of desulfurization catalyst for oil products
CN105056882A (en) * 2015-07-20 2015-11-18 昆明理工大学 Preparation method of modified charcoal-based adsorbent for removing hydrogen sulfide
CN106669670A (en) * 2015-11-11 2017-05-17 中国石油化工股份有限公司 Preparation method of flue gas desulfurization agent
CN105289476A (en) * 2015-11-19 2016-02-03 上海化工研究院 Metal-modified 13X molecular sieve desulphurization adsorbent and its preparation method and use
CN105903324A (en) * 2016-05-18 2016-08-31 天津普瑞特净化技术有限公司 Copper oxide loaded active carbon desulfurizing agent and preparation process thereof
CN108854434A (en) * 2017-05-15 2018-11-23 中国石油化工股份有限公司 A kind of processing method and processing device of refinery VOCs exhaust gas
CN107398253A (en) * 2017-08-02 2017-11-28 上海润琦化工科技有限公司 A kind of catalytic cracking fuel gas sulfur transferring assistant and preparation method thereof
CN109012016A (en) * 2018-07-25 2018-12-18 南京工业大学 Regeneration method for claus tail gas adsorption desulfurizer
CN111905521A (en) * 2020-08-18 2020-11-10 宁波中科远东催化工程技术有限公司 Coke oven gas desulfurization process and system
CN112058273A (en) * 2020-08-26 2020-12-11 中国科学院山西煤炭化学研究所 A kind of blast furnace gas desulfurization catalyst and its preparation method and application
CN113289583A (en) * 2021-07-01 2021-08-24 浙江工业大学 Active carbon desulfurizer loaded with metal oxide as well as preparation method and application thereof
CN113952931A (en) * 2021-12-01 2022-01-21 通化鑫鸿新材料有限公司 Supported desulfurizer and preparation method and application thereof

Also Published As

Publication number Publication date
CN117563556B (en) 2024-04-02

Similar Documents

Publication Publication Date Title
CN108722168B (en) Renewable dry flue gas desulfurizer as well as preparation method and application thereof
CN101804289B (en) Preparation, application and regeneration method of flue gas desulfurizing agent
CN105056882A (en) Preparation method of modified charcoal-based adsorbent for removing hydrogen sulfide
CN112708477B (en) Method for improving combustion heat value of blast furnace gas and simultaneously removing organic sulfur and inorganic sulfur
CN102580675A (en) Modified activated carbon, preparation method thereof and method for adsorbing hydrogen sulfide using modified activated carbon
CN111921363B (en) A kind of high-efficiency desulfurizer for gas dry purification and its preparation method and application
CN114345117B (en) Ferric oxide composite desulfurizer and preparation method and application thereof
CN102002402A (en) Preparation method of renewable manganese high-temperature gas desulfurizer
CN102500362A (en) Catalyst for removing H2S in coal gas by catalytic oxidation and its preparation method and application
CN112546851B (en) Activated carbon, preparation method thereof and application thereof in desulfurization
CN105772112B (en) A method of preparing synthesis vinyl chloride thereof catalyst using exhaust gas mercury
CN101804297A (en) Preparation, use and reproduction method of reproducible load type flue gas desulfurization agent
CN114471143B (en) Defect alumina modified wide-temperature desulfurizer and preparation method and application thereof
CN117563556B (en) Renewable load-type desulfurizing agent and preparation method thereof
CN101406794A (en) Method for preparing exhaust gas mercury-removing reagent from modification of waste desulfurizing agent
CN118649538A (en) A desulfurizing agent and its preparation method and application
CN103418233A (en) Preparation method of high-efficiency porous iron oxide desulfurizing agent
CN112675806B (en) Adsorbent for removing carbon monoxide in gas, preparation method and application
CN110833830B (en) A method for preparing mercury removal catalyst by utilizing natural ore and waste residue
CN114832805A (en) Hydrolysis catalyst for removing carbonyl sulfide in blast furnace gas, preparation method and application thereof
CN108014835A (en) Oxidation at room temperature hydrogen sulfide alkaline mesoporous Pd/carbon catalyst and preparation method and application
CN102029141A (en) Modified attapulgite flue gas desulfurization agent and preparation and application thereof
Yan et al. Synergistic effect of Cu and Ce bimetallic over MCM-41 zeolite for enhancing the catalytic hydrolysis performance of COS
CN116371392B (en) Integrated desulfurization and decyanation catalyst and preparation method and application thereof
CN115178234B (en) Composite hierarchical pore catalytic-adsorption material and preparation method thereof

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
GR01 Patent grant
GR01 Patent grant