CN111889113B - Coal gas layer treatment catalyst and preparation method thereof - Google Patents

Coal gas layer treatment catalyst and preparation method thereof Download PDF

Info

Publication number
CN111889113B
CN111889113B CN201910365819.0A CN201910365819A CN111889113B CN 111889113 B CN111889113 B CN 111889113B CN 201910365819 A CN201910365819 A CN 201910365819A CN 111889113 B CN111889113 B CN 111889113B
Authority
CN
China
Prior art keywords
zinc
sulfate
catalyst
ceryl
loaded alumina
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.)
Active
Application number
CN201910365819.0A
Other languages
Chinese (zh)
Other versions
CN111889113A (en
Inventor
李�杰
张信伟
王海洋
韩照明
刘全杰
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.)
Sinopec Dalian Petrochemical Research Institute Co ltd
China Petroleum and Chemical Corp
Original Assignee
China Petroleum and Chemical Corp
Sinopec Dalian Research Institute of Petroleum and Petrochemicals
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 China Petroleum and Chemical Corp, Sinopec Dalian Research Institute of Petroleum and Petrochemicals filed Critical China Petroleum and Chemical Corp
Priority to CN201910365819.0A priority Critical patent/CN111889113B/en
Publication of CN111889113A publication Critical patent/CN111889113A/en
Application granted granted Critical
Publication of CN111889113B publication Critical patent/CN111889113B/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
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/02Sulfur, selenium or tellurium; Compounds thereof
    • B01J27/053Sulfates
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L3/00Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
    • C10L3/06Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
    • C10L3/10Working-up natural gas or synthetic natural gas
    • C10L3/101Removal of contaminants
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/02Combustion or pyrolysis
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/52Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts

Abstract

The invention discloses a coal bed gas treatment catalyst, which contains zinc-loaded alumina and ceryl sulfate, wherein the zinc-loaded alumina is wrapped around the ceryl sulfate, the weight ratio of the zinc-loaded alumina to the ceryl sulfate is 8:1-2:1, and the content of zinc in oxide is 5-25 wt% based on the weight of the zinc-loaded alumina; the preparation method of the catalyst comprises the following steps: firstly, uniformly mixing a zinc-containing compound and aluminum hydroxide slurry, then spraying the mixed solution around cerous sulfate, drying and roasting to obtain the coal bed gas deoxidation catalyst. The catalyst is used for deoxidizing the coal bed gas and has the advantages of high activity, low reaction temperature, simple preparation method, low cost and the like.

Description

Coal gas layer treatment catalyst and preparation method thereof
Technical Field
The invention relates to a coal gas layer treatment catalyst and a preparation method thereof, in particular to a low-temperature high-activity coal gas layer deoxidation catalyst and a preparation method thereof.
Background
China is a large coal producing country, coal bed gas with different concentrations can be produced due to coal production every year, and developing effective coal bed gas utilization technology and reducing direct emission of methane are a component part for building an energy-saving and environment-friendly sustainable development mode and building a low-carbon economic system in China. The method has the advantages that the low-grade energy source coal bed gas is practically and reasonably developed by combining energy conservation and emission reduction and improvement of the requirement on the environment, the low-grade energy source coal bed gas is well converted into available resources, the application range and the scale of the coal bed gas are expanded, the utilization efficiency of the coal bed gas is improved, the dual meanings of energy conservation and environmental protection are realized, the national planning on energy policies is met, the control of the international environmental protection organization on the greenhouse effect is met, the strong support of China on the development and the use of the low-grade energy source is better met, and the domestic rapid development of the coal bed gas industry is promoted.
The deoxidation method by using coke combustion (ZL 02113627.0, 200610021720.1) is characterized in that oxygen in methane-rich gas reacts with coke under the high-temperature condition, and part of methane reacts with oxygen to achieve the aim of deoxidation. The advantage is that about 70% of the oxygen reacts with coke and 30% of the oxygen reacts with methane, so that methane losses are smaller. But the disadvantage is that the precious coke resource is consumed, and the coke consumption cost accounts for about 50 percent of the whole operation cost. In addition, the coke deoxidation method has high labor intensity during coke feeding and slag discharging, large environmental dust and difficulty in realizing self-control operation and large-scale production, and the coke contains sulfides in various forms, so that the sulfur content in the gas after oxygen removal is increased.
The technology for researching the supported noble metal catalyst at home and abroad is mature. For example, rare earth cerium component with oxygen storage and release functions is added into a catalyst system for the large-scale ligation of Chinese academy of sciences to prepare the novel supported palladium noble metal catalyst, and the oxygen concentration in produced gas is within 0.1 percent and the oxygen conversion rate is higher than 96 percent after the deoxidation treatment of coal bed gas with the methane concentration of 39.15 percent and the oxygen concentration of 12.6 percent. Since the noble metal catalyst is expensive and has limited resources, the range of application is limited. And the non-noble metal oxide catalyst has low cost and easy availability, so the catalyst is greatly concerned. However, the non-noble metal is limited by activity, and the reaction needs to be carried out at a higher temperature, so that the energy consumption is higher.
Disclosure of Invention
Aiming at the defects of the prior art, the invention provides a coal bed gas deoxidation catalyst and a preparation method thereof. The catalyst has the advantages of high activity, low reaction temperature, simple preparation method, low cost and the like.
The catalyst contains zinc-loaded alumina and ceryl sulfate, wherein the zinc-loaded alumina is wrapped around the ceryl sulfate, the weight ratio of the zinc-loaded alumina to the ceryl sulfate is 8:1-2:1, preferably 6:1-3:1, and the content of zinc in terms of oxides is 5-25 wt%, preferably 10-20 wt%, based on the weight of the zinc-loaded alumina.
In the catalyst, the thickness of the zinc-loaded alumina wrapped around the ceryl sulfate is 15 μm to 130 μm, preferably 20 μm to 100 μm.
In the catalyst, the cerous sulfate can be spherical or strip-shaped, and is preferably spherical; the cerous acyl sulfate equivalent diameter is 1mm to 8mm, preferably 3mm to 5 mm.
A preparation method of a coal bed methane deoxidation catalyst comprises the following steps: firstly, uniformly mixing a zinc-containing compound and aluminum hydroxide slurry, then spraying the mixed solution around cerous sulfate, drying and roasting to obtain the coal bed gas deoxidation catalyst.
In the above method, the ceryl sulfate may be commercially available or prepared according to the prior art. A specific preparation method of ceryl sulfate, such as the preparation of ceryl sulfate by roasting at 300-500 ℃ for 1-10 h. The aluminum hydroxide slurry is generally pseudo-boehmite slurry. The pseudoboehmite is also called alumina monohydrate or pseudoboehmite, and the molecular formula is AlOOH & nH 2 O (n = 0.08-0.62). The method for producing the aluminum hydroxide slurry is not particularly limited, and various methods commonly used in the art may be used, and examples thereof include aluminum alkoxide hydrolysis, acid or alkali methods of aluminum salt or aluminate, and NaA1O 2 Introducing CO into the solution 2 The carbonization method of (3). The specific operation method is well known to those skilled in the art and will not be described herein.
In the method, the zinc-containing compound can be one or more of zinc nitrate, zinc sulfate, zinc bromide and zinc chloride.
In the method, the drying time is 1-5h, preferably 2-4h, the drying temperature is 90-150 ℃, preferably 100-; the roasting time is 3-8h, preferably 4-6h, and the temperature is 300-700 ℃, preferably 400-500 ℃.
In the above method, the mixed solution contains at least one of 2, 5-dihydroxy-terephthalic acid and 1,3, 5-benzene tricarboxylic acid, and the mass content of at least one of 2, 5-dihydroxy-terephthalic acid and 1,3, 5-benzene tricarboxylic acid in the mixed solution is 0.5 to 10%, preferably 2 to 7%. The 2, 5-dihydroxy-terephthalic acid or 1,3, 5-benzene tricarboxylic acid added into the mixed solution has stronger coordination effect with zinc ions, can improve the dispersion degree of zinc on alumina, and further improves the activity of the catalyst.
In the method, before spraying and soaking the mixed solution, the ceryl sulfate is preferably treated by adopting a water vapor nitrogen mixed gas with the water vapor volume content of 0.5-5 percent, and more preferably 1-4 percent, the treatment temperature is 100-. The ceric acyl sulfate treated by the water vapor can improve the hydrophilicity of the surface of the ceric acyl sulfate, is beneficial to spray soaking of mixed liquor, improves the interaction force between the zinc-loaded aluminum oxide and the ceric acyl sulfate, avoids the zinc-loaded aluminum oxide from falling off from the periphery of the ceric acyl sulfate, and improves the stability of the catalyst.
Research results show that the mechanism of catalytic combustion of the coal bed gas is that methane is firstly dissociated into CH on the surface of the catalytic combustion catalyst x Species of which x<4, then carrying out oxidation reaction with the adsorbed oxygen or lattice oxygen. This application will catalyze the burning catalyst around ceric acid sulfate, ceric acid sulfate compares the catalytic burning catalyst and has stronger activated methane's effect at low temperature, and the methane substance after the activation diffuses to and reacts in the catalytic burning catalyst coating, burns fast more easily, has showing the activity that has improved the catalyst.
Detailed Description
The function and effect of a coal bed methane deoxidation catalyst and a preparation method thereof are further illustrated with reference to the following examples, but the following examples are not to be construed as limiting the invention. In this application,% is volume concentration unless otherwise specified.
The catalyst of the invention can adopt means such as transmission electron microscope observation, electron diffraction analysis, element composition analysis and the like to confirm the wrapping structure and determine the composition. The determination of the catalyst coating structure specifically adopts the following method: the sample was sufficiently ground in an agate mortar using a high-resolution transmission electron microscope (JEM 2100 LaB6, JEOL Ltd., Japan) with a resolution of 0.23 nm equipped with an X-ray energy dispersive spectrometer (EDX) from EDAX, and then ultrasonically dispersed in absolute ethanol for 20 min. And (3) dripping 2-3 drops of the suspension liquid on a micro-grid carbon film supported by a zinc net, and carrying out TEM observation, electron diffraction analysis and element composition analysis on the sample after the sample is dried. The ceric acid sulfate referred to in examples and comparative examples was prepared by calcining cerium sulfate at 350 ℃ for 3 hours.
Example 1
Preparing aluminum hydroxide slurry by adopting an aluminum isopropoxide hydrolysis method: mixing water and aluminum isopropoxide according to a molar ratio of 120:1, controlling the hydrolysis temperature at 80-85 ℃, hydrolyzing the aluminum isopropoxide for 1.5h, and then aging at 90-95 ℃ for 18h to obtain aluminum hydroxide slurry with the solid content of 21.3 wt%.
Spray soaking process: firstly, uniformly mixing zinc nitrate and aluminum hydroxide slurry, then spraying 500g of ceryl sulfate (a product sold in the market and with the equivalent diameter of 4 mm) in the mixed solution, drying and roasting to prepare the coal bed methane deoxidation catalyst, wherein the drying time is 4 hours, and the drying temperature is 100 ℃; the roasting time is 6h, and the temperature is 400 ℃.
The catalyst properties were as follows: the zinc-loaded alumina is wrapped around ceryl sulfate, the weight ratio of the zinc-loaded alumina to the ceryl sulfate is 4:1, and the content of zinc in oxide is 15wt% based on the weight of the zinc-loaded alumina. The thickness of the zinc-loaded alumina wrapped around the ceryl sulfate was 60 μm.
The catalyst performance is evaluated by taking coal bed methane deoxidation as a probe reaction, and the feed gas comprises the following components: CH (CH) 4 20 vol%,O 2 3 vol%, the balance being N 2 . The reaction temperature is 420 ℃, and the volume space velocity is 15000 h -1 After the reaction is stable, detecting O in tail gas at the outlet of the reactor by on-line chromatography 2 The concentration is 0.47%, and O in tail gas at the outlet of the reactor after 300 h operation 2 The concentration was 0.6%.
Example 2
Preparing aluminum hydroxide slurry by adopting an aluminum isopropoxide hydrolysis method: mixing water and aluminum isopropoxide according to a molar ratio of 120:1, controlling the hydrolysis temperature at 80-85 ℃, hydrolyzing the aluminum isopropoxide for 1.5h, and then aging at 90-95 ℃ for 18h to obtain aluminum hydroxide slurry with the solid content of 21.3 wt%.
And (3) spray-dipping process: firstly, uniformly mixing zinc nitrate and aluminum hydroxide slurry, then spraying 500g of ceryl sulfate (a product sold in the market and with the equivalent diameter of 5 mm) in the mixed solution, and drying and roasting to prepare the coal bed methane deoxidation catalyst, wherein the drying time is 4 hours, and the drying temperature is 100 ℃; the roasting time is 6h, and the temperature is 400 ℃.
The catalyst properties were as follows: the zinc-loaded alumina is wrapped around ceryl sulfate, the weight ratio of the zinc-loaded alumina to the ceryl sulfate is 3:1, and the content of zinc in oxide is 20wt% based on the weight of the zinc-loaded alumina.
The catalyst performance is evaluated by taking coal bed methane deoxidation as a probe reaction, and the feed gas comprises the following components: CH (CH) 4 20 vol%,O 2 3 vol%, the balance being N 2 . The reaction temperature is 420 ℃, and the volume space velocity is 15000 h -1 After the reaction is stable, detecting O in tail gas at the outlet of the reactor by on-line chromatography 2 The concentration was 0.51%.
Example 3
Preparing aluminum hydroxide slurry by adopting a carbonization method of introducing carbon dioxide gas into sodium metaaluminate solution: will contain 30wt% CO 2 CO of 2 /N 2 Introducing the mixed gas into a sodium metaaluminate solution, carrying out gelling reaction at 30 ℃, controlling the pH of the reaction end point to be 10.5-11.0, aging after the reaction is finished, and washing the mixture by deionized water at 60 ℃ until the pH of the filtrate is 6.5 to obtain aluminum hydroxide slurry with the solid content of 31.2 wt%.
And (3) spray-dipping process: firstly, uniformly mixing zinc nitrate and aluminum hydroxide slurry, then spraying 500g of ceryl sulfate (a product sold in the market and with the equivalent diameter of 3 mm) in the mixed solution, and drying and roasting to prepare the coal bed methane deoxidation catalyst, wherein the drying time is 4 hours, and the drying temperature is 100 ℃; the roasting time is 6h, and the temperature is 400 ℃.
The catalyst properties were as follows: the zinc-loaded alumina is wrapped around ceryl sulfate, the weight ratio of the zinc-loaded alumina to the ceryl sulfate is 6:1, and the content of zinc in oxide is 10wt% based on the weight of the zinc-loaded alumina.
The catalyst performance is evaluated by taking coal bed methane deoxidation as a probe reaction, and the feed gas comprises the following components: CH (CH) 4 20 vol%,O 2 3 vol%, the balance being N 2 . The reaction temperature is 420 ℃, and the volume space velocity is 15000 h -1 After the reaction is stable, detecting O in tail gas at the outlet of the reactor by on-line chromatography 2 The concentration was 0.62%.
Example 4
The difference from example 1 is that the mixed solution contains 6% by mass of 2, 5-dihydroxy-terephthalic acid.
The catalyst performance is evaluated by taking coal bed methane deoxidation as a probe reaction, and the feed gas comprises the following components: CH (CH) 4 20 vol%,O 2 3 vol%, the balance being N 2 . The reaction temperature is 420 ℃, and the volume space velocity is 15000 h -1 After the reaction is stable, detecting O in tail gas at the outlet of the reactor by on-line chromatography 2 The concentration was 0.12%.
Example 5
The difference from example 1 is that the mixed solution contains 3% by mass of 1,3, 5-benzenetricarboxylic acid.
The catalyst performance is evaluated by taking coal bed methane deoxidation as a probe reaction, and the feed gas comprises the following components: CH (CH) 4 20 vol%,O 2 3 vol%, the balance being N 2 . The reaction temperature is 420 ℃, and the volume space velocity is 15000 h -1 After the reaction is stable, detecting O in tail gas at the outlet of the reactor by on-line chromatography 2 The concentration was 0.05%.
Example 6
The difference from the example 1 is that before spraying and soaking the mixed solution, the ceryl sulfate is treated by adopting a water vapor nitrogen mixed gas with the water vapor volume content of 1 percent, the treatment temperature is 180 ℃, and the treatment time is 3 min.
The catalyst performance is evaluated by taking coal bed methane deoxidation as a probe reaction, and the raw material gas comprises the following components: CH (CH) 4 20 vol%,O 2 3 vol%, the balance being N 2 . The reaction temperature is 420 ℃, and the volume space velocity is 15000 h -1 After the reaction is stable, detecting O in tail gas at the outlet of the reactor by on-line chromatography 2 The concentration is 0.43 percent, and O in tail gas at the outlet of the reactor after 300 hours of operation 2 The concentration was 0.47%.
Example 7
Compared with the example 1, the difference is that before spraying and soaking the mixed solution, the ceric sulfate is treated by adopting the water vapor nitrogen mixed gas with the water vapor volume content of 4 percent, the treatment temperature is 120 ℃, and the treatment time is 10 min.
The catalyst performance is evaluated by taking coal bed methane deoxidation as a probe reaction, and the feed gas comprises the following components: CH (CH) 4 20 vol%,O 2 3 vol%, the balance being N 2 . The reaction temperature is 420 ℃, and the volume space velocity is 15000 h -1 After the reaction is stable, detecting O in tail gas at the outlet of the reactor by on-line chromatography 2 The concentration is 0.48 percent, and O in tail gas at the outlet of the reactor after 300 hours of operation 2 The concentration was 0.53%.

Claims (11)

1. A coal bed gas treatment catalyst, which is characterized in that: the catalyst contains zinc-loaded alumina and ceric sulfate, the zinc-loaded alumina is wrapped around the ceric sulfate, the weight ratio of the zinc-loaded alumina to the ceric sulfate is 8:1-2:1, and the content of zinc in terms of oxide is 5-25 wt% based on the weight of the zinc-loaded alumina; the preparation method of the cerous sulfate comprises the following steps: the cerium sulfate is prepared by roasting at the temperature of 300-500 ℃ for 1-10.
2. The catalyst of claim 1, wherein: the catalyst contains zinc-loaded alumina and ceric sulfate, the zinc-loaded alumina is wrapped around the ceric sulfate, the weight ratio of the zinc-loaded alumina to the ceric sulfate is 6:1-3:1, and the content of zinc in terms of oxides is 10-20 wt% based on the weight of the zinc-loaded alumina.
3. The catalyst of claim 1, wherein: the thickness of the zinc-loaded aluminum oxide wrapped around the ceryl sulfate is 15-130 μm, the ceryl sulfate is spherical or strip-shaped, and the equivalent diameter of the ceryl sulfate is 1-8 mm.
4. The catalyst of claim 3, wherein: the thickness of the zinc-loaded aluminum oxide wrapped around the ceryl sulfate is 20-100 μm, the ceryl sulfate is spherical, and the equivalent diameter of the ceryl sulfate is 3-5 mm.
5. A process for preparing a catalyst as claimed in any one of claims 1 to 4, characterized in that: the method comprises the following steps: firstly, uniformly mixing a zinc-containing compound and aluminum hydroxide slurry, then spraying the mixed solution around cerous sulfate, drying and roasting to obtain the coal bed gas deoxidation catalyst.
6. The method of claim 5, wherein: the aluminum hydroxide slurry is pseudo-boehmite slurry.
7. The method of claim 5, wherein: the zinc-containing compound is one or more of zinc nitrate, zinc sulfate, zinc bromide and zinc chloride.
8. The method of claim 5, wherein: the drying time is 1-5h, and the drying temperature is 90-150 ℃; the roasting time is 3-8h, and the temperature is 300-700 ℃.
9. The method of claim 8, wherein: the drying time is 2-4h, and the drying temperature is 100-130 ℃; the roasting time is 4-6h, and the temperature is 400-500 ℃.
10. The method of claim 5, wherein: the mixed solution contains at least one of 2, 5-dihydroxy-terephthalic acid or 1,3, 5-benzene tricarboxylic acid, and the mass content of at least one of 2, 5-dihydroxy-terephthalic acid or 1,3, 5-benzene tricarboxylic acid in the mixed solution is 0.5-10%.
11. The method of claim 5, wherein: before spraying and soaking the mixed liquid, the ceric sulfate is treated by adopting water vapor nitrogen mixed gas with the water vapor volume content of 0.5-5%, the treatment temperature is 100-.
CN201910365819.0A 2019-05-05 2019-05-05 Coal gas layer treatment catalyst and preparation method thereof Active CN111889113B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910365819.0A CN111889113B (en) 2019-05-05 2019-05-05 Coal gas layer treatment catalyst and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910365819.0A CN111889113B (en) 2019-05-05 2019-05-05 Coal gas layer treatment catalyst and preparation method thereof

Publications (2)

Publication Number Publication Date
CN111889113A CN111889113A (en) 2020-11-06
CN111889113B true CN111889113B (en) 2022-08-12

Family

ID=73169160

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910365819.0A Active CN111889113B (en) 2019-05-05 2019-05-05 Coal gas layer treatment catalyst and preparation method thereof

Country Status (1)

Country Link
CN (1) CN111889113B (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103920507A (en) * 2013-01-15 2014-07-16 南京工业大学 Catalyst for oxidation of hydrogen chloride to prepare chlorine and application thereof
CN108067262A (en) * 2016-11-11 2018-05-25 中国石油化工股份有限公司抚顺石油化工研究院 A kind of preparation method of highly selective methane zirconyl oxyhalides catalyst
CN108067263A (en) * 2016-11-11 2018-05-25 中国石油化工股份有限公司抚顺石油化工研究院 A kind of catalyst with core-shell structure and its preparation method and application
CN108067259A (en) * 2016-11-11 2018-05-25 中国石油化工股份有限公司抚顺石油化工研究院 A kind of preparation method of high activity methane zirconyl oxyhalides catalyst
CN108067265A (en) * 2016-11-11 2018-05-25 中国石油化工股份有限公司抚顺石油化工研究院 A kind of preparation method of methane reforming catalyst

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103920507A (en) * 2013-01-15 2014-07-16 南京工业大学 Catalyst for oxidation of hydrogen chloride to prepare chlorine and application thereof
CN108067262A (en) * 2016-11-11 2018-05-25 中国石油化工股份有限公司抚顺石油化工研究院 A kind of preparation method of highly selective methane zirconyl oxyhalides catalyst
CN108067263A (en) * 2016-11-11 2018-05-25 中国石油化工股份有限公司抚顺石油化工研究院 A kind of catalyst with core-shell structure and its preparation method and application
CN108067259A (en) * 2016-11-11 2018-05-25 中国石油化工股份有限公司抚顺石油化工研究院 A kind of preparation method of high activity methane zirconyl oxyhalides catalyst
CN108067265A (en) * 2016-11-11 2018-05-25 中国石油化工股份有限公司抚顺石油化工研究院 A kind of preparation method of methane reforming catalyst

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
含铈硫酸氧盐储氧材料的制备及储/释氧性能研究;王男等;《化学反应工程与工艺》;20110630;262-268页 *
甲烷制卤代甲烷研究进展;邵芸等;《工业催化》;20131130;第21卷(第11期);第6页右栏第2段和第7页左栏最后1段 *

Also Published As

Publication number Publication date
CN111889113A (en) 2020-11-06

Similar Documents

Publication Publication Date Title
CN110075831B (en) Iridium supported catalyst for catalytic combustion of low-concentration methane and preparation method thereof
CN108187665B (en) Denitration catalyst and preparation method thereof
CN113634257A (en) Application of bifunctional catalyst to CO in flue gas2Integration of capture and methanation
CN107983354B (en) Preparation method of alkali poisoning resistant copper-based spinel low-temperature denitration catalyst
Chen et al. Structure-activity strategy comparison of (NH4) 2CO3 and NH4OH precipitants on MnOx catalyst for low-temperature NO abatement
CN111889113B (en) Coal gas layer treatment catalyst and preparation method thereof
CN114345355A (en) Supported iron-based multi-component catalyst and preparation method thereof
CN109772441B (en) Catalyst with shell-core structure and preparation method and application thereof
CN101618323B (en) Structural catalyst for catalyzing and reducing nitrogen oxide and preparation method thereof
CN104109092B (en) The method of carbon monoxide vapor-phase synthesis barkite
CN106475128B (en) A kind of preparation method of industrial waste gas purifying catalyst
CN109772322B (en) Coal bed gas deoxidation catalyst and preparation method thereof
CN111889114B (en) Catalyst with shell-core structure and preparation method and application thereof
CN105642289A (en) Preparation method of catalyst for complete methanation of syngas
CN109772440B (en) Coal bed gas catalytic combustion catalyst and preparation method thereof
CN111889116B (en) Catalytic combustion catalyst and preparation method thereof
CN110898835A (en) Catalyst for efficiently treating ammonia nitrogen wastewater and preparation method thereof
CN105642290A (en) Preparation method of catalyst for reforming of methane and carbon dioxide to prepare syngas
CN111889106B (en) Compound and preparation method and application thereof
CN111250078B (en) MnOx @ Eu-CeOx low-temperature SCR flue gas denitration catalyst and preparation method and application thereof
CN109772371B (en) Compound and preparation method and application thereof
CN109772354B (en) Deoxygenation catalyst and preparation method and application thereof
CN107376915B (en) Carbon dioxide methanation catalyst and preparation method thereof
CN111889115B (en) Deoxygenation catalyst and preparation method and application thereof
CN108067264B (en) Methane conversion catalyst and preparation method and application 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
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20231027

Address after: 100728 No. 22 North Main Street, Chaoyang District, Beijing, Chaoyangmen

Patentee after: CHINA PETROLEUM & CHEMICAL Corp.

Patentee after: Sinopec (Dalian) Petrochemical Research Institute Co.,Ltd.

Address before: 100728 No. 22 North Main Street, Chaoyang District, Beijing, Chaoyangmen

Patentee before: CHINA PETROLEUM & CHEMICAL Corp.

Patentee before: DALIAN RESEARCH INSTITUTE OF PETROLEUM AND PETROCHEMICALS, SINOPEC Corp.