Nothing Special   »   [go: up one dir, main page]

CN115055186B - High-embedding CuO/CeO for removing CO in flue gas 2 Multi-layer catalyst and preparation method thereof - Google Patents

High-embedding CuO/CeO for removing CO in flue gas 2 Multi-layer catalyst and preparation method thereof Download PDF

Info

Publication number
CN115055186B
CN115055186B CN202210870999.XA CN202210870999A CN115055186B CN 115055186 B CN115055186 B CN 115055186B CN 202210870999 A CN202210870999 A CN 202210870999A CN 115055186 B CN115055186 B CN 115055186B
Authority
CN
China
Prior art keywords
catalyst
base material
cuo
ceo
flue gas
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
CN202210870999.XA
Other languages
Chinese (zh)
Other versions
CN115055186A (en
Inventor
张欣华
李小明
沈正华
邢相栋
郑兆颖
王宇星
马雨溦
谢昊峰
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.)
Xian University of Architecture and Technology
Original Assignee
Xian University of Architecture and 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 Xian University of Architecture and Technology filed Critical Xian University of Architecture and Technology
Priority to CN202210870999.XA priority Critical patent/CN115055186B/en
Publication of CN115055186A publication Critical patent/CN115055186A/en
Application granted granted Critical
Publication of CN115055186B publication Critical patent/CN115055186B/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
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/83Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with rare earths or actinides
    • 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
    • B01D53/86Catalytic processes
    • B01D53/864Removing carbon monoxide or hydrocarbons
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Environmental & Geological Engineering (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Catalysts (AREA)

Abstract

The invention discloses a high chimeric CuO/CeO for removing CO in flue gas 2 The preparation method of the multi-layer catalyst comprises the following steps: grinding low-metamorphic coal, copper acetate, ammonium cerium nitrate and a binder as raw materials, mixing, adding water for molding after fully and uniformly mixing, drying, carrying out grading degradation and carrier carbonization on the dried raw materials at low temperature, and activating a carbonized carrier material by high-temperature steam to obtain the carbonized Cu and Ce multi-compound catalyst base material. And washing and drying the obtained carbonaceous base material, and then impregnating and loading Cu under a high-temperature hydrothermal condition to directly realize baking-free decomposition of the carbonaceous base material, thereby obtaining the multi-level catalyst. The active components of the prepared catalyst are firmly embedded and are not easy to fall off; cu species are distributed in a multi-valence level, active components are highly dispersed, and effective active sites are more, so that the catalyst can be used for producing high-performance CuO/CeO for removing CO from high-performance industrial flue gas 2 A catalyst.

Description

High-embedding CuO/CeO for removing CO in flue gas 2 Multi-layer catalyst and preparation method thereof
Technical Field
The invention belongs to the technical field of catalysts, and in particular relates to a high-embedding CuO/CeO for removing CO in flue gas 2 A multi-layer catalyst and a preparation method thereof.
Background
CO is one of the main pollutants in the atmosphere and has a wide source. Industrial kiln, metallurgical industry flue gas and motor vehicle exhaust all contain a large amount of CO. CO can be combined with hemoglobin in human body to weaken oxygen transmission capacity, damage central nervous system, and increase CO content in air by more than 30mg/m 3 Can have toxic and harmful effects on human body. Introducing catalyst inHigh-efficiency conversion of CO into non-toxic CO at low temperature 2 Is currently recognized as the most promising CO elimination technology. CuO/CeO supported by carbonaceous material 2 The catalyst is considered as the most promising industrial flue gas CO removal catalyst due to higher catalytic activation and low cost, but Cu and Ce active components loaded on the surface of the carrier are easy to be washed out by gas in the application process, so that the catalytic activity is reduced. Therefore, a CuO/CeO is designed in which the active component is not easy to fall off 2 The preparation method of the catalyst has practical significance for eliminating CO in industrial flue gas.
The preparation method of the sintered flue gas carbonaceous adsorbing material (patent application number: CN 201710807924.6) applied by the university of Western-style building technology takes iron-containing materials, low-metamorphic coal, cerium-containing components, binders and pore formers as raw materials, and the sintered flue gas carbonaceous adsorbing material is obtained through high-temperature pyrolysis and steam activation. The preparation method has certain requirements on the catalytic active components, and has low application degree in the field of copper-cerium catalyst preparation. Copper cerium is easy to reduce in the process of preparing the copper cerium catalyst, and the copper cerium catalyst cannot be prepared based on the method. A catalyst for removing nitrogen oxide and carbon monoxide at low temperature and its preparation method (patent application number: CN201310338656. X) applied by Hunan university are to dip activated carbon in copper salt solution after washing with acid, washing with water and drying, then drying and roasting to obtain the catalyst finished product, and the preparation method has great environmental pollution.
Disclosure of Invention
In order to solve the problems in the prior art, the invention aims to provide a high chimeric CuO/CeO for removing CO in flue gas 2 The invention relates to a multi-layer catalyst and a preparation method thereof, which comprises the active component CuO/CeO 2 Uniformly embedded on the surface of the carbonaceous base material, and is not easy to fall off; and the active metal copper is distributed in a multi-valence level, the dispersibility of the active component is high, the effective activity is more, and the catalytic performance is excellent.
The aim of the invention is realized by the following technical scheme:
high-embedding CuO/CeO for removing CO in flue gas 2 A method for preparing a multi-layered catalyst comprising the steps of:
uniformly mixing low-metamorphic coal, copper salt, cerium salt and a binder, and forming and drying to obtain a formed body;
classifying the molded body for decomposition and carbonizing the carrier to obtain a carbonized carrier material;
activating the carbonaceous carrier material by utilizing steam to obtain a carbonaceous base material;
washing and drying the carbonaceous base material, impregnating and loading Cu under a hydrothermal condition, and drying the carbonaceous base material loaded with Cu to obtain the high chimeric CuO/CeO for removing CO in the flue gas 2 A multi-stage catalyst.
Preferably, the low-deterioration coal, copper salt, cerium salt and binder are respectively ground into powder, uniformly mixed, then mixed with water for molding, and then dried to obtain the molded body.
Preferably, the low-metamorphic coal content in the mixture of the low-metamorphic coal, the copper salt, the cerium salt and the binder is 70.5-80.5% in percentage by mass; the content of the binder is 2.0-10.0%;
the content of copper salt and cerium salt is 10.5% -20.5%, wherein the molar ratio of copper to cerium is 1: (3.5-5).
Preferably, the copper salt is copper acetate, and the cerium salt is ceric ammonium nitrate.
Preferably, the process of classifying the molded body into a decomposition and a carbonization of the carrier comprises: heating the molded body to 250-300 ℃, then preserving heat until the copper acetate decomposition rate is more than 90%, and then heating to 500-600 ℃ to decompose ceric ammonium nitrate and carbonize, wherein the temperature is preserved until the volatile component of the carbonize carrier material is 5-15%.
Preferably, the process for activating a carbonaceous carrier material with steam to obtain a carbonaceous base material comprises: heating the carbonaceous carrier material to 1000-1100 ℃ at a heating rate of 10-12 ℃/min in an inert atmosphere, preserving heat for 5-10 min, then cooling to 700-750 ℃ and then introducing steam for activation until the specific surface area of the carbonaceous material is 500-600 m 2 /g。
Preferably, when the dried carbonaceous base material is impregnated with Cu under hydrothermal conditions, the solution used is a copper acetate solution, and the hydrothermal temperature of impregnation is 220-260 ℃.
Preferably, the dry carbonaceous base material is impregnated with a load of Cu in an amount of 1.2 to 3.0 times the Cu content of the carbonaceous base material under hydrothermal conditions.
Preferably, the binder is sodium carboxymethyl cellulose or soluble starch.
The invention also provides a high chimeric CuO/CeO for removing CO in the flue gas 2 Multi-layer catalyst, the high chimeric CuO/CeO for removing CO in flue gas 2 The multi-layered catalyst is prepared by the preparation method of the invention as described above.
The invention has the following beneficial effects:
the invention removes high chimeric CuO/CeO of CO in the flue gas 2 The preparation method of the multi-layer catalyst can be used for preparing the active component CuO/CeO 2 Uniformly embedded on the surface of the carbonaceous base material, and is not easy to fall off; and the active metal copper is distributed in a multi-valence level, the dispersibility of the active component is high, the effective activity is more, and the catalytic performance is excellent.
Further, in the process of classifying decomposition of the molded body and carbonization of the carrier, the molded body is heated to 250-300 ℃ firstly, then the molded body is insulated until the copper acetate decomposition rate is more than 90%, and then the molded body is heated to 500-600 ℃ again to decompose and carbonize ceric ammonium nitrate, so that the mechanical strength of the carbonized carrier is ensured to be less influenced by copper acetate and ceric ammonium nitrate, and meanwhile, cu and Ce active components are firmly embedded on the surface of the carbonized carrier and are not easy to fall off.
Further, in the process of activating the carbonaceous carrier material by using water vapor, the carbonaceous carrier is firstly and rapidly heated to 1000-1100 ℃ in an inert atmosphere (at a heating rate of 10-12 ℃/min), and is kept for 5-10 min, so that the closed holes on the surface of the carbonaceous carrier are opened, and then the temperature is reduced to 700-750 ℃ for activating the carbonaceous carrier material, and then the carbonaceous carrier material is activated by introducing water vapor, so that the mass base material with large specific surface area, which is favorable for exposing more active sites, is obtained.
Further, when the dried carbonaceous base material is impregnated with Cu under hydrothermal conditions, the Cu is loaded with water at 220-260 ℃ by using a copper acetate solutionAnd (3) impregnating and loading Cu under a thermal condition, wherein Cu is highly dispersed and uniformly adhered on the surface of the carbonaceous base material. The active components of the obtained catalyst are tightly embedded on the surface of the carbonized base material, copper species are distributed in a multivalent level, and CuO/CeO is improved while the falling of the active components is prevented 2 Catalytic activity.
Detailed Description
The invention will be further illustrated with reference to the following examples.
The invention removes high chimeric CuO/CeO of CO in the flue gas 2 A method for preparing a multi-layered catalyst comprising the steps of:
grinding low-metamorphic coal, copper acetate, ammonium cerium nitrate and binder into powder respectively, mixing, adding water into the raw materials after fully and uniformly mixing, stirring uniformly, pressing, drying, heating the dried raw materials to 250-300 ℃, preserving heat until the copper acetate decomposition rate is more than 90%, heating to 500-600 ℃ and preserving heat to perform ammonium cerium nitrate decomposition and carbonization processes, and preserving heat until the volatile components of the carbonized carrier material are 5-15%, thus obtaining the carbonized carrier. Rapidly heating the carbonaceous carrier to 1000-1100 ℃ at a heating rate of 10-12 ℃/min in an inert atmosphere, preserving heat for 5-10 min, cooling to 700-750 ℃ and then introducing steam for activation until the specific surface area of the carbonaceous carrier is 500-600 m 2 Between/g, a carbonaceous Cu, ce multi-element compound catalyst base material is obtained. Wherein, the raw materials for preparing the carbonaceous base material comprise the following components in percentage by mass: 70.5 to 80.5 percent of low metamorphic coal; copper acetate and ammonium cerium nitrate are 10.5% -20.5% in total, the binder is 2.0% -10.0%, and the Cu/Ce molar ratio is 1:3.5 to 5.
Washing and drying the obtained carbonized base material, and impregnating and loading Cu with a copper acetate solution under the high-temperature hydrothermal condition of 220-260 ℃ until Cu content in the prepared carbonized base material is 1.2-3.0 times, thereby obtaining the high chimeric CuO/CeO for removing the CO in the flue gas 2 A multi-stage catalyst.
The active components of the catalyst prepared by the method are firmly embedded and are not easy to fall off; cu species are distributed in a multi-valence level, active components are highly dispersed, and effective active sites are more, so that the Cu-based composite material can be used for producing high-performance workersHigh-performance CuO/CeO for removing CO from industrial flue gas 2 A catalyst.
The invention will be further illustrated with reference to the following examples.
In the following examples of the invention, the simulated reaction gas composition containing CO used in the experiments was: 1% CO, 20% O 2 、79%N 2 The gas flow rate was 100ml/min.
The calculation formula of the CO removal efficiency is as follows: CO removal rate= (content of CO in feed gas-content of CO in tail gas)/content of CO in feed gas x 100%.
Example 1:
in the embodiment, the raw materials are calculated according to mass fraction: the low metamorphic coal content is 70.5%, the binder content is 9.0%, the sum of copper salt and cerium salt is 20.5%, wherein the molar ratio of copper to cerium is 1:5, the content of copper acetate and ammonium cerium nitrate is 1.3% and 19.2% respectively. (wherein, the low metamorphic coal is brown coal, the industrial analysis is that ash content is 6.7%, volatile matter is 37.4%, fixed carbon is 55.9%, and the binder is sodium carboxymethyl cellulose.) the low metamorphic coal, copper acetate, ceric ammonium nitrate and the binder are respectively ground into powder and then mixed, the fully and uniformly mixed raw materials are added with water and uniformly stirred, are dried after being pressed and molded, the dried raw materials are heated to 250 ℃ and kept for 50min, the decomposition rate of copper acetate is detected to be 93.5%, then heated to 500 ℃ and kept for 80min, the decomposition rate of ceric ammonium nitrate is detected to be 93.7%, and the temperature is kept until the volatile component of the carbonized carrier material is 5%, thus obtaining the carbonized carrier material. Carbonaceous support material in N 2 Heating to 1000 ℃ at a heating rate of 10-12 ℃/min in the atmosphere, preserving heat for 5min, then cooling to 700 ℃, introducing steam, activating for 50min, and detecting that the specific surface area of the base material of the C-Cu and Ce multi-compound catalyst is 536m 2 And/g. Washing and drying the obtained carbonized base material, impregnating and loading Cu with a copper acetate solution under 220 ℃ hydrothermal condition, wherein the Cu content of the hydrothermal impregnation and loading is 1.2 times of Cu in the carbonized base material, and obtaining the high chimeric CuO/CeO for removing the CO in the flue gas 2 A multi-stage catalyst.
High embedding CuO/CeO for removing CO in the obtained flue gas 2 Performance testing of the multi-layered catalyst: 300mg of catalyst is filled in 8mm quartz for reactionIn the tube, controlling the reaction temperature to be 180 ℃, introducing simulated reaction gas containing CO, and detecting the concentration of CO in the inlet and outlet gas; the high chimeric CuO/CeO for removing the CO in the flue gas prepared by the method 2 The multi-level catalyst has the CO removal rate of 95.6% in the simulation reaction, the CO conversion rate is only reduced by 1.3% after the catalytic reaction is carried out for 128h, and the catalytic performance is superior to that of CuO/CeO prepared by the conventional method 2 A catalyst.
Example 2
In the embodiment, the raw materials are calculated according to mass fraction: the low metamorphic coal content is 79.5%, the binder content is 10.0%, the sum of copper salt and cerium salt is 10.5%, wherein the molar ratio of copper to cerium is 1:4, the content of copper acetate and ammonium cerium nitrate is 0.8% and 9.7% respectively. (wherein, the low-metamorphic coal is brown coal, the industrial analysis is that ash content is 6.7 percent, volatile matter is 37.4 percent, fixed carbon is 55.9 percent, and the binder is soluble starch.) respectively grinding the low-metamorphic coal, copper acetate, ceric ammonium nitrate and the binder into powder, mixing, adding water into the fully and uniformly mixed raw materials, uniformly stirring, pressing, drying, heating the dried raw materials to 275 ℃, preserving heat for 60 minutes, and detecting that the decomposition rate of copper acetate is 95.5 percent; and then heating to 550 ℃ and preserving heat for 100min, wherein the decomposition rate of ceric ammonium nitrate is detected to be 96.1%, and preserving heat until the volatile components of the carbonized carrier material are 11%, thus obtaining the carbonized carrier material. Carbonaceous support material in N 2 Heating to 1050 ℃ at a heating rate of 10-12 ℃/min in the atmosphere, preserving heat for 7min, then cooling to 725 ℃, introducing steam, activating for 60min, and detecting that the specific surface area of the carbonaceous Cu, ce multi-compound catalyst base material is 578m 2 And/g. Washing and drying the obtained carbonized base material, impregnating and loading Cu with a copper acetate solution under a hydrothermal condition at 240 ℃, wherein the Cu content of the hydrothermal impregnation and loading is 2.2 times of that of Cu in the carbonized base material, and obtaining the high chimeric CuO/CeO for removing the CO in the flue gas 2 A multi-stage catalyst.
High embedding CuO/CeO for removing CO in the obtained flue gas 2 Performance testing of the multi-layered catalyst: filling 300mg of catalyst into an 8mm quartz reaction tube, controlling the reaction temperature to be 180 ℃, introducing simulated reaction gas containing CO, and detecting the concentration of CO in inlet and outlet gases; the method for removing CO in the flue gasHigh mosaic CuO/CeO 2 The multi-level catalyst has the CO removal rate of 97.2% in the simulation reaction, the CO conversion rate is reduced by 0.7% after the catalytic reaction is carried out for 128h, and the catalytic performance is superior to that of CuO/CeO prepared by the conventional method 2 A catalyst.
Example 3
In the embodiment, the raw materials are calculated according to mass fraction: the low metamorphic coal content is 80.5%, the binder content is 2.0%, the sum of copper salt and cerium salt is 17.5%, wherein the molar ratio of copper to cerium is 1:3.5, the content of copper acetate and ammonium cerium nitrate is 1.6% and 15.9% respectively. (wherein, the low metamorphic coal is brown coal, the industrial analysis is that ash content is 6.7%, volatile matter is 37.4%, fixed carbon is 55.9%, and the binder is sodium carboxymethyl cellulose.) the low metamorphic coal, copper acetate, ceric ammonium nitrate and the binder are respectively ground into powder and then mixed, the fully and uniformly mixed raw materials are added with water and uniformly stirred, are dried after being pressed and molded, the dried raw materials are heated to 300 ℃ and kept for 70min, the decomposition rate of copper acetate is detected to be 96.2%, then heated to 600 ℃ and kept for 120min, the decomposition rate of ceric ammonium nitrate is detected to be 98.6%, and the temperature is kept until the volatile component of the carbonized carrier material is 15%, thus obtaining the carbonized carrier material. Carbonaceous support material in N 2 Heating to 1100 ℃ at a heating rate of 10-12 ℃/min in the atmosphere, preserving heat for 10min, cooling to 750 ℃, introducing steam, activating for 70min, and detecting that the specific surface area of the carbonaceous Cu, ce multi-compound catalyst base material is 592m 2 And/g. Washing and drying the obtained carbonized base material, impregnating and loading Cu with a copper acetate solution under a hydrothermal condition at 260 ℃, wherein the Cu content of the hydrothermal impregnation and loading is 3 times of that of Cu in the carbonized base material, and obtaining the high chimeric CuO/CeO for removing CO in flue gas 2 A multi-stage catalyst.
High embedding CuO/CeO for removing CO in the obtained flue gas 2 Performance testing of the multi-layered catalyst: filling 300mg of catalyst into an 8mm quartz reaction tube, controlling the reaction temperature to be 180 ℃, introducing simulated reaction gas containing CO, and detecting the concentration of CO in inlet and outlet gases; the high chimeric CuO/CeO for removing the CO in the flue gas prepared by the method 2 The multi-level catalyst has a CO removal rate of 94.5% in the simulated reaction, and the CO conversion rate is only reduced after 128h of the catalytic reaction is carried out1.6 percent, the catalytic performance is better than that of CuO/CeO prepared by the conventional method 2 A catalyst.
In conclusion, the invention prepares the high chimeric CuO/CeO for removing the CO in the flue gas from the perspective of CO catalytic oxidation 2 A multi-stage catalyst. Mixing, molding, drying, grading degradation, carbonization and activation of low-metamorphic coal, copper acetate, ammonium cerium nitrate and a binder to obtain a carbonized base material; the obtained carbonaceous base material is subjected to high-temperature hydrothermal impregnation to obtain high-embedding CuO/CeO 2 The multi-level catalyst has low cost, simple production process and easy implementation. The prepared catalyst has large specific surface area, high mechanical strength, firm embedding of active components, difficult falling off, high dispersibility, copper oxide in multi-valence level distribution, high catalytic activity and good stability, and is favorable for producing high-performance CuO/CeO for removing CO in industrial flue gas 2 A catalyst.

Claims (2)

1. High-embedding CuO/CeO for removing CO in flue gas 2 The preparation method of the multi-level catalyst is characterized by comprising the following steps:
uniformly mixing low-metamorphic coal, copper salt, cerium salt and a binder, and forming and drying to obtain a formed body;
classifying the molded body for decomposition and carbonizing the carrier to obtain a carbonized carrier material;
activating the carbonaceous carrier material by utilizing steam to obtain a carbonaceous base material;
washing and drying the carbonaceous base material, impregnating and loading Cu under a hydrothermal condition, and drying the carbonaceous base material loaded with Cu to obtain the high chimeric CuO/CeO for removing CO in the flue gas 2 A multi-level catalyst;
wherein, the specific process for obtaining the molded body comprises the following steps of uniformly mixing low-metamorphic coal, copper salt, cerium salt and a binder, molding and drying: grinding low-deterioration coal, copper salt, cerium salt and binder into powder respectively, uniformly mixing, mixing with water for molding, and drying to obtain the molded body;
when the dried carbonaceous base material is impregnated with Cu under hydrothermal condition, the used solution is copper acetate solution, and the impregnating hydrothermal temperature is 220-260 ℃;
the low-metamorphic coal content in the mixture of the low-metamorphic coal, the copper salt, the cerium salt and the binder is 70.5-80.5% in percentage by mass; the content of the binder is 2.0-10.0%; the content of copper salt and cerium salt is 10.5% -20.5%, wherein the molar ratio of copper to cerium is 1: (3.5-5);
the copper salt adopts copper acetate, and the cerium salt adopts ceric ammonium nitrate;
the process of classifying and decomposing the molded body and carbonizing the carrier comprises the following steps: heating the molded body to 250-300 ℃, then preserving heat until the copper acetate decomposition rate is more than 90%, and then heating to 500-600 ℃ to decompose ceric ammonium nitrate and carbonize the molded body until the volatile components of the carbonize carrier material are 5-15%;
the process for activating a carbonaceous carrier material with steam to obtain a carbonaceous base material comprises: heating the carbonaceous carrier material to 1000-1100 ℃ at a heating rate of 10-12 ℃/min in an inert atmosphere, preserving heat for 5-10 min, cooling to 700-750 ℃ and then introducing steam for activation until the specific surface area of the carbonaceous carrier material is 500-600 m 2 /g;
The Cu content of the impregnation load of the dried carbonized base material under the hydrothermal condition is 1.2-3.0 times of the Cu content in the carbonized base material;
the binder adopts sodium carboxymethyl cellulose or soluble starch.
2. High-embedding CuO/CeO for removing CO in flue gas 2 The multi-level catalyst is characterized in that the high chimeric CuO/CeO for removing CO in the flue gas 2 The multi-layer catalyst is prepared by removing high chimeric CuO/CeO of CO in flue gas according to claim 1 2 The preparation method of the multi-layer catalyst is provided.
CN202210870999.XA 2022-07-22 2022-07-22 High-embedding CuO/CeO for removing CO in flue gas 2 Multi-layer catalyst and preparation method thereof Active CN115055186B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210870999.XA CN115055186B (en) 2022-07-22 2022-07-22 High-embedding CuO/CeO for removing CO in flue gas 2 Multi-layer catalyst and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210870999.XA CN115055186B (en) 2022-07-22 2022-07-22 High-embedding CuO/CeO for removing CO in flue gas 2 Multi-layer catalyst and preparation method thereof

Publications (2)

Publication Number Publication Date
CN115055186A CN115055186A (en) 2022-09-16
CN115055186B true CN115055186B (en) 2024-03-26

Family

ID=83205746

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210870999.XA Active CN115055186B (en) 2022-07-22 2022-07-22 High-embedding CuO/CeO for removing CO in flue gas 2 Multi-layer catalyst and preparation method thereof

Country Status (1)

Country Link
CN (1) CN115055186B (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104307534A (en) * 2014-10-31 2015-01-28 天津市联合环保工程设计有限公司 Preparation method for MnO2-CeO2-CoO/AC ternary supported catalyst for treatment of phenolic wastewater
JP2015016394A (en) * 2013-07-09 2015-01-29 株式会社豊田中央研究所 N2o decomposition catalyst and method for decomposing n2o-containing gas using the same
CN107442069A (en) * 2017-09-08 2017-12-08 西安建筑科技大学 A kind of preparation method for sintering denitrating flue gas carbonaceous sorbing material
CN108855108A (en) * 2018-06-26 2018-11-23 天津工业大学 Starch-based bio activated carbon loaded nano catalysis material and preparation method thereof
CN113828311A (en) * 2021-10-14 2021-12-24 西安建筑科技大学 High-sulfur-resistance catalyst for removing CO and preparation method thereof
CN113996309A (en) * 2021-11-23 2022-02-01 国能龙源催化剂江苏有限公司 Preparation method of high-strength SCR catalyst for CO collaborative removal

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10322407B2 (en) * 2015-12-17 2019-06-18 Council Of Scientific & Industrial Research Catalyst for carbon monoxide oxidation and process for the preparation thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015016394A (en) * 2013-07-09 2015-01-29 株式会社豊田中央研究所 N2o decomposition catalyst and method for decomposing n2o-containing gas using the same
CN104307534A (en) * 2014-10-31 2015-01-28 天津市联合环保工程设计有限公司 Preparation method for MnO2-CeO2-CoO/AC ternary supported catalyst for treatment of phenolic wastewater
CN107442069A (en) * 2017-09-08 2017-12-08 西安建筑科技大学 A kind of preparation method for sintering denitrating flue gas carbonaceous sorbing material
CN108855108A (en) * 2018-06-26 2018-11-23 天津工业大学 Starch-based bio activated carbon loaded nano catalysis material and preparation method thereof
CN113828311A (en) * 2021-10-14 2021-12-24 西安建筑科技大学 High-sulfur-resistance catalyst for removing CO and preparation method thereof
CN113996309A (en) * 2021-11-23 2022-02-01 国能龙源催化剂江苏有限公司 Preparation method of high-strength SCR catalyst for CO collaborative removal

Also Published As

Publication number Publication date
CN115055186A (en) 2022-09-16

Similar Documents

Publication Publication Date Title
CN109225179B (en) Regeneration and waste gas treatment process for adsorption saturated chlorinated hydrocarbon-containing organic compound waste activated carbon
CN109794246B (en) Integrated honeycomb Ni @ C/C catalyst and preparation method and application thereof
CN107442069B (en) Preparation method of sintered flue gas denitration carbonaceous adsorption material
CN110711584B (en) Semicoke-loaded coke oil steam reforming catalyst and preparation method and application thereof
CN111229209B (en) Lotus leaf source charcoal-loaded manganese oxide low-temperature SCR (selective catalytic reduction) flue gas denitration catalyst and preparation method and application thereof
CN108485692B (en) High-quality harmless utilization method of hyper-enriched plants
CN111099591B (en) Surface-modified high-activity low-temperature denitration active coke and preparation method thereof
CN114887654B (en) Molecular sieve based nano carbon coated supported advanced oxidation catalyst and preparation method thereof
CN111569864A (en) Activated carbon composite material for catalytic purification of formaldehyde and preparation method thereof
CN113231009A (en) Ammonia adsorbent and preparation method thereof
CN114160104A (en) Kiln flue gas CO2Trapping and utilizing coupling material and application thereof
CN115055186B (en) High-embedding CuO/CeO for removing CO in flue gas 2 Multi-layer catalyst and preparation method thereof
CN113198523A (en) Preparation method of efficient flue gas desulfurization and denitrification catalyst
CN114671432B (en) Coal-based high-performance CO 2 Preparation method of activated carbon material for adsorption
CN108435175B (en) Modified carbon-based material for catalyzing oxidation-reduction reaction, and preparation method and application thereof
CN113828311B (en) High sulfur-resistant catalyst for removing CO and preparation method thereof
CN111495410B (en) Honeycomb ceramic-porous carbon monolithic catalyst, honeycomb ceramic-porous carbon monolithic adsorbent and preparation method and application thereof
CN114433073A (en) Manganese-based catalyst and preparation method and application thereof
CN113426448A (en) Preparation method and application of novel biochar-based tar cracking catalyst
CN113332954B (en) Sintered flue gas denitration adsorbent and preparation method and application thereof
CN110013828B (en) Preparation method of modified activated carbon material for flue gas demercuration
CN111889115B (en) Deoxygenation catalyst and preparation method and application thereof
CN115193434B (en) Method and system for cooperatively removing carbon-based catalyst, VOCs and nitrogen oxides
CN115672306B (en) Modified activated carbon for desulfurization and denitrification and preparation process thereof
CN114602422B (en) Li (lithium ion battery) 4 SiO 4 Base double-function 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