CN115400756B - Non-noble metal catalyst for removing high-concentration laughing gas at low temperature and preparation method and application thereof - Google Patents

Non-noble metal catalyst for removing high-concentration laughing gas at low temperature and preparation method and application thereof Download PDF

Info

Publication number
CN115400756B
CN115400756B CN202211100533.8A CN202211100533A CN115400756B CN 115400756 B CN115400756 B CN 115400756B CN 202211100533 A CN202211100533 A CN 202211100533A CN 115400756 B CN115400756 B CN 115400756B
Authority
CN
China
Prior art keywords
concentration
laughing gas
noble metal
low temperature
metal catalyst
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
CN202211100533.8A
Other languages
Chinese (zh)
Other versions
CN115400756A (en
Inventor
张建强
李燕燕
杨许召
吴诗德
蔡立芳
韩莉锋
李亚坤
张盈盈
韩敬莉
平丹
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.)
Zhengzhou University of Light Industry
Original Assignee
Zhengzhou University of Light Industry
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 Zhengzhou University of Light Industry filed Critical Zhengzhou University of Light Industry
Priority to CN202211100533.8A priority Critical patent/CN115400756B/en
Publication of CN115400756A publication Critical patent/CN115400756A/en
Application granted granted Critical
Publication of CN115400756B publication Critical patent/CN115400756B/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
    • B01J23/74Iron group metals
    • B01J23/745Iron
    • 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
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • B01D53/8628Processes characterised by a specific catalyst
    • B01J35/40
    • B01J35/613
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/0009Use of binding agents; Moulding; Pressing; Powdering; Granulating; Addition of materials ameliorating the mechanical properties of the product catalyst
    • B01J37/0027Powdering
    • B01J37/0036Grinding
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/10Heat treatment in the presence of water, e.g. steam
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/202Hydrogen
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/204Carbon monoxide

Abstract

The invention discloses a non-noble metal catalyst for removing high-concentration laughing gas at low temperature, a preparation method and application thereof, belonging to the field of environmental protection and being capable of relieving the problems of greenhouse effect and the like. The copper-based catalyst is a main catalyst which is copper oxide and a cocatalyst which is iron oxide. The catalyst is prepared by adopting the processes of solution heat synthesis, planetary ball milling and the like, does not need auxiliary agents such as a carrier, a binder and the like, and has simple preparation process, low cost and good economic benefit. The non-noble metal copper-based catalyst provided by the invention has good performance in removing high-concentration laughing gas at low temperature, and the removal rate can reach more than 90% when the volume fraction of laughing gas is 10% at 300 ℃. The process relieves the problem of laughing gas pollution under the condition of low cost, has good economic benefit and social benefit, and meets the requirement of green low-carbon development.

Description

Non-noble metal catalyst for removing high-concentration laughing gas at low temperature and preparation method and application thereof
Technical Field
The invention relates to a non-noble metal catalyst for removing high-concentration laughing gas at low temperature, which is applied to occasions where laughing gas pollution is generated in the chemical production process. The technology belongs to the field of air pollution control, the field of clean production of nylon chemical industry and the field of industrial catalytic reaction engineering.
Background
Laughing gas (N) 2 O) is one of six greenhouse gases, the greenhouse effect being about 310 times that of carbon dioxide, and has been listed in the "united nations climate change framework convention", which, due to its extremely stable nature, can remain in the atmosphere for a long period of time up to about 150 years. The main hazard of laughing gas is to destroy the ozone layer, form ozone layer cavities, and finally cause greenhouse effect. Laughing gas is known to be the most damaging substance to the ozone layer at present, and its Global Warming Potential (GWP) is about CO 2 300 times of (2). The relevant literature indicates that N 2 O is growing at a rate of 0.2% per year, i.e. it is slowly eroding our ozone layer and causing damage. In the atmosphereN of (2) 2 O mostly comes from tail gas discharged from industrial production, and the largest discharge amount is generated in the industrial production process of adipic acid and nylon-66; other sources are automobile exhaust, biomass combustion, waste water, municipal solid waste and the like. N (N) 2 O is extremely stable in chemical nature, and how it is decomposed or treated to reduce N 2 The impact of O on atmospheric pollution is a research hotspot in the chemical field in recent years.
In recent years, a great deal of extreme weather appears in the world, the risk of methane overflow under ice is gradually increased due to the fact that the arctic temperature rise is caused in the world, once a great deal of greenhouse gas methane is released into the atmosphere, the greenhouse effect is increased, and catastrophic vicious circle is formed, so that the greenhouse effect is relieved, and the reduction of laughing gas emission is a key problem for safety of people and living of living organisms in the world.
The chemical industry is closely related to our life, is an indispensable important component in the economic development of China, and promotes the economic development of China. At present, the environmental pollution problem caused by chemical production is very serious, and along with the national advocated sustainable development strategy, the green chemical technology is gradually developed. Considering the factors such as cost and environmental pollution comprehensively, nitric acid is widely used as an oxidant in chemical production, and has the main defects of by-product of a large amount of nitrogen oxides, wherein nitric oxide and nitrogen dioxide are easily oxidized and recovered, and laughing gas has high thermodynamic stability and is difficult to treat. Adipic acid is a main intermediate for producing nylon-66 in nylon industry chains, and the adipic acid is generally produced by adopting a nitric acid oxidation process, which is relatively mature, and difficult to produce laughing gas in production.
In view of this, the present invention has been made. The invention provides a catalytic oxidation method for removing laughing gas generated in the nitric acid industry by adopting non-noble metals. The process has the advantages of low cost and good treatment effect, solves the problem of laughing gas emission, and relieves global warming effect.
Disclosure of Invention
Aiming at the problem that laughing gas is difficult to treat in the prior nitric acid oxidation process, the invention provides a non-noble metal copper-based catalyst for removing high-concentration laughing gas at a low temperature, and solves the problem that the laughing gas treatment process is harsh, high in energy consumption, high in cost and the like and is difficult to treat.
In order to solve the technical problems, the invention adopts the following technical scheme:
the non-noble metal catalyst for removing high-concentration laughing gas at low temperature is a copper-based catalyst, the copper-based catalyst uses copper oxide as a main catalyst, uses iron oxide as a cocatalyst, does not need auxiliary agents such as a carrier, a binder and the like, wherein the mass fraction of the copper oxide is 20-90 w.t%, the rest is the iron oxide, and the specific surface area of the non-noble metal catalyst is 10-50m 2 And/g, the particle size is 0.1-20 microns, and the particle size is mainly concentrated in small particles with the large size of about 10 microns and about 100 nanometers.
The preparation method of the non-noble metal catalyst for removing high-concentration laughing gas at low temperature comprises the following steps:
(1) Adding copper salt and ferric salt into a mixed solvent consisting of a high-viscosity solvent and a low-viscosity solvent, and stirring until the copper salt and the ferric salt are completely dissolved to form a double-solvent metal salt solution;
(2) Adding a water-soluble dispersing agent and an oil-soluble dispersing agent into the double-solvent metal salt solution obtained in the step (1), and stirring to obtain a mixed solution;
(3) Adding sodium hydroxide into the mixed solution obtained in the step (2), and vigorously stirring to obtain a mixed suspension;
(4) Transferring the mixed suspension obtained in the step (3) to a dynamic crystallization kettle for crystallization;
(5) Centrifugally separating the suspension crystallized in the step (4) to obtain a solid substance, washing with deionized water for three times and washing with ethanol for three times to obtain a washed solid;
(6) Putting the solid cleaned in the step (5) into a planetary ball milling tank for ball milling, and washing a sample obtained after ball milling by adopting ethanol;
(7) And (3) placing the ball-milled and washed sample in the step (6) in a blast drying oven for drying, and placing the dried sample in a muffle furnace for calcining to obtain the non-noble metal catalyst for removing high-concentration laughing gas at low temperature.
Further, the high-viscosity solvent in the step (1) refers to a solvent with a viscosity of more than 1.5 mPa.s at 20 ℃ and comprises n-propanol, n-butanol, isobutanol, glycerol and dimethyl sulfoxide, and the low-viscosity solvent comprises water, ethanol, methanol and n-hexane, and the volume ratio of the high-viscosity solvent to the low-viscosity solvent is (1-8): 1.
Further, the copper salt in the step (1) adopts one or more of inorganic copper salt and/or organic copper salt, and the iron salt adopts one or more of inorganic iron salt and/or organic iron salt; the mol ratio of the copper salt to the ferric salt is (0.7-2.5): 1.
Further, the water-soluble dispersing agent in the step (2) refers to a dispersing agent with better solubility in water, and comprises PVP, gelatin and polyethylene glycol; the oil-soluble dispersant refers to a dispersant with better oil solubility, such as turpentine (natural extract), oleylamine, octadecenoic acid and the like; the mass ratio of the oil-soluble dispersing agent to the water-soluble dispersing agent is (0.1-1): 1; in the mixed solution, the total concentration of the two dispersing agents is 0.01-0.1g/ml; the stirring speed is 100-150rpm, and the stirring time is 1-1.5 hours.
Further, the molar number of sodium hydroxide added in the step (2) is 1 to 1.5 times of the sum of the molar numbers of the ferric salt and the cupric salt in the raw material; the rotation speed of the vigorous stirring is 200-400rpm, and the vigorous stirring time is 2-6 hours.
Further, the crystallization temperature in the step (3) is 160-240 ℃ and the crystallization time is 12-24 hours.
Further, the ball milling in the planetary ball milling tank in the step (6) means that the sample is subjected to physical impact after hydrothermal treatment, including physical treatment processes such as ball milling, sand milling, grinding and the like; the rotating speed of ball milling in the planetary ball milling tank in the step (6) is 150rpm, the ball milling agent adopts linolenic acid, and the ball milling time is 1-2 hours.
Further, the drying temperature in the step (7) is 80 ℃, the drying time is 12 hours, the calcining temperature is 360 ℃, and the calcining time is 6 hours.
The invention relates to an application of a non-noble metal catalyst for removing high-concentration laughing gas at low temperature in removing high-concentration laughing gas at low temperature, which comprises the following steps: reducing substances including carbon monoxide, hydrogen and the like are added in the process of removing the high-concentration laughing gas; the low temperature is 250-350 ℃, and the volume concentration of the high concentration laughing gas is 1-50%, preferably 10%.
The invention adopts the reaction of the reducing gas and nitrous oxide (laughing gas) in the nitric acid oxidation section aiming at the generated nitrogen oxide waste gas to realize the goal of removing the laughing gas at low temperature, and the process solves the problem of treating the waste gas laughing gas under mild conditions with lower cost, thereby relieving the global warming effect.
The invention has the beneficial effects that: 1. the catalyst prepared by the invention has good catalytic performance, can promote the rapid reaction of reducing gas hydrogen or carbon monoxide and laughing gas, and solves the problem of waste gas treatment. 2. The catalyst used in the invention is a non-noble metal catalyst, copper and iron with low cost are used as catalyst active elements, the cost is low, the treatment condition is mild, the energy consumption is low, and the development concept of green chemical industry is met. Therefore, the invention has good application prospect, has the advantages of low cost, mild treatment condition and the like, and accords with the development trend of green chemical industry.
Drawings
FIG. 1 is a scanning electron microscope image of a non-noble metal copper-based catalyst according to example 1 of the present invention.
Detailed Description
The present invention will be described in further detail with reference to the following examples in order to make the objects, technical solutions and advantages of the present invention more apparent. The specific embodiments described herein are to be considered in an illustrative sense only and are not intended to limit the invention.
Example 1
The preparation method of the non-noble metal catalyst in the embodiment is as follows:
(1) Firstly, weighing 4.0g of ferric trichloride hexahydrate and 2.4g of copper nitrate, dispersing the ferric trichloride hexahydrate and the copper nitrate into 50ml of glycerin and 10ml of deionized water solution, placing the suspension into an ultrasonic dispersing instrument for ultrasonic dispersion for 15 min for stirring until the suspension is uniformly mixed to form a double-solvent metal salt solution;
(2) Then adding 2.0g of water-soluble dispersant polyvinylpyrrolidone (K30), 0.5g of oil-soluble dispersant turpentine, and stirring for 1 hour at the rotating speed of 100rpm uniformly; then adding 2.8g of sodium carbonate into the mixture, and stirring vigorously for 3 hours at a mechanical stirring speed of 300rpm to obtain a suspension;
(3) Transferring the stirred suspension to a dynamic crystallization kettle, and maintaining the temperature at 180 ℃ for 12 hours;
(4) Centrifugally separating the crystallized suspension at 9000rpm to obtain a solid substance, washing with deionized water for three times and washing with ethanol for three times to obtain a washed solid;
(5) Placing the cleaned solid into a planetary ball milling tank for ball milling, wherein the rotating speed is 150rpm, the ball milling agent is linolenic acid, and the sample is washed with ethanol for three times after ball milling for 1 hour;
(6) And (3) drying the ball-milled and washed sample in a blast drying oven at 80 ℃ for 12 hours, and calcining in a muffle furnace for 6 hours at 360 ℃ to obtain the copper-based catalyst. The catalyst was named: CF-1.
Laughing gas removal reaction example
N was carried out in a fixed bed reactor 2 The reaction performance evaluation of O removal comprises the following specific steps:
catalyst evaluation was carried out in a fixed bed stainless steel tube reactor, a layer of quartz sand having 20 to 80 mesh particles was first packed in the reactor of the catalyst evaluation apparatus, and then 0.1g of catalyst CF-1 was charged into the reactor. After the air tightness is detected, the catalyst is pretreated to have catalytic activity. The nitrogen is used for activation, the gas flow is 40ml/min, the activation temperature is 300 ℃, the pressure is 0.1MPa, and the time is 5 hours, so that the catalyst can be fully activated. After activation, the activity of the catalyst was evaluated under the conditions of a reaction temperature of 300℃and a reaction pressure of 0.1MPa, a laughing gas flow rate of 20ml/min, a carbon monoxide flow rate of 20ml/min and an argon flow rate of 160 ml/min. After the reaction is in a stable state, experimental data are collected, after the stable reaction is carried out for 4 hours, sampling is carried out, and the sample enters a gas chromatograph through a three-way valve to carry out product analysis.
Reaction results: the conversion rate of laughing gas is 89.7%.
Example 2
As in example 1, 2.7g of ferric trichloride hexahydrate and 3.6g of copper nitrate were weighed and dispersed in 50ml of ethylene glycol to obtain catalyst CF-2, and 0.1g of catalyst CF-2 was charged into the reactor in the laughing gas removal reaction example. Otherwise, the same as in example 1 was conducted.
Example 3
As in example 1, 4.0g of ferric trichloride hexahydrate and 2.4g of copper nitrate were weighed, dispersed in 50ml of ethylene glycol and 10ml of deionized water solution, and 0g of water type dispersant polyvinylpyrrolidone was added to obtain catalyst CF-3, and 0.1g of catalyst CF-3 was charged into the reactor in the laughing gas removal reaction example. Otherwise, the same as in example 1 was conducted.
Example 4
As in example 1, 4.0g of ferric trichloride hexahydrate and 2.4g of copper nitrate were weighed, and a catalyst CF-4 was obtained without planetary ball milling treatment, and 0.1g of the catalyst CF-4 was charged into a reactor in the laughing gas removal reaction example. Otherwise, the same as in example 1 was conducted.
Example 5
As in example 1, the flow rate of reducing gas hydrogen gas was 20ml/min in the example of laughing gas removal reaction, and the other steps were as in example 1.
Example 6
The catalyst loading was 0g as in example 1, and the same as in example 1.
The evaluation results of the examples are shown in Table 1.
Table 1 results of catalyst evaluation
As can be seen from Table 1, the addition of catalyst CF-1 promotes the conversion of laughing gas in example 1 as compared to example 6. In the absence of a catalyst, laughing gas is hardly reduced.
Also, example 2 demonstrates that the catalyst activity is reduced when the catalyst is prepared using a single solvent, but also has a certain catalytic activity, compared with example 1, illustrating the effect of the di-dispersant on catalyst performance.
Example 3 the elimination of the aqueous dispersant compared to example 1 also resulted in a decrease in catalyst activity, a decrease in dispersant, and possibly agglomeration or non-uniformity of dispersion, thereby decreasing catalyst activity.
Example 4 the elimination of the ball milling process also resulted in a decrease in catalyst activity compared to example 1, and the ball milling process destroyed the dispersant on the catalyst surface, leaving more active sites exposed, facilitating the catalytic reaction.
Example 5 shows that the different reducing gases all exhibit good catalytic activity over the CF-1 catalyst and are universal compared to example 1.
The above examples show that the copper-based catalyst has the performance of catalyzing the reaction of reducing gas and laughing gas, and provides a new process and thought for treating laughing gas in the nitric acid oxidation industry chain. Solves the problem of treating waste gas laughing gas, reduces the emission of greenhouse gases at lower cost, and accords with the development trend of green chemical industry.
The foregoing has shown and described the basic principles and main features of the present invention and the advantages of the present invention. It will be understood by those skilled in the art that the present invention is not limited to the embodiments described above, and that the above embodiments and descriptions are merely illustrative of the principles of the present invention, and various changes and modifications may be made without departing from the spirit and scope of the invention, which is defined in the appended claims. The scope of the invention is defined by the appended claims and equivalents thereof.

Claims (9)

1. The preparation method of the non-noble metal catalyst for removing high-concentration laughing gas at low temperature is characterized by comprising the following steps:
(1) Adding copper salt and ferric salt into a mixed solvent consisting of a high-viscosity solvent and a low-viscosity solvent, and stirring until the copper salt and the ferric salt are completely dissolved to form a double-solvent metal salt solution;
(2) Adding a water-soluble dispersing agent and an oil-soluble dispersing agent into the double-solvent metal salt solution obtained in the step (1), and stirring to obtain a mixed solution;
(3) Adding sodium hydroxide into the mixed solution obtained in the step (2), and vigorously stirring to obtain a mixed suspension;
(4) Transferring the mixed suspension obtained in the step (3) to a dynamic crystallization kettle for crystallization;
(5) Centrifugally separating the suspension crystallized in the step (4) to obtain a solid substance, washing with deionized water for three times and washing with ethanol for three times to obtain a washed solid;
(6) Putting the solid cleaned in the step (5) into a planetary ball milling tank for ball milling, and washing a sample obtained after ball milling by adopting ethanol;
(7) Placing the ball-milled and washed sample obtained in the step (6) in a blast drying oven for drying, and then placing the dried sample in a muffle furnace for calcining to obtain the non-noble metal catalyst for removing high-concentration laughing gas at low temperature;
the non-noble metal catalyst is a copper-based catalyst, the copper-based catalyst takes copper oxide as a main catalyst and iron oxide as a cocatalyst, wherein the mass fraction of the copper oxide is 20-90 w.t%, and the balance is the iron oxide, and the specific surface area of the non-noble metal catalyst is 10-50m 2 And/g, the particle size is 0.1-20 microns.
2. The method for preparing the non-noble metal catalyst for removing the high-concentration laughing gas at the low temperature according to claim 1, which is characterized in that: the high-viscosity solvent in the step (1) refers to a solvent with the viscosity of more than 1.5 mPa.s at 20 ℃ and comprises n-propanol, n-butanol, isobutanol, glycerol and dimethyl sulfoxide, and the low-viscosity solvent comprises water, ethanol, methanol and n-hexane, and the volume ratio of the high-viscosity solvent to the low-viscosity solvent is (1-8): 1.
3. The method for preparing the non-noble metal catalyst for removing the high-concentration laughing gas at the low temperature according to claim 1, which is characterized in that: the copper salt in the step (1) adopts one or more of inorganic copper salt and/or organic copper salt, and the ferric salt adopts one or more of inorganic ferric salt and/or organic ferric salt; the mol ratio of the copper salt to the ferric salt is (0.7-2.5): 1.
4. The method for preparing the non-noble metal catalyst for removing the high-concentration laughing gas at the low temperature according to claim 1, which is characterized in that: the water-soluble dispersing agent in the step (2) comprises PVP, gelatin and polyethylene glycol; the oil-soluble dispersant comprises turpentine, oleylamine and octadecenoic acid; the mass ratio of the oil-soluble dispersing agent to the water-soluble dispersing agent is (0.1-1): 1; the total concentration of the two dispersants in the mixed solution is 0.01-0.1g/mL; the stirring speed is 100-150rpm, and the stirring time is 1-1.5 hours.
5. The method for preparing the non-noble metal catalyst for removing the high-concentration laughing gas at the low temperature according to claim 1, which is characterized in that: the mole number of sodium hydroxide added in the step (2) is 1-1.5 times of the sum of the mole numbers of ferric salt and cupric salt in the raw material; the rotation speed of the vigorous stirring is 200-400rpm, and the vigorous stirring time is 2-6 hours.
6. The method for preparing the non-noble metal catalyst for removing the high-concentration laughing gas at the low temperature according to claim 1, which is characterized in that: the crystallization temperature in the step (3) is 160-240 ℃ and the crystallization time is 12-24 hours.
7. The method for preparing the non-noble metal catalyst for removing the high-concentration laughing gas at the low temperature according to claim 1, which is characterized in that: the rotating speed of ball milling in the planetary ball milling tank in the step (6) is 150rpm, the ball milling agent adopts linolenic acid, and the ball milling time is 1-2 hours.
8. The method for preparing the non-noble metal catalyst for removing the high-concentration laughing gas at the low temperature according to claim 1, which is characterized in that: the drying temperature in the step (7) is 80 ℃, the drying time is 12 hours, the calcining temperature is 360 ℃, and the calcining time is 6 hours.
9. The use of a non-noble metal catalyst for removing high concentration laughing gas at low temperature according to any one of the preparation methods of claims 1 to 8, wherein: reducing substances are added in the process of removing the high-concentration laughing gas, and the reducing substances comprise carbon monoxide and hydrogen; the low temperature is 250-350 ℃, and the volume concentration of the high concentration laughing gas is 1-50%.
CN202211100533.8A 2022-09-09 2022-09-09 Non-noble metal catalyst for removing high-concentration laughing gas at low temperature and preparation method and application thereof Active CN115400756B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202211100533.8A CN115400756B (en) 2022-09-09 2022-09-09 Non-noble metal catalyst for removing high-concentration laughing gas at low temperature and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202211100533.8A CN115400756B (en) 2022-09-09 2022-09-09 Non-noble metal catalyst for removing high-concentration laughing gas at low temperature and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN115400756A CN115400756A (en) 2022-11-29
CN115400756B true CN115400756B (en) 2023-09-19

Family

ID=84165824

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202211100533.8A Active CN115400756B (en) 2022-09-09 2022-09-09 Non-noble metal catalyst for removing high-concentration laughing gas at low temperature and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN115400756B (en)

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4259303A (en) * 1978-10-17 1981-03-31 Kuraray Co., Ltd. Method of and system for treating waste anesthetic gas
DE102004058956A1 (en) * 2004-12-08 2006-06-14 Forschungszentrum Jülich GmbH Process for increasing the efficiency of surfactants and emulsifiers by means of additives
DE102008048159A1 (en) * 2008-09-19 2010-04-08 Universität Karlsruhe Catalyst, useful for decomposition of nitrous oxide, comprises a carrier material made of alpha or gamma aluminum oxide and a coating containing rhodium as active component
CN102489305A (en) * 2011-12-15 2012-06-13 南京工业大学 Transition metal composite oxide catalyst for catalytic decomposition of N2O and method for preparing catalyst
CN102962073A (en) * 2012-12-06 2013-03-13 辽宁科隆精细化工股份有限公司 Catalyst for directly decomposing N2O and preparation method of catalyst
CN104475112A (en) * 2014-12-15 2015-04-01 华烁科技股份有限公司 Catalyst capable of catalyzing and decomposing N2O under high-temperature water-oxygen supplying condition and preparation method of catalyst
CN105381801A (en) * 2015-11-12 2016-03-09 开滦(集团)有限责任公司 Catalyst capable of directly catalytically decomposing N2O
CN106076380A (en) * 2016-07-19 2016-11-09 青岛科技大学 The preparation method of modified coal activated carbon base catalyst
CN110523265A (en) * 2018-05-24 2019-12-03 中国石油化工股份有限公司 A kind of NO_x elimination method

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4259303A (en) * 1978-10-17 1981-03-31 Kuraray Co., Ltd. Method of and system for treating waste anesthetic gas
DE102004058956A1 (en) * 2004-12-08 2006-06-14 Forschungszentrum Jülich GmbH Process for increasing the efficiency of surfactants and emulsifiers by means of additives
CN101072860A (en) * 2004-12-08 2007-11-14 于利奇研究中心有限公司 Method for improving the efficiency of surfactants and emulsifiers by means of additives
DE102008048159A1 (en) * 2008-09-19 2010-04-08 Universität Karlsruhe Catalyst, useful for decomposition of nitrous oxide, comprises a carrier material made of alpha or gamma aluminum oxide and a coating containing rhodium as active component
CN102489305A (en) * 2011-12-15 2012-06-13 南京工业大学 Transition metal composite oxide catalyst for catalytic decomposition of N2O and method for preparing catalyst
CN102962073A (en) * 2012-12-06 2013-03-13 辽宁科隆精细化工股份有限公司 Catalyst for directly decomposing N2O and preparation method of catalyst
CN104475112A (en) * 2014-12-15 2015-04-01 华烁科技股份有限公司 Catalyst capable of catalyzing and decomposing N2O under high-temperature water-oxygen supplying condition and preparation method of catalyst
CN105381801A (en) * 2015-11-12 2016-03-09 开滦(集团)有限责任公司 Catalyst capable of directly catalytically decomposing N2O
CN106076380A (en) * 2016-07-19 2016-11-09 青岛科技大学 The preparation method of modified coal activated carbon base catalyst
CN110523265A (en) * 2018-05-24 2019-12-03 中国石油化工股份有限公司 A kind of NO_x elimination method

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
An influence of thermal treatment conditions of hydrotalcite-like materials on their catalytic activity in the process of N2O decomposition;Lucjan Chmielarz et al.;《J Therm Anal Calorim》;第105卷;161–170 *
Catalytic Decomposition of N2O on Ordered Crystalline Metal Oxides;Zhen Ma et al.;《Journal of Nanoscience and Nanotechnology》(第13期);5093–5103 *
Heterostructured hybrids of metal–organic frameworks (MOFs) and covalent–organic frameworks (COFs);Chuanpan Guo et al.,;《Journal of Materials Chemistry A》;475–507 *
Ru-Fe/C催化剂上邻氯硝基苯原位液相加氢性能;许响生;陈傲昂;周莉;李小青;顾辉子;严新焕;;催化学报(02);全文 *
介孔Co_3O_4-CeO_2复合氧化物的制备及在CO选择性氧化中的应用;刘华;许珊;王晓来;;分子催化(04);全文 *

Also Published As

Publication number Publication date
CN115400756A (en) 2022-11-29

Similar Documents

Publication Publication Date Title
CN109847697B (en) Biochar-based nano zero-valent iron material and preparation method thereof
CN111790422B (en) Graphitized nitrogen-complexed Fe (III) -Fe0Catalyst, and synthesis method and application thereof
CN111604082A (en) Preparation method of iron-loaded biochar, product and application of product
CN112169797B (en) Preparation method of Cu-Fe bimetallic complex magnetic chitosan carbon aerogel catalyst applied to wet oxidation
CN109835897B (en) Metal/heteroatom modified distiller's grain-based activated carbon and preparation method thereof
CN111939896B (en) Liquid catalyst for catalyzing ozonolysis at normal temperature and preparation method and application thereof
CN111905751B (en) Modified LaCoO by high-temperature quenching3-δMethod for catalyzing and degrading phenol in water body by using material
CN111437859B (en) High-efficiency non-metal carbon-based catalyst and preparation method and application thereof
CN113877599A (en) Cobalt-manganese spinel material and preparation method and application thereof
CN113546632A (en) Catalyst for treating phenolic wastewater by wet oxidation method and preparation method thereof
CN113600166A (en) Biomass-based catalyst for advanced oxidation and preparation method and application thereof
CN115318300A (en) Preparation method of magnetic biochar with catalytic and specific phosphorus adsorption performances
CN110170328B (en) Preparation method and application of cobalt manganate/N-doped graphene composite catalyst
CN115400756B (en) Non-noble metal catalyst for removing high-concentration laughing gas at low temperature and preparation method and application thereof
CN112206834B (en) Method for reconstructing and regenerating waste SCR denitration catalyst
CN110548519A (en) porous nano cobalt-doped zinc manganate spinel catalyst and preparation method and application thereof
CN114160136B (en) Preparation method of copper-iron-attapulgite-chitosan catalyst applied to heterogeneous Fenton-like system under condition of wide pH range
CN113304770B (en) Method for preparing nitrogen-rich metal catalyst by using nitrogen-modified chromium-containing leather scraps and application of nitrogen-rich metal catalyst
CN112915990B (en) Coal gangue in-situ carbon activation material and preparation method and application thereof
CN114700082B (en) Preparation method of catalyst for ozone tail gas destruction
CN114433162B (en) Composite catalyst and preparation method and application thereof
CN116764647B (en) Cubic CoCu spinel/carbon catalyst for efficient hydrogen production and pollutant degradation
CN115888793A (en) g-C 3 N 4 Preparation method and application of loaded iron monatomic catalyst
CN112588295B (en) Catalyst for organic wastewater treatment and preparation method thereof
CN109731888B (en) Harmless treatment method for chromium slag

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