CN112827512A - Desulfurization and denitrification agent and preparation method thereof - Google Patents

Desulfurization and denitrification agent and preparation method thereof Download PDF

Info

Publication number
CN112827512A
CN112827512A CN202011570792.8A CN202011570792A CN112827512A CN 112827512 A CN112827512 A CN 112827512A CN 202011570792 A CN202011570792 A CN 202011570792A CN 112827512 A CN112827512 A CN 112827512A
Authority
CN
China
Prior art keywords
desulfurization
temperature
parts
denitrification agent
reactor
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202011570792.8A
Other languages
Chinese (zh)
Inventor
褥星云
张景杏
赖鹏
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.)
Foshan Zhengzhou Environmental Protection Ventilation Equipment Co ltd
Original Assignee
Foshan Zhengzhou Environmental Protection Ventilation Equipment Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Foshan Zhengzhou Environmental Protection Ventilation Equipment Co ltd filed Critical Foshan Zhengzhou Environmental Protection Ventilation Equipment Co ltd
Priority to CN202011570792.8A priority Critical patent/CN112827512A/en
Publication of CN112827512A publication Critical patent/CN112827512A/en
Pending legal-status Critical Current

Links

Classifications

    • B01J35/56
    • 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
    • B01D53/8603Removing sulfur compounds
    • B01D53/8609Sulfur oxides
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • 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
    • 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
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • B01J37/0207Pretreatment of the support
    • 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
    • B01J37/082Decomposition and pyrolysis
    • B01J37/084Decomposition of carbon-containing compounds into carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/20Reductants
    • B01D2251/206Ammonium compounds
    • B01D2251/2062Ammonia
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/40Nitrogen compounds
    • B01D2257/404Nitrogen oxides other than dinitrogen oxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Materials Engineering (AREA)
  • Biomedical Technology (AREA)
  • Health & Medical Sciences (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Inorganic Chemistry (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention relates to the technical field of flue gas treatment, and discloses a desulfurization and denitrification agent which comprises the following raw materials in parts by weight: 10-15 parts of binder for raw coal,5-8 parts of dilute nitric acid 8-13 parts and 10-15 parts of ferric nitrate. Surface of desulfurization and denitrification agent to SO2Has the functions of adsorption and catalytic oxidation, and when no oxygen and water vapor exist in the flue gas, the active coke adsorbs SO2The adsorption capacity is small only by physical adsorption, and when oxygen and water vapor exist in the flue gas, chemical adsorption is also generated in addition to physical adsorption, and adsorbed SO2Under the catalytic oxidation of active coke with O in flue gas2Reaction to form SO3Then the reaction with water vapor to produce sulfuric acid, so as to greatly increase the adsorption capacity.

Description

Desulfurization and denitrification agent and preparation method thereof
Technical Field
The invention relates to the technical field of flue gas treatment, in particular to a desulfurization and denitrification agent and a preparation method thereof.
Background
SO discharged from coal combustion2And NOxIs a main atmospheric pollutant and is a main source causing acid rain and photochemical smog, and for years, the nation has paid great attention to the treatment of SO2 and NOx, along with NOXThe control standard is becoming more and more strict, and the desulfurization and denitrification technology is receiving increasing attention from various countries.
The flue gas desulfurization and denitration technology is a boiler flue gas purification technology applied to the chemical industry of generating multi-nitrogen oxides and sulfur oxides. Nitrogen oxides and sulfur oxides are one of the main sources of air pollution. The application of this technology is of considerable benefit for ambient air purification. Known flue gas desulfurization and denitrification technologies include the technologies of PAFP, ACFP, pyrolusite method, electron beam ammonia method, pulse corona method, gypsum wet method, catalytic oxidation method, microbial degradation method and the like.
At present, wet flue gas desulfurization and catalytic reduction denitration are two most common technologies for industrial application, but the technology has high investment cost and great operation difficulty, so that the popularization and the use of the technology in China are limited, and the development of a high-efficiency and low-cost desulfurization and denitration technology is urgently needed, so that a desulfurization and denitration agent and a preparation method thereof are provided.
Disclosure of Invention
Aiming at the defects in the prior art, the invention provides a desulfurization and denitrification agent and a preparation method thereof.
The invention provides the following technical scheme: a desulfurization and denitrification agent comprises the following raw materials in parts by weight:
10-15 parts of raw coal
5-8 parts of adhesive
8-13 parts of dilute nitric acid
10-15 parts of ferric nitrate
Preferably, the desulfurization and denitrification agent comprises the following raw materials in parts by weight:
raw coal 10 parts
5 parts of adhesive
Dilute nitric acid 8 portions
10 portions of ferric nitrate
Preferably, the desulfurization and denitrification agent comprises the following raw materials in parts by weight:
raw coal 12 parts
6 parts of adhesive
10 portions of dilute nitric acid
12 parts of ferric nitrate
Preferably, the desulfurization and denitrification agent comprises the following raw materials in parts by weight:
raw coal 15 parts
8 parts of adhesive
Dilute nitric acid 13 portions
15 parts of ferric nitrate
A preparation method of a desulfurization and denitrification agent comprises the following specific steps:
s1, crushing and screening raw coal, then feeding the raw coal into a fluidized bed mild gasification lignite upgrading reactor, fluidizing the raw coal in the upgrading reactor by hot air, performing mild gasification, combustion and dry distillation reactions in the reactor, controlling the temperature in the reactor within a proper range, and finally discharging the raw material;
s2, adding an adhesive into the processed raw coal after a powder making process, performing an extrusion molding process, drying, carbonizing and activating the dried raw material, and cooling to obtain activated coke;
s3, putting the activated coke into a three-neck round-bottom flask, adding diluted nitric acid solution, carrying out reflux treatment at constant temperature of 85 ℃ for 2h, taking out a sample, washing with water until the pH value is greater than 6, drying at 120 ℃ for 12h, putting the sample into a tubular stainless steel reactor, keeping the temperature of 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain a semi-finished product;
and S4, dipping the semi-finished product into ferric nitrate solution with a certain concentration, standing at room temperature for 2h, taking out, drying at 110 ℃ for 12h, keeping the temperature at 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain the adsorbent.
Preferably, in the carbonization process of S2, the carbonization temperature of the carbonization furnace is 450-550 ℃.
Preferably, in the activation process of S2, a steam activation process is adopted, and the activation temperature is controlled at 750-950 ℃.
Preferably, the adsorbent obtained in S4 is put into water after being used, stirred for 30 minutes and put into a stainless steel reactor, the temperature is raised to 700 ℃ under the condition of the nitrogen flow rate of 100mL/min, the temperature is kept for 2 hours, and the adsorbent is taken out after being cooled to room temperature, so that the adsorbent can be recycled.
Compared with the prior art, the desulfurization and denitrification agent and the preparation method thereof have the following beneficial effects:
surface of desulfurization and denitrification agent to SO2Has the functions of adsorption and catalytic oxidation, and when no oxygen and water vapor exist in the flue gas, the active coke adsorbs SO2The adsorption capacity is small only by physical adsorption, and when oxygen and water vapor exist in the flue gas, chemical adsorption is also generated in addition to physical adsorption, and adsorbed SO2Under the catalytic oxidation of active coke with O in flue gas2Reaction to form SO3Then the sulfuric acid reacts with water vapor to generate sulfuric acid, so that the adsorption capacity of the sulfuric acid is greatly increased;
surface of desulfurization and denitrification agent to NOXHas adsorption and catalytic oxidation effects, and can be used for adsorbing NO by adding ammonia into active coke adsorption desulfurization systemXReacts with NH to effectively react with NOXThe cleaning is carried out, and the cleaning is carried out,
fe is loaded in pores of desulfurization and denitrification agent2O3Can further improve the desulfurization activity of the adsorbent, and the active coke can remove ash in the active coke after modification treatment to form rich woven mesh structure, improve the surface property of the active coke and be beneficial to SO2Adsorption and oxidation on the surface of the semicoke, supported metal oxides, on the one hand, capable of promoting SO2On the other hand with SO2Interaction can also occur, and a certain sulfur fixing effect is achieved;
in addition, after the active coke is modified, the specific surface area is increased, oxygen-containing functional groups and basic functional groups on the surface are increased, the adsorption and oxidation conversion of gas NO are facilitated, and the denitration activity is obviously improved.
Detailed Description
To make the objects, technical solutions and advantages of the embodiments of the present disclosure clearer and to describe more fully technical solutions of the embodiments of the present disclosure, and to keep the following description of the embodiments of the present disclosure clear and concise, detailed descriptions of known functions and known parts of the disclosure are omitted so as to avoid unnecessarily obscuring the concepts of the present disclosure.
A desulfurization and denitrification agent comprises the following raw materials in parts by weight:
10-15 parts of raw coal
5-8 parts of adhesive
8-13 parts of dilute nitric acid
10-15 parts of ferric nitrate
A preparation method of a desulfurization and denitrification agent comprises the following specific steps:
s1, crushing and screening raw coal, then feeding the raw coal into a fluidized bed mild gasification lignite upgrading reactor, fluidizing the raw coal in the upgrading reactor by hot air, performing mild gasification, combustion and dry distillation reactions in the reactor, controlling the temperature in the reactor within a proper range, and finally discharging the raw material;
s2, adding a binder into the processed raw coal after a powder preparation process, performing an extrusion molding process, drying, carbonizing and activating the dried raw material, and cooling to obtain activated coke, wherein in the carbonization process, the carbonization temperature of a carbonization furnace is 450-550 ℃, and in the activation process, a steam activation process is adopted, and the activation temperature is controlled to be 750-950 ℃;
s3, putting the activated coke into a three-neck round-bottom flask, adding diluted nitric acid solution, carrying out reflux treatment at constant temperature of 85 ℃ for 2h, taking out a sample, washing with water until the pH value is greater than 6, drying at 120 ℃ for 12h, putting the sample into a tubular stainless steel reactor, keeping the temperature of 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain a semi-finished product;
and S4, dipping the semi-finished product into ferric nitrate solution with a certain concentration, standing at room temperature for 2h, taking out, drying at 110 ℃ for 12h, keeping the temperature at 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain the adsorbent.
After the adsorbent is used, the adsorbent is put into water, stirred for 30 minutes and put into a stainless steel reactor, the temperature is raised to 700 ℃ under the condition of 100mL/min of nitrogen flow, the temperature is kept for 2 hours, and the adsorbent is taken out after being cooled to room temperature and can be recycled.
Example 1
A desulfurization and denitrification agent comprises the following raw materials in parts by weight:
raw coal 10 parts
5 parts of adhesive
Dilute nitric acid 8 portions
10 portions of ferric nitrate
A preparation method of a desulfurization and denitrification agent comprises the following specific steps:
s1, crushing and screening raw coal, then feeding the raw coal into a fluidized bed mild gasification lignite upgrading reactor, fluidizing the raw coal in the upgrading reactor by hot air, performing mild gasification, combustion and dry distillation reactions in the reactor, controlling the temperature in the reactor within a proper range, and finally discharging the raw material;
s2, adding a binder into the processed raw coal after a powder preparation process, performing an extrusion molding process, drying, carbonizing and activating the dried raw material, and cooling to obtain activated coke, wherein in the carbonization process, the carbonization temperature of a carbonization furnace is 450-550 ℃, and in the activation process, a steam activation process is adopted, and the activation temperature is controlled to be 750-950 ℃;
s3, putting the activated coke into a three-neck round-bottom flask, adding diluted nitric acid solution, carrying out reflux treatment at constant temperature of 85 ℃ for 2h, taking out a sample, washing with water until the pH value is greater than 6, drying at 120 ℃ for 12h, putting the sample into a tubular stainless steel reactor, keeping the temperature of 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain a semi-finished product;
and S4, dipping the semi-finished product into ferric nitrate solution with a certain concentration, standing at room temperature for 2h, taking out, drying at 110 ℃ for 12h, keeping the temperature at 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain the adsorbent.
After the adsorbent is used, the adsorbent is put into water, stirred for 30 minutes and put into a stainless steel reactor, the temperature is raised to 700 ℃ under the condition of 100mL/min of nitrogen flow, the temperature is kept for 2 hours, and the adsorbent is taken out after being cooled to room temperature and can be recycled.
Example 2
A desulfurization and denitrification agent comprises the following raw materials in parts by weight:
raw coal 12 parts
6 parts of adhesive
10 portions of dilute nitric acid
12 parts of ferric nitrate
A preparation method of a desulfurization and denitrification agent comprises the following specific steps:
s1, crushing and screening raw coal, then feeding the raw coal into a fluidized bed mild gasification lignite upgrading reactor, fluidizing the raw coal in the upgrading reactor by hot air, performing mild gasification, combustion and dry distillation reactions in the reactor, controlling the temperature in the reactor within a proper range, and finally discharging the raw material;
s2, adding a binder into the processed raw coal after a powder preparation process, performing an extrusion molding process, drying, carbonizing and activating the dried raw material, and cooling to obtain activated coke, wherein in the carbonization process, the carbonization temperature of a carbonization furnace is 450-550 ℃, and in the activation process, a steam activation process is adopted, and the activation temperature is controlled to be 750-950 ℃;
s3, putting the activated coke into a three-neck round-bottom flask, adding diluted nitric acid solution, carrying out reflux treatment at constant temperature of 85 ℃ for 2h, taking out a sample, washing with water until the pH value is greater than 6, drying at 120 ℃ for 12h, putting the sample into a tubular stainless steel reactor, keeping the temperature of 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain a semi-finished product;
and S4, dipping the semi-finished product into ferric nitrate solution with a certain concentration, standing at room temperature for 2h, taking out, drying at 110 ℃ for 12h, keeping the temperature at 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain the adsorbent.
After the adsorbent is used, the adsorbent is put into water, stirred for 30 minutes and put into a stainless steel reactor, the temperature is raised to 700 ℃ under the condition of 100mL/min of nitrogen flow, the temperature is kept for 2 hours, and the adsorbent is taken out after being cooled to room temperature and can be recycled.
Example 3
A desulfurization and denitrification agent comprises the following raw materials in parts by weight:
raw coal 15 parts
8 parts of adhesive
Dilute nitric acid 13 portions
15 parts of ferric nitrate
A preparation method of a desulfurization and denitrification agent comprises the following specific steps:
s1, crushing and screening raw coal, then feeding the raw coal into a fluidized bed mild gasification lignite upgrading reactor, fluidizing the raw coal in the upgrading reactor by hot air, performing mild gasification, combustion and dry distillation reactions in the reactor, controlling the temperature in the reactor within a proper range, and finally discharging the raw material;
s2, adding a binder into the processed raw coal after a powder preparation process, performing an extrusion molding process, drying, carbonizing and activating the dried raw material, and cooling to obtain activated coke, wherein in the carbonization process, the carbonization temperature of a carbonization furnace is 450-550 ℃, and in the activation process, a steam activation process is adopted, and the activation temperature is controlled to be 750-950 ℃;
s3, putting the activated coke into a three-neck round-bottom flask, adding diluted nitric acid solution, carrying out reflux treatment at constant temperature of 85 ℃ for 2h, taking out a sample, washing with water until the pH value is greater than 6, drying at 120 ℃ for 12h, putting the sample into a tubular stainless steel reactor, keeping the temperature of 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain a semi-finished product;
and S4, dipping the semi-finished product into ferric nitrate solution with a certain concentration, standing at room temperature for 2h, taking out, drying at 110 ℃ for 12h, keeping the temperature at 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain the adsorbent.
After the adsorbent is used, the adsorbent is put into water, stirred for 30 minutes and put into a stainless steel reactor, the temperature is raised to 700 ℃ under the condition of 100mL/min of nitrogen flow, the temperature is kept for 2 hours, and the adsorbent is taken out after being cooled to room temperature and can be recycled.
Experiment of
The desulfurization and denitrification agents are prepared according to the formula and the process of the examples 1, 2 and 3, 8 groups of the desulfurization and denitrification agents prepared in the examples 1, 2 and 3 are tested under the same environment, and the desulfurization and denitrification conditions are detected within 6 hours, wherein the detailed data are as follows:
Figure 619137DEST_PATH_IMAGE002
the desulfurization and denitrification agents are prepared according to the formula and the process of the examples 1, 2 and 3, and the desulfurization and denitrification conditions are detected under the same environment and at different times, and the detailed data are as follows:
Figure 333015DEST_PATH_IMAGE004
therefore, the desulfurization and denitrification agent has good desulfurization and denitrification effects.
The above embodiments are only exemplary embodiments of the present invention, and are not intended to limit the present invention, and the scope of the present invention is defined by the claims. Various modifications and equivalents may be made by those skilled in the art within the spirit and scope of the present invention, and such modifications and equivalents should also be considered as falling within the scope of the present invention.

Claims (8)

1. The desulfurization and denitrification agent is characterized by comprising the following raw materials in parts by weight:
Figure RE-FDA0003028893950000011
2. the desulfurization and denitrification agent is characterized by comprising the following raw materials in parts by weight:
Figure RE-FDA0003028893950000012
3. the desulfurization and denitrification agent is characterized by comprising the following raw materials in parts by weight:
Figure RE-FDA0003028893950000013
4. a desulfurization and denitrification agent is characterized in that: the composite material comprises the following raw materials in parts by weight:
Figure RE-FDA0003028893950000014
5. the preparation method of the desulfurization and denitrification agent as claimed in any one of claims 1 to 4, which is characterized by comprising the following steps:
s1, crushing and screening raw coal, then feeding the raw coal into a fluidized bed mild gasification lignite upgrading reactor, fluidizing the raw coal in the upgrading reactor by hot air, performing mild gasification, combustion and dry distillation reactions in the reactor, controlling the temperature in the reactor within a proper range, and finally discharging the raw material;
s2, adding an adhesive into the processed raw coal after a powder making process, performing an extrusion molding process, drying, carbonizing and activating the dried raw material, and cooling to obtain activated coke;
s3, putting the activated coke into a three-neck round-bottom flask, adding diluted nitric acid solution, carrying out reflux treatment at constant temperature of 85 ℃ for 2h, taking out a sample, washing with water until the pH value is greater than 6, drying at 120 ℃ for 12h, putting the sample into a tubular stainless steel reactor, keeping the temperature of 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain a semi-finished product;
and S4, dipping the semi-finished product into ferric nitrate solution with a certain concentration, standing at room temperature for 2h, taking out, drying at 110 ℃ for 12h, keeping the temperature at 700 ℃ for 2h under the protection of nitrogen, and cooling to room temperature to obtain the adsorbent.
6. The method as claimed in claim 5, wherein the carbonization temperature of the carbonization furnace is 450-550 ℃ in the carbonization process of S2.
7. The method as claimed in claim 5, wherein the activation of S2 is performed by a steam activation process, wherein the activation temperature is controlled at 750-950 ℃.
8. The method for preparing a desulfurization and denitrification agent according to claim 5, wherein the adsorbent obtained in S4 is placed in water after use, stirred for 30 minutes, placed in a stainless steel reactor, heated to 700 ℃ under the condition of a nitrogen flow of 100mL/min, kept at the constant temperature for 2 hours, cooled to room temperature, and taken out for recycling.
CN202011570792.8A 2020-12-26 2020-12-26 Desulfurization and denitrification agent and preparation method thereof Pending CN112827512A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202011570792.8A CN112827512A (en) 2020-12-26 2020-12-26 Desulfurization and denitrification agent and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202011570792.8A CN112827512A (en) 2020-12-26 2020-12-26 Desulfurization and denitrification agent and preparation method thereof

Publications (1)

Publication Number Publication Date
CN112827512A true CN112827512A (en) 2021-05-25

Family

ID=75924717

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202011570792.8A Pending CN112827512A (en) 2020-12-26 2020-12-26 Desulfurization and denitrification agent and preparation method thereof

Country Status (1)

Country Link
CN (1) CN112827512A (en)

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63294942A (en) * 1987-05-26 1988-12-01 Central Res Inst Of Electric Power Ind Dry desulfurizing adsorbent
CN102491324A (en) * 2011-11-29 2012-06-13 山西新华化工有限责任公司 Preparation method of high denitrification activated coke
CN104229793A (en) * 2014-09-12 2014-12-24 中国华能集团清洁能源技术研究院有限公司 Brown coal active coke and preparation method thereof
CN104525116A (en) * 2014-12-31 2015-04-22 上海克硫环保科技股份有限公司 Desulfurization and denitrification modified active coke and preparation method thereof
US20190046962A1 (en) * 2016-12-23 2019-02-14 Valiant Co., Ltd. Method for preparing molecular sieve-multielement oxide composite integrally extruded denitration catalyst
CN111704132A (en) * 2020-06-24 2020-09-25 中冶南方都市环保工程技术股份有限公司 Active coke and preparation method and application thereof
CN111847448A (en) * 2020-07-07 2020-10-30 太原理工大学 Columnar activated coke based on waste plastic binder and preparation method thereof

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63294942A (en) * 1987-05-26 1988-12-01 Central Res Inst Of Electric Power Ind Dry desulfurizing adsorbent
CN102491324A (en) * 2011-11-29 2012-06-13 山西新华化工有限责任公司 Preparation method of high denitrification activated coke
CN104229793A (en) * 2014-09-12 2014-12-24 中国华能集团清洁能源技术研究院有限公司 Brown coal active coke and preparation method thereof
CN104525116A (en) * 2014-12-31 2015-04-22 上海克硫环保科技股份有限公司 Desulfurization and denitrification modified active coke and preparation method thereof
US20190046962A1 (en) * 2016-12-23 2019-02-14 Valiant Co., Ltd. Method for preparing molecular sieve-multielement oxide composite integrally extruded denitration catalyst
CN111704132A (en) * 2020-06-24 2020-09-25 中冶南方都市环保工程技术股份有限公司 Active coke and preparation method and application thereof
CN111847448A (en) * 2020-07-07 2020-10-30 太原理工大学 Columnar activated coke based on waste plastic binder and preparation method thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
于英民等: "半焦吸附剂烟气脱硫脱硝性能", 《燃料化学学报》 *

Similar Documents

Publication Publication Date Title
Knoblauch et al. Application of active coke in processes of SO2-and NOx-removal from flue gases
JP3272367B2 (en) Heat-treated activated carbon fiber for denitration, method for producing the same, denitration method using the same, and denitration system using the same
CN107213917B (en) Amine compound-supported composite denitration catalyst, and preparation method and application thereof
CN1126594C (en) Flue-gas treatment system
JP2012245444A (en) Method for desulfurizing and denitrating sintering furnace exhaust gas
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
CN104190478A (en) Regeneration method of denitration desulfurization active carbon catalyst
CN108993476B (en) Metal oxide-vanadate/TiO2Catalyst, preparation method and application thereof
CN110407210A (en) A kind of active carbon base catalytic desulfurizing process
CN110252387A (en) A kind of ferrum-based catalyst and its preparation method and application for high temperature denitration
CN112892547A (en) Catalyst for simultaneously removing nitrogen oxide and carbon monoxide and preparation method thereof
CN110102302B (en) Catalyst for carbonyl sulfide purification and preparation method and application thereof
KR101527028B1 (en) Activated carbon catalyst
US6106791A (en) Exhaust gas treating systems
CN106984319B (en) It is a kind of for removing the iron-based composite catalyst and preparation method thereof of nitrogen oxides in effluent and organic pollutant simultaneously
CN106732547B (en) Demercuration catalyst for low-temperature oxidation of zero-valent mercury in coal-fired flue gas and preparation method thereof
CN112827512A (en) Desulfurization and denitrification agent and preparation method thereof
CN112221488A (en) Novel core-shell structure catalyst for synergistic denitration and demercuration and preparation method thereof
Kastner et al. Catalytic ozonation of ammonia using biomass char and wood fly ash
CN111375274B (en) Containing SO 2 Gas treatment method and apparatus
KR101651220B1 (en) Preparing method of platinum/vanadium/titania catalyst for removing ammonia
KR101329828B1 (en) A tungsten/titania-based catalyst and a method of preparing the same
CN109647175B (en) Cyanuric acid denitration agent, and preparation method and application thereof
CN113546644A (en) Preparation method and application of catalyst for deeply removing organic sulfur from coke oven gas
KR102224335B1 (en) Selective oxidation catalyst for converting gaseous ammonia into nitrogen and its production method

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20210525

RJ01 Rejection of invention patent application after publication