CN114832578A - Method for adsorbing hydrogen fluoride and hydrogen chloride by SBA-15 adsorbent - Google Patents

Method for adsorbing hydrogen fluoride and hydrogen chloride by SBA-15 adsorbent Download PDF

Info

Publication number
CN114832578A
CN114832578A CN202210508680.2A CN202210508680A CN114832578A CN 114832578 A CN114832578 A CN 114832578A CN 202210508680 A CN202210508680 A CN 202210508680A CN 114832578 A CN114832578 A CN 114832578A
Authority
CN
China
Prior art keywords
sba
hydrogen chloride
hydrogen fluoride
hydrogen
adsorbent
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
CN202210508680.2A
Other languages
Chinese (zh)
Inventor
张芷桐
李凯
郝星光
孙鑫
王驰
宁平
王飞
马懿星
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.)
Jiangxi Blue Environmental Engineering Technology Co ltd
Kunming University of Science and Technology
Original Assignee
Jiangxi Blue Environmental Engineering Technology Co ltd
Kunming University of Science 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 Jiangxi Blue Environmental Engineering Technology Co ltd, Kunming University of Science and Technology filed Critical Jiangxi Blue Environmental Engineering Technology Co ltd
Priority to CN202210508680.2A priority Critical patent/CN114832578A/en
Publication of CN114832578A publication Critical patent/CN114832578A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • 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
    • B01D53/02Separation 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 by adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation 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 by adsorption, e.g. preparative gas chromatography with stationary adsorbents
    • 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
    • B01D53/46Removing components of defined structure
    • B01D53/68Halogens or halogen compounds
    • 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
    • B01D53/77Liquid phase processes
    • B01D53/78Liquid phase processes with gas-liquid contact
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/30Alkali metal compounds
    • B01D2251/306Alkali metal compounds of potassium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/60Inorganic bases or salts
    • B01D2251/604Hydroxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/106Silica or silicates
    • B01D2253/108Zeolites
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/20Halogens or halogen compounds
    • B01D2257/204Inorganic halogen compounds
    • B01D2257/2045Hydrochloric acid
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/20Halogens or halogen compounds
    • B01D2257/204Inorganic halogen compounds
    • B01D2257/2047Hydrofluoric acid

Abstract

The invention discloses a method for adsorbing hydrogen fluoride and hydrogen chloride by using an SBA-15 adsorbent, belonging to the technical field of dry method deacidification waste gas. The method comprises the steps of crushing SBA-15 to obtain SBA-15 particles, loading the SBA-15 particles on the surface of a filler by adopting a roasting technology, putting the particles into a filler tower to remove hydrogen fluoride and hydrogen chloride gas, and absorbing unreacted hydrogen fluoride and hydrogen chloride gas by using an absorption liquid to complete the absorption of the hydrogen fluoride and the hydrogen chloride. The method for adsorbing hydrogen fluoride and hydrogen chloride by fixing the SBA-15 adsorbent on the surface of the filler through the high-temperature filler roasting technology has a good removal effect on the hydrogen fluoride and the hydrogen chloride, and does not generate flying powder. The adsorption method has simple equipment structure and simple and convenient operation, can be widely used for removing hydrogen fluoride and hydrogen chloride from various gas sources, and has good application prospect.

Description

Method for adsorbing hydrogen fluoride and hydrogen chloride by SBA-15 adsorbent
Technical Field
The invention belongs to the technical field of dry deacidification of waste gas, and particularly relates to a method for adsorbing hydrogen fluoride and hydrogen chloride by using an SBA-15 adsorbent.
Background
Hydrogen fluoride (Hydrogen fluoride-HF) is a colorless, pungent and toxic gas, has very strong hygroscopicity, generates white smoke when contacting air, and is easily dissolved in water. The main source of atmospheric HF is the emission of industrial waste gases. For example, in the aluminum production industry, a large amount of gases such as hydrofluoric acid and silicon tetrafluoride and dusts such as aluminum fluoride and calcium fluoride are generated in the production process of aluminum by the electrolysis method. The harm of hydrogen fluoride to human body is twenty times of that of sulfur dioxide, and when the content of fluoride in air exceeds 1mg/m 3 In time, direct damage can occur to the eyes, skin and respiratory organs of humans. Fluoride produced by the hydrogen fluoride reaction also causes bone damage, tooth weakness, and the like. The corrosion effect on aluminum products is also extremely strong.
Hydrogen chloride (Hydrogen chloride-HCl) is a colorless gas with a choking odor. HCl gas in the atmosphere mainly comes from the aspects of coal combustion and industrial waste gas emission, and acid gases such as HCl and the like can be generated by incomplete combustion of coal. And hydrogen chloride gas is generated in the production process of industries such as paper mills, steel industry, electroplating industry and the like. Most of the hydrogen chloride is retained by the mucosa of the upper respiratory tract after being inhaled, and a part of the hydrogen chloride is neutralized, so that the hydrogen chloride has stimulation and burning effects on local mucosa, causes inflammatory edema, hyperemia and necrosis, can react with various metals to generate hydrogen, and generates hydrogen cyanide which is a virulent agent when encountering cyanide. The combination of atmospheric hydrogen chloride and air water can form the acidic substance hydrochloric acid. Thus aggravating the formation of acid rain which has great harm to plants and buildings.
In general, the methods for removing HF and HCl include wet, dry, semi-dry deacidification, and the like. In the dry method, lime powder is directly sprayed into a flue to react with acid gas in the flue to generate a solid product. Its advantages are: no wastewater is generated (no wastewater treatment equipment is required to be configured), and the operation is simple; the disadvantages are: the lime powder consumption is large, the later flying powder treatment cost is increased, and the removal efficiency is low. However, studies on improvement of the removal efficiency of hydrogen fluoride and hydrogen chloride by using SBA-15 adsorbent have been reported.
Disclosure of Invention
The invention provides a method for adsorbing hydrogen fluoride and hydrogen chloride by using an SBA-15 adsorbent, which aims to solve the problems of high lime powder consumption, serious powder flying, low removal efficiency and the like in the prior art. The method for adsorbing hydrogen fluoride and hydrogen chloride by fixing the SBA-15 adsorbent on the surface of the filler through the high-temperature filler roasting technology has a good removal effect on the hydrogen fluoride and the hydrogen chloride, and does not generate flying powder.
In order to achieve the purpose, the invention provides the following scheme:
the invention provides a method for adsorbing hydrogen fluoride and hydrogen chloride by using an SBA-15 adsorbent, which comprises the following steps: the method comprises the steps of crushing SBA-15 to obtain SBA-15 particles, loading the SBA-15 particles on the surface of a filler by adopting a roasting technology, putting the particles into a filler tower to remove hydrogen fluoride and hydrogen chloride gas, and absorbing unreacted hydrogen fluoride and hydrogen chloride gas by using an absorption liquid to complete the absorption of the hydrogen fluoride and the hydrogen chloride.
Furthermore, the crushing is to crush SBA-15 into particles of 40-60 meshes.
Further, the filler is one or more of high-pressure graphite packing, aluminum silicate, borax and kaolin.
In the invention, all the selected fillers have the property of high temperature resistance. Ultrasonic treatment and rotary steaming treatment are also carried out before roasting.
Further, the roasting temperature is 400-500 ℃, and the roasting time is 2-5 hours.
Further, nitrogen is introduced into the packed tower, and the gas flow rate is 50-150 mol/min.
Further, the absorption liquid is 2mmol/L KOH solution.
The invention has the beneficial effects that:
the method for adsorbing hydrogen fluoride and hydrogen chloride by fixing the SBA-15 adsorbent on the surface of the filler through a high-temperature filler roasting technology has a good effect of removing hydrogen fluoride and hydrogen chloride, the removal rate of hydrogen fluoride can reach 99%, the removal rate of hydrogen chloride can reach 96%, and no flying powder is generated. The adsorption method has simple equipment structure and simple and convenient operation, can be widely used for removing hydrogen fluoride and hydrogen chloride from various gas sources, and has good application prospect.
Drawings
In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the drawings needed in the embodiments will be briefly described below, and it is obvious that the drawings in the following description are only some embodiments of the present invention, and it is obvious for those skilled in the art to obtain other drawings without creative efforts.
FIG. 1 is an adsorption curve of example 1 for hydrogen fluoride removal at 15 ℃ and 58% RH;
FIG. 2 is an adsorption curve of example 1 at 15 ℃ and 58% RH for hydrogen chloride removal.
Detailed Description
Reference will now be made in detail to various exemplary embodiments of the invention, the detailed description should not be construed as limiting the invention but as a more detailed description of certain aspects, features and embodiments of the invention.
It is to be understood that the terminology used herein is for the purpose of describing particular embodiments only and is not intended to be limiting of the invention. Further, for numerical ranges in this disclosure, it is understood that each intervening value, between the upper and lower limit of that range, is also specifically disclosed. Every smaller range between any stated value or intervening value in a stated range and any other stated or intervening value in a stated range is encompassed within the invention. The upper and lower limits of these smaller ranges may independently be included or excluded in the range.
Unless defined otherwise, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art to which this invention belongs. Although only preferred methods and materials are described herein, any methods and materials similar or equivalent to those described herein can be used in the practice or testing of the present invention. All documents mentioned in this specification are incorporated by reference herein for the purpose of disclosing and describing the methods and/or materials associated with the documents. In case of conflict with any incorporated document, the present specification will control.
It will be apparent to those skilled in the art that various modifications and variations can be made in the specific embodiments of the present disclosure without departing from the scope or spirit of the disclosure. Other embodiments will be apparent to those skilled in the art from consideration of the specification. It is intended that the specification and examples be considered as exemplary only.
As used herein, the terms "comprising," "including," "having," "containing," and the like are open-ended terms that mean including, but not limited to.
SBA-15 was prepared in all the following examples: soaking P123 in hydrochloric acid solution (the concentration of hydrochloric acid is 2mol/L, the mass ratio of P123 to hydrochloric acid solution is 1:11.76), and stirring at 35 ℃ and the rotation speed of 350r/min until the solution is dissolved to obtain mixed solution; dropping tetraethyl silicate into the mixed solution (the mass ratio of tetraethyl silicate to P123 is 1:0.36, and the dropping speed of tetraethyl silicate is 0.30mL/min), and stirring for 24h to obtain a white suspension; placing the white suspension in a reaction kettle, and carrying out hydrothermal treatment at 100 ℃ for 24 hours; the SBA-15 was obtained by filtration, washing (solution washing to neutrality), drying (in a forced air oven at 100 ℃) and calcination (at 550 ℃ for 5 h).
Example 1
The method comprises the steps of crushing SBA-15 to obtain SBA-15 particles of 40-60 meshes, loading the SBA-15 particles on the surface of a kaolin filler by adopting a roasting technology, wherein the roasting temperature is 400-500 ℃, the roasting time is 5 hours, putting the particles into a packed tower to remove hydrogen fluoride and hydrogen chloride gas (the concentrations of HF and HCl in industrial waste gas containing hydrogen fluoride and hydrogen chloride obtained from a certain copper smelting plant are 135ppm and 164ppm respectively), introducing nitrogen into the packed tower, enabling the gas flow rate to be 100mol/min, and absorbing unreacted hydrogen fluoride and hydrogen chloride gas by using an absorption liquid (2mmol/L KOH solution) to obtain absorption curves of the hydrogen fluoride and the hydrogen chloride, wherein the absorption curves are shown in figures 1 and 2.
As can be seen from FIG. 1, the removal effect of SBA-15 on fluorine ions is good, penetration is carried out for about 350min (the absorption efficiency is less than 90%), and the removal rate on hydrogen fluoride can reach 99%.
As can be seen from FIG. 2, the chlorine ion removal effect is good, penetration is performed for about 50min, and the removal rate of hydrogen chloride can reach 96%.
In the embodiment, SBA-15 particles are loaded on the surface of a kaolin filler by adopting a high-temperature roasting technology (roasting at 400-500 ℃), and compared with low-temperature roasting (roasting at 100-200 ℃), nitrogen with flow rates of 50mol/min, 100mol/min and 150mol/min is respectively used for sweeping the filler loaded with SBA-15, mass changes before and after sweeping are obtained, the mass changes are recorded in table 1, the mass difference of the filler before and after nitrogen sweeping of a high-temperature roasting group is small, and the powder flying of SBA-15 powder can be reduced.
TABLE 1 Mass Difference of fillers before and after nitrogen purging
Figure BDA0003637071340000051
Example 2
The method comprises the steps of crushing SBA-15 to obtain SBA-15 particles of 40-60 meshes, loading the SBA-15 particles on the surface of a high-pressure graphite packing filler by adopting a roasting technology, roasting at 400-500 ℃ for 5 hours, removing hydrogen fluoride and hydrogen chloride gas (the concentrations of HF and HCl in industrial waste gas containing hydrogen fluoride and hydrogen chloride obtained from a certain garbage incineration plant are 123ppm and 147ppm respectively) in a packed tower, introducing nitrogen into the packed tower at a gas flow rate of 100mol/min, and absorbing unreacted hydrogen fluoride and hydrogen chloride gas by using an absorption liquid (2mmol/L KOH solution), so that the adsorption of the hydrogen fluoride and the hydrogen chloride is completed.
Example 3
The method comprises the steps of crushing SBA-15 to obtain SBA-15 particles of 40-60 meshes, loading the SBA-15 particles on the surface of a borax filler by adopting a roasting technology, roasting at 400-500 ℃ for 5 hours, putting the particles into a packed tower to remove hydrogen fluoride and hydrogen chloride gas (the concentrations of HF and HCl are 148ppm and 172ppm respectively in industrial waste gas containing hydrogen fluoride and hydrogen chloride obtained from a certain power plant), introducing nitrogen into the packed tower at a gas flow rate of 100mol/min, and absorbing unreacted hydrogen fluoride and hydrogen chloride gas by using an absorption liquid (2mmol/L KOH solution), namely completing the absorption of hydrogen fluoride and hydrogen chloride.
The removal rate of the hydrogen fluoride and the hydrogen chloride in each example is shown in Table 2, and the treatment cost is compared with that in Table 3 (the conventional treatment method specifically comprises the step of directly spraying lime powder into a flue to react with acid gas in the flue to generate a solid product, so that the solid product can remove the hydrogen fluoride and the hydrogen chloride with the same quality).
TABLE 2
Item Hydrogen fluoride removal rate (%) Hydrogen chloride removal rate (%)
Example 1 99.0% 96.5%
Example 2 98.8% 94.5%
Example 3 98.5% 95.2%
TABLE 3
Figure BDA0003637071340000071
As shown in tables 2 and 3, the method of the present invention, which uses SBA-15 adsorbent to adsorb hydrogen fluoride and hydrogen chloride by fixing on the surface of the filler by high temperature filler roasting technique, has a good effect of removing hydrogen fluoride and hydrogen chloride and a low cost.
The above-described embodiments are merely illustrative of the preferred embodiments of the present invention, and do not limit the scope of the present invention, and various modifications and improvements of the technical solutions of the present invention can be made by those skilled in the art without departing from the spirit of the present invention, and the technical solutions of the present invention are within the scope of the present invention defined by the claims.

Claims (6)

1. A method for adsorbing hydrogen fluoride and hydrogen chloride by using SBA-15 adsorbent is characterized by comprising the following steps: the method comprises the steps of crushing SBA-15 to obtain SBA-15 particles, loading the SBA-15 particles on the surface of a filler by adopting a roasting technology, putting the particles into a filler tower to remove hydrogen fluoride and hydrogen chloride gas, and absorbing unreacted hydrogen fluoride and hydrogen chloride gas by using an absorption liquid to complete the absorption of the hydrogen fluoride and the hydrogen chloride.
2. The method for adsorbing hydrogen fluoride and hydrogen chloride by using the SBA-15 adsorbent as claimed in claim 1, wherein the pulverization is carried out by pulverizing SBA-15 into particles of 40-60 meshes.
3. The method for adsorbing hydrogen fluoride and hydrogen chloride by using the SBA-15 adsorbent according to claim 1, wherein the filler is one or more of high pressure graphite packing, aluminum silicate, borax and kaolin.
4. The method for adsorbing hydrogen fluoride and hydrogen chloride by using the SBA-15 adsorbent as claimed in claim 1, wherein the roasting temperature is 400-500 ℃ and the roasting time is 2-5 h.
5. The method for adsorbing hydrogen fluoride and hydrogen chloride by using the SBA-15 adsorbent as claimed in claim 1, wherein nitrogen is introduced into the packed tower at a gas flow rate of 50-150 mol/min.
6. The method for adsorbing hydrogen fluoride and hydrogen chloride by using the SBA-15 adsorbent as claimed in claim 1, wherein the absorbing solution is 2mmol/L KOH solution.
CN202210508680.2A 2022-05-10 2022-05-10 Method for adsorbing hydrogen fluoride and hydrogen chloride by SBA-15 adsorbent Pending CN114832578A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210508680.2A CN114832578A (en) 2022-05-10 2022-05-10 Method for adsorbing hydrogen fluoride and hydrogen chloride by SBA-15 adsorbent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210508680.2A CN114832578A (en) 2022-05-10 2022-05-10 Method for adsorbing hydrogen fluoride and hydrogen chloride by SBA-15 adsorbent

Publications (1)

Publication Number Publication Date
CN114832578A true CN114832578A (en) 2022-08-02

Family

ID=82570602

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210508680.2A Pending CN114832578A (en) 2022-05-10 2022-05-10 Method for adsorbing hydrogen fluoride and hydrogen chloride by SBA-15 adsorbent

Country Status (1)

Country Link
CN (1) CN114832578A (en)

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1887410A (en) * 2005-06-29 2007-01-03 财团法人工业技术研究院 Process and apparatus for treating gas containing fluoric compound
JP2007091560A (en) * 2005-09-30 2007-04-12 Tokuyama Corp Process for refining hydrogen chloride gas
CN205876105U (en) * 2016-07-08 2017-01-11 北京京铁金龙铁路消防工程有限公司 Fire -proof door
CN109173990A (en) * 2018-09-17 2019-01-11 成都新柯力化工科技有限公司 A kind of composite mesoporous adsorbent material and preparation method for air cleaning
CN109865309A (en) * 2017-12-01 2019-06-11 中国科学院大连化学物理研究所 A kind of enrichment of volatile organic trace compounds low temperature and Thermal desorption integration cold-trap
CN110433780A (en) * 2019-08-16 2019-11-12 昆明理工大学 A kind of mesoporous material base adsorbent and its preparation method and application
CN111330534A (en) * 2020-03-11 2020-06-26 昆明理工大学 Mesoporous alumina-based adsorbent and preparation method and application thereof
CN113842744A (en) * 2021-09-06 2021-12-28 化学与精细化工广东省实验室 Adsorption purification recycling method for recovering insulating gas from perfluoroisobutyronitrile/carbon dioxide

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1887410A (en) * 2005-06-29 2007-01-03 财团法人工业技术研究院 Process and apparatus for treating gas containing fluoric compound
JP2007091560A (en) * 2005-09-30 2007-04-12 Tokuyama Corp Process for refining hydrogen chloride gas
CN205876105U (en) * 2016-07-08 2017-01-11 北京京铁金龙铁路消防工程有限公司 Fire -proof door
CN109865309A (en) * 2017-12-01 2019-06-11 中国科学院大连化学物理研究所 A kind of enrichment of volatile organic trace compounds low temperature and Thermal desorption integration cold-trap
CN109173990A (en) * 2018-09-17 2019-01-11 成都新柯力化工科技有限公司 A kind of composite mesoporous adsorbent material and preparation method for air cleaning
CN110433780A (en) * 2019-08-16 2019-11-12 昆明理工大学 A kind of mesoporous material base adsorbent and its preparation method and application
CN111330534A (en) * 2020-03-11 2020-06-26 昆明理工大学 Mesoporous alumina-based adsorbent and preparation method and application thereof
CN113842744A (en) * 2021-09-06 2021-12-28 化学与精细化工广东省实验室 Adsorption purification recycling method for recovering insulating gas from perfluoroisobutyronitrile/carbon dioxide

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
孙志明: "非金属矿物负载型光催化复合材料", 中国建材工业出版社, pages: 165 *
焦杨: "《潮湿细粒煤的团聚与解聚机制和气流分级研究》", 30 September 2019, 中国矿业大学出版社, pages: 143 *
赵奕奕: "《提高工业锅炉和蒸汽系统效率培训教材》", 31 December 2007, 中国计量出版社, pages: 41 *
项宇: "分子筛的发展及在空分设备中的应用", 深冷技术, no. 03, pages 20 - 23 *

Similar Documents

Publication Publication Date Title
CN101024140B (en) Method for purifying phosphor tail-gas
CN111569604A (en) Low-temperature flue gas adsorption desulfurization method
CN104445335B (en) It is a kind of to utilize the production anhydrous calcium chloride technique of waste hydrochloric acid containing organic matter and system
CN110559813B (en) Method for preparing mercury removal on line by using plasma to induce nano sulfur particles
CN104722183A (en) Treatment process for smoke gas produced by amino acid preparation process
Zawrah et al. Preparation and characterization of SiO2@ C nanocomposites from rice husk for removal of heavy metals from aqueous solution
CN114229852A (en) Method for removing SO in flue gas by using steel slag2Method for synergistically extracting silica gel
CN114832578A (en) Method for adsorbing hydrogen fluoride and hydrogen chloride by SBA-15 adsorbent
CN107115841A (en) Multistage pickling aftertreatment technology prepares ultralow ash content plant base charcoal
CN107261805B (en) Hydrazine solution special for chimney flue gas desulfurization and denitrification and preparation method thereof
CN106000073A (en) Environmental protection process for treating boiler flue gas
CN102886203B (en) A kind of method of flue gas desulfurizing and hydrargyrum-removing
CN102179234B (en) Production method of special active carbon for removing mercuric chloride
CN104258699B (en) The method of plasma and gas-solid or Gas-Liquid Dispersion system synergistic purification pollutant
CN105879569B (en) A kind of advanced purification process of coal-fired flue-gas
CN104874284B (en) A kind of alkalescence hydrate gel micro mist and preparation method and application
CN111346486A (en) Method and system for treating tail gas of oxygen-iodine chemical laser
JP3101181B2 (en) Exhaust gas treatment agent and exhaust gas treatment method
JP6587095B2 (en) Exhaust gas treatment method and treatment apparatus
CN112547047A (en) Method for preparing nano manganese dioxide catalyst by freeze drying method
CN212119535U (en) Oxygen iodine chemical laser tail gas treatment system
JPH1076138A (en) Treatment of waste gas containing halogen compound
TWI771842B (en) Demercuration catalyst, method of producing the same and application thereof
CN109967034A (en) Final treatment techniques prepare ultralow ash content solid waste base charcoal
CN215962920U (en) Biological absorption tower

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