CN110639473A - Modified activated carbon adsorbent for adsorbing NOx at high temperature and preparation method thereof - Google Patents
Modified activated carbon adsorbent for adsorbing NOx at high temperature and preparation method thereof Download PDFInfo
- Publication number
- CN110639473A CN110639473A CN201911003202.0A CN201911003202A CN110639473A CN 110639473 A CN110639473 A CN 110639473A CN 201911003202 A CN201911003202 A CN 201911003202A CN 110639473 A CN110639473 A CN 110639473A
- Authority
- CN
- China
- Prior art keywords
- activated carbon
- adsorbent
- raw materials
- preparation
- high temperature
- 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
Links
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/02—Separation 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/40—Nitrogen compounds
- B01D2257/404—Nitrogen oxides other than dinitrogen oxide
Abstract
Used for adsorbing NO at high temperaturexThe invention relates to a modified activated carbon adsorbent and a preparation method thereof, belonging to the technical field of adsorbents, and the modified activated carbon adsorbent is characterized by being prepared from the following raw materials in parts by weight: 15-25 parts of raw material active carbon, 4-5 parts of potassium carbonate, 0.2-1 part of potassium silicate and 45-60 parts of water. Impregnation is carried out first and then calcination is carried out. The invention has simple process and low cost, and can treat NO at normal temperature to 120 DEG CxHas good adsorption effect, and the adsorbent is nontoxic, harmless and easy to regenerate.
Description
Technical Field
The invention relates to a method for adsorbing NO at high temperaturexThe preparation method of the modified activated carbon adsorbent. Belongs to the technical field of adsorbents.
Background
At present, the weather of haze is frequent, the environmental problem is increasingly prominent, and NO isxIs one of the main pollutants in the atmosphere, and NO is strengthened in various countriesxThe treatment strength of (2). The current adsorption method is to treat NOxAs long as it isThe method has the advantages of simple process and low cost. But when the temperature of the flue gas is higher, the active carbon NOxThe adsorption capacity is poor, the improvement of the adsorption capacity of the activated carbon becomes a current research focus, and a scholars can improve the pore structure of the activated carbon to achieve the effects of hole expansion and capacity increase by treating the activated carbon with an oxidant; the researchers also improve the adsorption capacity of the activated carbon by treating the activated carbon with alkali liquor containing potassium or sodium and metal salt solution, improving the types and the number of surface functional groups, introducing metal cations and the like.
CN101480603A discloses a preparation method of a nitrogen oxide adsorbent, which prepares modified activated carbon by combining surface oxidation modification, solution impregnation and metal loading, the activated carbon has excellent adsorption effect under normal temperature and pressure, and has good SO adsorption effect2The VOC has better adsorption effect; CN101879435A discloses a method for preparing a high-adsorption-capacity normal-temperature nitrogen oxide adsorbent, which comprises the steps of pre-oxidizing activated carbon by an oxidizing solution, drying, roasting, soaking by a metal salt solution twice, drying and roasting to obtain the adsorbent suitable for adsorbing NO at normal temperaturexThe adsorbent is NO at 25 DEG CxThe adsorption capacity can reach 80 mg/g; CN101884906A discloses a method for preparing modified activated carbon by using metal oxide and urea through impregnation modification, wherein NO is contained in the activated carbon under the conditions of normal temperature and normal pressurexThe removal effect of (2) is excellent.
In the existing preparation methods of modified activated carbon, some methods need washing after the activated carbon is soaked, a large amount of waste water is generated, and the subsequent treatment process is complex; some methods need harmful modification reagents, thus threatening human health; some methods require multiple times of dipping treatment, so that the production steps are complicated and large-scale production is difficult to realize. The evaluation conditions are single, and SO is not considered2、CO2Influence of water vapor on adsorption performance of the activated carbon; the adsorption performance of the activated carbon was evaluated only under normal temperature and pressure conditions, and the adsorption performance under high temperature conditions was not evaluated. The invention develops a modified activated carbon adsorbent suitable for high temperature conditions aiming at the limit of the scale production and application of the modified activated carbon, and the modified activated carbon adsorbent is prepared at 120℃ and containsWith SO2、CO2Under the condition of water vapor, NO thereofxThe adsorption capacity can reach more than 0.3mmol/g, the adsorption capacity is improved by 40-55 times compared with the original adsorption capacity, the production process of the adsorbent is simple, and the used modification reagent is non-toxic and harmless and is suitable for large-scale production.
Disclosure of Invention
The invention aims to provide a method for adsorbing NO at high temperaturexThe preparation method of the modified activated carbon adsorbent; the adsorbent has the advantages of large adsorption capacity, simple preparation method, no toxicity and harmlessness of the modifying reagent, and suitability for large-scale production.
The technical scheme of the invention is as follows:
used for adsorbing NO at high temperaturexThe modified activated carbon adsorbent and the preparation method thereof are characterized by being prepared from the following raw materials in parts by weight: raw materials of activated carbon, potassium carbonate, potassium silicate and water, wherein the raw materials of the activated carbon are 15-25%, the potassium carbonate is 4-5%, the potassium silicate is 0.2-1%, and the water is preferably 45-60%.
Used for adsorbing NO at high temperaturexThe preparation method of the modified activated carbon adsorbent comprises the following steps:
(1) weighing raw materials according to the composition of raw materials of the adsorbent, wherein the activated carbon is coal-based activated carbon, fruit-wood-based activated carbon and the like, and the ash content of the activated carbon is 5-13%;
(2) dissolving potassium carbonate in partial water to prepare a solution, adding the prepared potassium silicate aqueous solution, and ultrasonically stirring uniformly for later use;
(3) slowly pouring the prepared solution in the step (2) into active carbon, and continuously shaking until the solution just passes through the active carbon; then stirring once every 10-15 min for 4-6 times, and performing ultrasonic treatment for 2-5 min after each stirring is finished;
(4) soaking activated carbon for 6-12 h, uniformly stirring the activated carbon, discharging residual liquid in the activated carbon, performing microwave treatment on the activated carbon for 2-8 min by using a microwave reactor, and finally continuously drying in an oven;
(5) and (3) placing the dried activated carbon in a tubular furnace, heating to 550-650 ℃ at a heating rate of 3-5 ℃/min under the atmosphere of one or the combination of inert gases such as nitrogen, helium, argon and the like, and roasting for 2h under the temperature condition, wherein the preferred temperature is 600 ℃. And cooling the activated carbon to room temperature, and drying and storing.
The activated carbon adsorbent is used for adsorbing NO at high temperaturexFor example, nitrogen oxide NO is adsorbed under the high temperature condition of 100-120 DEG Cx。
The invention has the following advantages:
(1) has excellent adsorption performance at normal temperature to 120 ℃, and has stronger CO resistance2And the water-mixing capacity is improved by 40-55 times compared with the original capacity when the efficiency reaches 50% at the high temperature of 120 ℃.
(2) No toxicity and harm, and no secondary pollution in the preparation process.
(3) The preparation process is simple, the cost is low, and the method is suitable for large-scale production.
Drawings
FIG. 1 shows NO at 120 deg.C before and after modification with activated carbon (1#, 2#)xAdsorption rate change curve.
FIG. 2 shows NO of modified activated carbon (3#) at 100 deg.CxAdsorption rate change curve.
Detailed Description
The present invention will be further illustrated with reference to the following examples, but the present invention is not limited to the following examples.
Example 1:
weighing 5 parts of potassium carbonate in a beaker, adding 50 parts of deionized water, stirring for dissolving, adding 0.5 part of potassium silicate to prepare a solution, uniformly stirring by ultrasound for later use, taking 30 parts of proper coal-based activated carbon (the ash content of the coal-based activated carbon is 12.5%, the same applies below) in a conical flask, adding the prepared solution to just immerse the activated carbon, shaking, stirring once every 10min, stirring for 6 times totally, and performing ultrasound for 4min after each stirring is finished; soaking activated carbon overnight, removing residual liquid, then placing the activated carbon in a microwave reactor for treatment for a certain time, and finally placing the activated carbon in a 110 ℃ oven for complete drying; after the active carbon is dried, the active carbon is placed in a tube furnace, and the reaction is carried out in N2Roasting at 600 deg.C for 2h under atmosphere, cooling to room temperature, and drying and storing the activated carbon adsorbent. The modified activated carbon is marked as No. 2,unmodified activated carbon is noted as 1 #.
Example 2:
weighing 4.5 parts of potassium carbonate into a beaker, adding 50 parts of deionized water, stirring for dissolving, adding 0.95 part of potassium silicate to prepare a solution, uniformly stirring by ultrasound for later use, adding 25 parts of coal-based activated carbon (the ash content of the coal-based activated carbon is 12.5 percent, the same applies below) into a conical flask, adding the prepared solution to just immerse the activated carbon, shaking, stirring once every 10min, stirring for 6 times totally, and performing ultrasound for 5min after each stirring; soaking activated carbon overnight, removing residual liquid, then placing the activated carbon in a microwave reactor for treatment for a certain time, and finally placing the activated carbon in a 110 ℃ oven for complete drying; after the active carbon is dried, the active carbon is placed in a tube furnace, and the reaction is carried out in N2Roasting at 600 deg.C for 2h under atmosphere, cooling to room temperature, and drying and storing the activated carbon adsorbent. The modified activated carbon is marked as # 3.
Test example 1:
the testing device is shown in fig. 1, and comprises the following specific steps: the gas is distributed by using the gas in the steel cylinder, the concentration of NO is controlled to be about 200ppm, and SO is controlled2Concentration of about 25ppm, CO2About 4.5% of O2The content is about 15 percent, the water vapor content is 1.5 percent, the gas flow is 1.7L/min, the gas velocity in the adsorption column is 0.1m/s, the temperature of an adsorbent bed layer is 120 ℃, the dosage of an adsorbent is 15g, the thickness of the bed layer is about 10cm, and a flue gas analyzer is used for continuously monitoring NO at an outletxConcentration until the outlet NO concentration reaches 50% of the inlet concentration. The modified active carbon NO can be obtained by calculationxThe adsorption capacity of the adsorbent # (2#) to NO can reach more than 0.335mmol/g, which is 55.8 times higher than that of the activated carbon sample # (1 #).
Test example 2:
the testing device is shown in fig. 1, and comprises the following specific steps: the gas is distributed by using the gas in the steel cylinder, the concentration of NO is controlled to be about 200ppm, and SO is controlled2Concentration of about 25ppm, CO2About 4.5% of O2The content is about 15 percent, the water vapor content is 1.5 percent, the gas flow is 1.7L/min, the gas velocity in the adsorption column is 0.1m/s, the temperature of an adsorbent bed layer is 100 ℃, the dosage of an adsorbent is 15g, the thickness of the bed layer is about 10cm, and a flue gas analyzer is used for continuously monitoring NO at an outletxIn a concentration ofThe outlet NO concentration reached 50% of the inlet concentration. The modified active carbon NO can be obtained by calculationx Adsorbent # 3 to NOxThe adsorption capacity of the adsorbent can reach more than 0.307 mmol/g.
TABLE 1 NO before and after modification of activated carbon under different temperature conditionsxComparison of adsorption amount
Claims (4)
1. Used for adsorbing NO at high temperaturexThe preparation method of the modified activated carbon adsorbent is characterized by being prepared from the following raw materials in parts by weight: raw materials of activated carbon, potassium carbonate, potassium silicate and water, wherein the raw materials of the activated carbon are 15-25%, the potassium carbonate is 4-5%, the potassium silicate is 0.2-1%, and the water is preferably 45-60%;
the preparation method comprises the following steps:
(1) weighing raw materials according to the composition of raw materials of the adsorbent, wherein the activated carbon is coal-based activated carbon, fruit-wood-based activated carbon and the like, and the ash content of the activated carbon is 5-13%;
(2) dissolving potassium carbonate in partial water to prepare a solution, adding the prepared potassium silicate aqueous solution, and ultrasonically stirring uniformly for later use;
(3) slowly pouring the prepared solution in the step (2) into active carbon, and continuously shaking until the solution just passes through the active carbon; then stirring once every 10-15 min for 4-6 times, and performing ultrasonic treatment for 2-5 min after each stirring is finished;
(4) soaking activated carbon for 6-12 h, uniformly stirring the activated carbon, discharging residual liquid in the activated carbon, performing microwave treatment on the activated carbon for 2-8 min by using a microwave reactor, and finally continuously drying in an oven;
(5) and (3) placing the dried activated carbon in a tubular furnace, heating to 550-650 ℃ at a heating rate of 3-5 ℃/min under the atmosphere of one or a combination of inert gases such as nitrogen, helium, argon and the like, roasting for 2h under the temperature condition, cooling the activated carbon to room temperature, and drying and storing.
2. The method of claim 1, wherein the temperature of the calcination in step (5) is 600 ℃.
3. The modified activated carbon adsorbent prepared according to the method of claim 1 or 2.
4. Use of the modified activated carbon adsorbent prepared according to the method of claim 1 or 2 for high temperature adsorption of NOxAdsorbing nitrogen oxide NO at 100-120 deg.cx。
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201911003202.0A CN110639473A (en) | 2019-10-22 | 2019-10-22 | Modified activated carbon adsorbent for adsorbing NOx at high temperature and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201911003202.0A CN110639473A (en) | 2019-10-22 | 2019-10-22 | Modified activated carbon adsorbent for adsorbing NOx at high temperature and preparation method thereof |
Publications (1)
Publication Number | Publication Date |
---|---|
CN110639473A true CN110639473A (en) | 2020-01-03 |
Family
ID=68994460
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201911003202.0A Pending CN110639473A (en) | 2019-10-22 | 2019-10-22 | Modified activated carbon adsorbent for adsorbing NOx at high temperature and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN110639473A (en) |
Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1242252A (en) * | 1999-06-18 | 2000-01-26 | 化学工业部西南化工研究设计院 | Removing and recovering nitrogen oxide(s) by adsorption separation method from mixed gas contg. nitrogen oxide(s) |
US6652821B1 (en) * | 1999-02-18 | 2003-11-25 | Yasuo Fukutani | Purificating agent for flue gas and incinerated ash and purificating method using the same |
CN101693162A (en) * | 2009-10-10 | 2010-04-14 | 华北电力大学(保定) | Method for desulfurizing and denitrating boiler gas simultaneously by using active carbon under microwave radiation |
CN101879435A (en) * | 2010-06-08 | 2010-11-10 | 华东理工大学 | High-adsorption-capacity room-temperature nitrogen oxide adsorbent and preparation method thereof |
CN101884906A (en) * | 2010-07-06 | 2010-11-17 | 上海纳米技术及应用国家工程研究中心有限公司 | Modified honeycomb activated carbon with nitric oxide adsorption function and preparation method thereof |
CN105170139A (en) * | 2015-09-17 | 2015-12-23 | 海南大学 | Denitration catalyst, preparation method and application thereof |
CN106031861A (en) * | 2015-03-19 | 2016-10-19 | 上海融熠投资管理有限公司 | Composite adsorbent |
CN108283920A (en) * | 2017-01-09 | 2018-07-17 | 青州日新特种材料有限公司 | A kind of de- NOx catalyst and preparation method thereof |
-
2019
- 2019-10-22 CN CN201911003202.0A patent/CN110639473A/en active Pending
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6652821B1 (en) * | 1999-02-18 | 2003-11-25 | Yasuo Fukutani | Purificating agent for flue gas and incinerated ash and purificating method using the same |
CN1242252A (en) * | 1999-06-18 | 2000-01-26 | 化学工业部西南化工研究设计院 | Removing and recovering nitrogen oxide(s) by adsorption separation method from mixed gas contg. nitrogen oxide(s) |
CN101693162A (en) * | 2009-10-10 | 2010-04-14 | 华北电力大学(保定) | Method for desulfurizing and denitrating boiler gas simultaneously by using active carbon under microwave radiation |
CN101879435A (en) * | 2010-06-08 | 2010-11-10 | 华东理工大学 | High-adsorption-capacity room-temperature nitrogen oxide adsorbent and preparation method thereof |
CN101884906A (en) * | 2010-07-06 | 2010-11-17 | 上海纳米技术及应用国家工程研究中心有限公司 | Modified honeycomb activated carbon with nitric oxide adsorption function and preparation method thereof |
CN106031861A (en) * | 2015-03-19 | 2016-10-19 | 上海融熠投资管理有限公司 | Composite adsorbent |
CN105170139A (en) * | 2015-09-17 | 2015-12-23 | 海南大学 | Denitration catalyst, preparation method and application thereof |
CN108283920A (en) * | 2017-01-09 | 2018-07-17 | 青州日新特种材料有限公司 | A kind of de- NOx catalyst and preparation method thereof |
Non-Patent Citations (5)
Title |
---|
周安宁等: "《洁净煤技术》", 28 February 2018 * |
姚刚: "烟气脱硝活性炭的研究进展", 《化工时刊》 * |
杨代军: "NO adsorption and temperature programmed desorption on K2CO3 modified activated carbons", 《JOURNAL OF CENTRAL SOUTH UNIVERSITY》 * |
蔡建宇: "改性活性炭吸附烧结烟气中氮氧化物的研究", 《钢铁钒钛》 * |
马双忱: "微波改性活性炭用于烟气脱硫脱硝的实验研究", 《燃料化学学报》 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Yang et al. | Experimental and kinetic study on Hg0 removal by microwave/hydrogen peroxide modified seaweed-based porous biochars | |
CN106076380A (en) | The preparation method of modified coal activated carbon base catalyst | |
CN105921139B (en) | A kind of mercury absorbent and its preparation method and application | |
CN111229208B (en) | Lotus leaf-source biochar-loaded metal oxide low-temperature SCR (selective catalytic reduction) flue gas denitration catalyst and preparation method and application thereof | |
CN114259978B (en) | Preparation process of efficient coal-fired flue gas mercury removal adsorbent and product thereof | |
WO2018121003A1 (en) | Manufacturing method using low temperature nox removal and popcorn as precursor for heteropoly acid carbon composite | |
CN107008323B (en) | A kind of activated-carbon catalyst preparation method for flue gas desulfurization and denitrification | |
CN104841441B (en) | The method for preparing catalyst of hydrolysis oxidation coupled method purification HCN a kind of and application | |
CN107684916A (en) | A kind of integer catalyzer for being used for low temperature removal formaldehyde using carbide wood as carrier and preparation method thereof | |
CN110227428A (en) | The activating and regenerating treatment process of industrial smoke dry desulfurization semicoke | |
CN113101898A (en) | Porous granular molecular sieve VOCs adsorbent and preparation method thereof | |
CN106179218A (en) | A kind of sintering flue gas desulfurization agent with active carbocoal as carrier and preparation, renovation process and application | |
CN113769534B (en) | Activated carbon modification method for removing nitric oxide and nitrogen dioxide gas in air | |
CN110605108A (en) | Method for regenerating desulfurization and denitrification waste active carbon | |
KR100746704B1 (en) | Manufacture of reacting media with carbon support impregrated metal catalyst and removing of nox using its media | |
CN113231014A (en) | Hydrophobic biomass polydopamine composite activated carbon and preparation method thereof | |
CN110639473A (en) | Modified activated carbon adsorbent for adsorbing NOx at high temperature and preparation method thereof | |
CN108722352B (en) | Macroporous carbon-based material for adsorbing environmental carbon monoxide and preparation method thereof | |
CN100336588C (en) | Process for regenerating sulfur loading active carbon | |
CN110013888B (en) | Method for regenerating bifunctional catalyst | |
CN113499753A (en) | Preparation and regeneration method of renewable demercuration adsorbent | |
CN112387247B (en) | Modified fly ash adsorbent and preparation method thereof, and trimethylamine adsorption method | |
CN112642495A (en) | Realize low SO2Catalyst regeneration and modification method for conversion rate and high zero-valent mercury oxidation performance | |
CN113976078A (en) | Sisal fiber-based biomass activated carbon and preparation method and application thereof | |
CN107961673A (en) | Organic waste gas treatment device |
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 |