CN1621498A - Method for preparing active semicoking H2S desulphurizer - Google Patents

Method for preparing active semicoking H2S desulphurizer Download PDF

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CN1621498A
CN1621498A CN 200410079366 CN200410079366A CN1621498A CN 1621498 A CN1621498 A CN 1621498A CN 200410079366 CN200410079366 CN 200410079366 CN 200410079366 A CN200410079366 A CN 200410079366A CN 1621498 A CN1621498 A CN 1621498A
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semicoke
solution
content
active
coke
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CN100443161C (en
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李春虎
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Ocean University of China
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Ocean University of China
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Abstract

The present invention discloses the preparation process of active semi-coke H2S desulfurizer. The active semi-coke H2S desulfurizer is prepared with lignite semi-coke, anthracite or soft coal semi-coke and other carbon containing material and through first pressurized hydrothermal chemical modification, subsequent soaking with cuprammonia, CuSO4 solution or K2CO3 solution, drying and high temperature calcining. The present invention has the features of wide material source, low cost, repeated use of the adsorbent product, final use in waste water treatment and as fuel and no secondary pollution. The present invention may be used widely in purifying gas in various plants and environment protecting industry.

Description

Active semicoke H2Preparation method of S desulfurizer
Technical Field
The invention relates to a method for preparing a gas purification desulfurizer in production plants such as petroleum, coal and natural gas production plants and environmental protection industries by using petroleum, coal and natural gas as raw materials, in particular to a method for preparing an active semicoke H2A preparation method of an S desulfurizer.
Background
The most of the plants for synthesizing ammonia, urea and bi-alcohol in China, which take three carbon-containing resources of petroleum, coal and natural gas as raw materials, wherein coal is about 70 percent of the raw materials. At present, due to the price rise of petroleum, some production plants such as coke-oven plants, gas plants and the like also consider synthesizing methanol and ammonia by taking coke-oven gas as a raw material; also, some large-scale fertilizer plants change the original high-cost production process of ' oil head ' and ' gas head ' gas-making fertilizer into ' coalHead ". Meanwhile, in order to save energy consumption, a low-pressure method is generally adopted to synthesize ammonia, methanol and the like at present, and the selected catalysts are all high-efficiency noble metal catalysts. Can be the sulfide (mainly H) contained in the synthesis gas prepared by using coal as raw material2S、COS、CS2Etc.) are easy to cause a series of serious consequences such as poisoning of the noble metal catalyst, great reduction of the service life of the catalyst and the like, so that the plant is frequently started and stopped, and the economic benefit is sharply reduced. Therefore, manufacturers are eagerly hoped to add a normal-temperature desulfurization process to reduce the total sulfur to below 0.5ppm so as to ensure that the service life of the synthetic ammonia and the bi-alcohol catalyst reaches more than one year.
Currently, the desulfurizing agents used at home and abroad are classified into iron-based desulfurizing agents, activated carbon desulfurizing agents, aluminum-based organic sulfur-based catalysts, zinc-based desulfurizing agents and molecular sieve-based desulfurizing agents according to systems. Wherein, the active carbon desulfurizer can be used for removing organic sulfur and inorganic sulfur; can be used for coarse desulfurization of high-concentration sulfur and fine desulfurization of low-concentration sulfur.
Activated carbon was used for industrial desulfurization in the last 30 th century, but it was recognized as an oxidative desulfurization agent in the 70 th century. Compared with other industrial desulfurizing agents, it has the advantages of convenient operation, large sulfur capacity and high desulfurizing efficiency, thus being widely applied, in particular to processing the desulfurizing agent containing low-concentration H2S gas.
Removal of H from activated carbon2Principle of S (M represents a divalent metal atom):
(1)
(2)
H2s and trace oxygen in the raw material gas generate S under the catalytic action of the fine activated carbon desulfurizer, and the S is deposited in gaps of the desulfurizer, or sulfate is generated according to the formula (2).
The activated carbon method can be classified into an adsorption method, an oxidation method, and a catalytic method according to a desulfurization mechanism.
The adsorption method is most effective in removing thiophene by utilizing the characteristic of selective adsorption of activated carbon, but the use is limited because the sulfur capacity is too small.
The catalytic method is to impregnate heavy metals such as copper and iron in the active carbon, so that organic sulfur is catalytically converted into hydrogen sulfide, and the hydrogen sulfide is absorbed by the active carbon.
Oxidation activated carbon desulfurization is one of the most commonly used processes, with the aid of ammonia catalysis, H2S and COS are oxidized by oxygen in the gas.
Currently, the activated carbon desulfurizer developed and applied in China mainly comprises RS-1, RS-2, EAC-4, T101 (original EAC-1), T102 (original EAC-2) and T103 (original EAC-3) type desulfurizers. They are made up by using coal-base active carbon as carrier, impregnating soluble salt of active metal, activating agent and accelerating agent, drying, roasting and activating. In recent years, the use of these desulfurization agents has been limited due to the rapid rise in the price of coal-based activated carbon; on the other hand, the treatment of the waste activated carbon desulfurization agent is also an important problem.
Disclosure of Invention
Aiming at the defects of the activated carbon desulfurizer, the invention aims to provide the activated semicoke H which is high in efficiency and low in cost2A preparation method of an S desulfurizer.
Active semicoke H2The S desulfurizing agent is prepared with brown coal semi-coke, anthracite, bituminous coal semi-coke and other carbon containing material as material and through pressurized water thermochemical modification, soaking in active solution in the same volume, drying and high temperature calcination.
Wherein the active solution is copper ammonia complex solution and CuSO4Solutions or K2CO3And (3) solution.
Wherein the carbon-containing materials such as lignite semicoke or anthracite, bituminous coal semicoke and the like are characterized by the bulk density of 0.5-0.7g/ml and the specific surface area of 10-200m2The carbon content is 70-85%,the hydrogen content is 0.5-2.5%, the oxygen content is 10-30%, the nitrogen content is 0.3-1.2%, the moisture content is 2-9%, the ash content is 3-15%, and the volatile content is 6-18%.
The preparation process is as follows: screening the semicoke meeting the physicochemical conditions to obtain 4-10 mesh particles, mixing the semicoke particles and water according to the volume ratio of 1: 0.6-1.2, adding the mixture into a high-pressure reaction kettle, reacting for 1-8h at the temperature of 150 plus materials at 270 ℃ and under the pressure of 6-43atm, naturally cooling, taking out, drying the semicoke for 2h at the temperature of 100 plus materials at 120 ℃, and then using copper ammonia complex liquid and CuSO at the temperature of normal temperature-60 ℃ to obtain the semicoke with the particle size of 4-10 mesh4Solution, K2CO3Soaking the solution in the same volume,the content of the metal oxide accounts for 0.5 to 10 percent of the total weight of the semicoke, the semicoke is placed for 24 hours, and then the semicoke is heated at the temperature of 400 ℃ and 700 ℃ at the space velocity of 50 to 5000 hours-1Lower N2Roasting in the atmosphere for 1-8h and activating.
The activity and sulfur capacity test of the desulfurizer are carried out in a fixed bed glass reactor, the inner diameter of the reactor is 20 mm, the desulfurizer is 4-8 meshes, the filling volume of the desulfurizer is 25ml, the bed height of the reactor is 100mm, and H is removed2The temperature of S is normal temperature to 60 ℃, and the space velocity is 800-1500h-1The grain/pipe diameter ratio is 0.1-0.13, and the sulfur-containing gas consists of H2S1000ppm、H2O5% and the balance of N2And (4) balancing. Sulfur capacity is outlet H2The S concentration of 0.01ppm is the cumulative sulfur capacity calculated by penetration.
The invention is characterized in that the carbon-based materials such as active semicoke and the like have wide sources and low price, and the prepared adsorbent can be repeatedly regenerated and recycled, and can be finally used for wastewater treatment or boiler fuel without secondary pollution. Can be widely used for gas purification in production plants such as synthetic ammonia, urea, methanol, coking plants, gas plants and the like which take petroleum, coal and natural gas as raw materials and in the environmental protection industry. As is well known, the last century is a silicon material century, and the century is probably a carbon material century, so that the invention has wide application prospect.
Detailed Description
The present invention is described in detail below with reference to specific examples.
Examples 1 to 5:
mixing 4-10 mesh particles obtained by screening bituminous coal semicoke with water according to the volume ratio of 1: 0.83, adding the mixture into a high-pressure reaction kettle, reacting for 4 hours at the temperature of 150 ℃ and the pressure of 270 ℃ under the pressure of 8atm, 10atm, 12atm, 14atm and 43atm respectively, taking out after natural cooling, measuring the specific surface area and the pore volume of the mixture, filling 30ml of the mixture into a fixed bed reactor, measuring the desulfurization activity of the mixture, wherein the inner diameter of the reactor is 20 mm, and the bed height of the reactor is 100 mm. The results are shown in Table 1.
TABLE 1 active semicoke H after thermochemical modification of water at different pressures2Specific surface area and pore volume of S desulfurizer
And influence on the sulfur capacity
Sample raw material semicoke 8atm, 10atm, 12atm, 14atm and 43atm
Specific surface area m2/g 49.19 1115.84 610.35 414.74 510.63 482.64
Pore volume ml/g 0.03510.45930.34120.13100.24700.3214
Sulfur capacity gH2S/100gC 3.11 3.63 6.54 8.14 9.17 12.45
And (3) testing conditions are as follows: temperature: 40 ℃; space velocity: 1200h-1;H2The concentration of S: 1000 ppm; h2O(g):5%。
Thus, the sulfur capacity of the semicoke is obviously improved after the pressurized water thermochemical modification.
Examples 6 to 10:
the modified semicoke obtained by the preparation method of the embodiment 1-5 is soaked in copper-ammonia complex liquid with the same volume at normal temperature, so that the CuO accounts for 8.0 percent of the total weight of the semicoke, the semicoke is placed for 24 hours, and then the temperature is 700 ℃ and the space velocity is 1000 hours-1Lower N2And (5) roasting in the atmosphere for 6h for activation. The desulfurization activity was then measured (method 1). The results are shown in Table 2.
TABLE 2 thermochemical modification of semicoke by pressurized water, isovolumetric immersion modification of copper ammonia complex solution and N at 700 deg.C2
Change in sulfur capacity after activation
Sample raw material semicoke 8atm, 10atm, 12atm, 14atm and 43atm
Penetration time h 1.511.5141515.515.9
Sulfur capacity gSO2/100gC 3.11 8.20 9.4612.78 14.50 16.84
And (3) testing conditions are as follows: temperature: 40 ℃; space velocity: 1200h-1;H2The concentration of S: 1000 ppm; h2O(g):5%。
Visible semicoke subjected to pressurized water thermochemical modification is subjected to isovolumetric impregnation modification by copper-ammonia complex solution and subjected to 700 ℃ N2After activation, the sulfur capacity can be increased by about 3 times.
Examples 11 to 13:
active semicoke H obtained by the preparation method described in example 72S desulfurization agent (the agent was prepared at 40 atm.) desulfurization/regeneration experiments were performed using two columns in series, and the results are shown in Table 3.
TABLE 3 active semicoke H2Relationship between S desulfurizer regeneration frequency and sulfur capacity
Sample twice three times
Sulfur capacity (gS/100Gc) 12.3011.8212.23
Regeneration conditions are as follows: at normal temperature at an airspeed of 50h-1Air was passed through the tube for 40 hours.
It can be seen that after 3 times of desulfurization regeneration, the desulfurization activity is not significantly reduced. Illustrating the active semicoke H2The S desulfurizer has great desulfurization potential.

Claims (5)

1. Active semicoke H2A process for preparing S-desulfurizing agent features that the raw materials of semi-coke of lignite, anthracite or bituminous coal are thermochemically modified by pressurized waterAnd then soaking the active solution in the same volume, drying and calcining at high temperature to obtain the catalyst.
2. The method according to claim 1, wherein the active solution is a copper ammine complex solution or CuSO4Solutions or K2CO3And (3) solution.
3. The desulfurizing agent preparation method according to claim 1, wherein the lignite semicoke or anthracite, bituminous coal semicoke has a bulk density of 0.5-0.7g/ml and a specific surface area of 10-200m2The carbon content is 70-85%, the hydrogen content is 0.5-2.5%, the oxygen content is 10-30%, the nitrogen content is 0.3-1.2%, the moisture content is 2-9%, the ash content is 3-15%, and the volatile content is 6-18%.
4. The method for preparing desulfurizing agent according to claim 1, wherein the pressurized water thermochemical modification is carried out by mixing semicoke and water, adding into a high-pressure reactor, and reacting at 150-270 ℃ and 6-43atm for 1-8 h.
5. The method for preparing desulfurizer as claimed in claim 1, wherein the semicoke is sieved to obtain 4-10 mesh particles, the semicoke particles and water are mixed according to the volume ratio of 1: 0.6-1.2, and then added into a high-pressure reaction kettle to react for 1-8h at 150-4Solution, K2CO3Soaking in equal volume of solution to make CuO and K2The amount of O accounts for 0.5-10% of the total weight of the semicoke, the semicoke is placed for 24 hours, and then the space velocity is 50-5000 hours at the temperature of 500--1N2Roasting in the atmosphere for 1-8h for activation.
CNB2004100793669A 2004-10-16 2004-10-16 Method for preparing active semicoking H2S desulphurizer Expired - Fee Related CN100443161C (en)

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Cited By (13)

* Cited by examiner, † Cited by third party
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CN101718766A (en) * 2008-10-09 2010-06-02 北京三聚环保新材料股份有限公司 Device for measuring breakthrough sulphur capacity and using method thereof
CN101791519A (en) * 2010-04-08 2010-08-04 周琪 Application process for treating acid gas containing H2S by active carbocoal method
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
CN102225328A (en) * 2011-04-02 2011-10-26 山东科技大学 Silver-loaded lignite semi-coke used for absorbing elemental mercury from coal-fired flue gas and preparation method thereof
CN102240566A (en) * 2011-05-12 2011-11-16 太原理工大学 Preparation method of catalyst for preparing synthesis gas by reforming CH4/CO2
CN104437366A (en) * 2014-11-13 2015-03-25 安徽凤凰滤清器股份有限公司 Uneasily-disintegrated mixed active carbon desulfurizing agent and preparation method thereof
CN104891487A (en) * 2015-04-30 2015-09-09 山东大学 Method for rapidly preparing powdery active coke
CN106268741A (en) * 2016-07-21 2017-01-04 常熟理工学院 A kind of desulfurization catalyst of flue gas
CN107539986A (en) * 2016-06-27 2018-01-05 中国石油化工股份有限公司 A kind of activated coke and preparation method thereof
CN107552032A (en) * 2017-10-26 2018-01-09 华北理工大学 Semicoke loads TiO2Sintering smoke denitrifier and its solvothermal preparation method
CN110465265A (en) * 2018-05-11 2019-11-19 萍乡市华星环保工程技术有限公司 Organic waste-gas adsorbant and preparation method thereof
CN112705163A (en) * 2020-12-22 2021-04-27 长沙工研院环保有限公司 Multi-metal in-situ doped desulfurizer based on low-coalification-degree inferior coal and preparation method thereof
CN115520863A (en) * 2022-11-04 2022-12-27 合肥工业大学 Coal-based activated carbon prepared by hydrothermal or solvothermal method and preparation method and application thereof

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CN1089034C (en) * 1999-04-30 2002-08-14 中国科学院山西煤炭化学研究所 Desulfurization catalyst of flue gas and its application method

Cited By (18)

* Cited by examiner, † Cited by third party
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CN101718766A (en) * 2008-10-09 2010-06-02 北京三聚环保新材料股份有限公司 Device for measuring breakthrough sulphur capacity and using method thereof
CN101791519A (en) * 2010-04-08 2010-08-04 周琪 Application process for treating acid gas containing H2S by active carbocoal method
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
CN101884906B (en) * 2010-07-06 2012-05-23 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
CN102225328A (en) * 2011-04-02 2011-10-26 山东科技大学 Silver-loaded lignite semi-coke used for absorbing elemental mercury from coal-fired flue gas and preparation method thereof
CN102225328B (en) * 2011-04-02 2012-11-21 山东科技大学 Silver-loaded lignite semi-coke used for absorbing elemental mercury from coal-fired flue gas and preparation method thereof
CN102240566A (en) * 2011-05-12 2011-11-16 太原理工大学 Preparation method of catalyst for preparing synthesis gas by reforming CH4/CO2
CN102240566B (en) * 2011-05-12 2013-02-20 太原理工大学 Preparation method of catalyst for preparing synthesis gas by reforming CH4/CO2
CN104437366A (en) * 2014-11-13 2015-03-25 安徽凤凰滤清器股份有限公司 Uneasily-disintegrated mixed active carbon desulfurizing agent and preparation method thereof
CN104891487A (en) * 2015-04-30 2015-09-09 山东大学 Method for rapidly preparing powdery active coke
CN107539986A (en) * 2016-06-27 2018-01-05 中国石油化工股份有限公司 A kind of activated coke and preparation method thereof
CN106268741A (en) * 2016-07-21 2017-01-04 常熟理工学院 A kind of desulfurization catalyst of flue gas
CN107552032A (en) * 2017-10-26 2018-01-09 华北理工大学 Semicoke loads TiO2Sintering smoke denitrifier and its solvothermal preparation method
CN107552032B (en) * 2017-10-26 2020-06-16 华北理工大学 Semicoke-supported TiO2Sintering flue gas denitration agent and solvothermal preparation method thereof
CN110465265A (en) * 2018-05-11 2019-11-19 萍乡市华星环保工程技术有限公司 Organic waste-gas adsorbant and preparation method thereof
CN112705163A (en) * 2020-12-22 2021-04-27 长沙工研院环保有限公司 Multi-metal in-situ doped desulfurizer based on low-coalification-degree inferior coal and preparation method thereof
CN115520863A (en) * 2022-11-04 2022-12-27 合肥工业大学 Coal-based activated carbon prepared by hydrothermal or solvothermal method and preparation method and application thereof
CN115520863B (en) * 2022-11-04 2023-11-21 合肥工业大学 Coal-based activated carbon prepared by hydrothermal or solvothermal method and preparation method and application thereof

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