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CN110523366A - A molding method suitable for carbon capture sodium-based adsorbent - Google Patents

A molding method suitable for carbon capture sodium-based adsorbent Download PDF

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CN110523366A
CN110523366A CN201910601612.9A CN201910601612A CN110523366A CN 110523366 A CN110523366 A CN 110523366A CN 201910601612 A CN201910601612 A CN 201910601612A CN 110523366 A CN110523366 A CN 110523366A
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adsorbent
carbon capture
forming method
sodium
crushed
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吴烨
刘威
张权
冯鸣谦
王伟
刘冬
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Nanjing Tech University
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    • 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
    • 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
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • 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
    • B01J20/08Solid 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 comprising aluminium oxide or hydroxide; comprising bauxite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/50Carbon oxides
    • B01D2257/504Carbon dioxide
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/40Capture or disposal of greenhouse gases of CO2

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  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
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  • Engineering & Computer Science (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

本发明公开了一种适应于碳捕集钠基吸附剂的成型方法,该方法为将钠基吸附剂经浸渍、干燥、煅烧、破碎后得到吸附剂颗粒,再将颗粒状的吸附剂颗粒置于流化床中流化成型,筛分得到所需要的吸附剂粒径;收集流化床扬析的细粉再次破碎至粉末后,与水混合搅拌、干燥、煅烧、破碎后,再次置于流化床中,循环使用。本发明的成型方法相比现有的钠基吸附剂成型工艺,该方法简单便捷,生产效率高。

The invention discloses a molding method suitable for carbon-capturing sodium-based adsorbents. The method comprises the steps of impregnating, drying, calcining and crushing the sodium-based adsorbents to obtain adsorbent particles, and then placing the granular adsorbent particles in It is fluidized and formed in a fluidized bed, and sieved to obtain the required particle size of the adsorbent; the fine powder collected in the fluidized bed is crushed again to a powder, mixed with water, dried, calcined, crushed, and then placed in the fluidized bed again. In the chemical bed, it can be recycled. Compared with the existing sodium-based adsorbent forming process, the forming method of the present invention is simple and convenient, and has high production efficiency.

Description

一种适用于碳捕集钠基吸附剂的成型方法A molding method suitable for carbon capture sodium-based adsorbent

技术领域technical field

本发明涉及一种适用于碳捕集钠基吸附剂的成型方法,属于二氧化碳减排领域。The invention relates to a molding method suitable for a carbon-capturing sodium-based adsorbent, which belongs to the field of carbon dioxide emission reduction.

背景技术Background technique

随着工业化的不断发展,化石能源的过度开发利用引起了日趋严重的环境问题。由温室效应引起的温度升高等环境问题,愈发引起人们的重视。其中,由化石燃料燃烧导致空气中二氧化碳(CO2)含量的升高是温室效应的重要因素。燃煤电厂作为最大、最集中的固定单点排放源,发展适用于燃煤电厂的碳捕集技术对于缓解温室效应具有十分重要的意义。With the continuous development of industrialization, the excessive development and utilization of fossil energy has caused increasingly serious environmental problems. Environmental issues such as temperature rise caused by the greenhouse effect have attracted more and more attention. Among them, the increase of carbon dioxide (CO 2 ) content in the air caused by the combustion of fossil fuels is an important factor of the greenhouse effect. Coal-fired power plants are the largest and most concentrated fixed single-point emission sources, and the development of carbon capture technologies suitable for coal-fired power plants is of great significance for mitigating the greenhouse effect.

在针对电厂的各种CO2减排技术中,碱金属基吸附剂脱碳技术,由于其循环利用率高、再生能耗低、对设备腐蚀小、无二次污染等优势被认为是极具发展前景的碳捕集技术之一。Among the various CO2 emission reduction technologies for power plants, alkali metal-based adsorbent decarbonization technology is considered to be extremely effective due to its advantages such as high recycling rate, low regeneration energy consumption, little corrosion to equipment, and no secondary pollution. One of the promising carbon capture technologies.

美国三角研究所(RTI)、路易斯安那州立大学(LSU)和切奇杜威公司(C&D)在美国能源部(DOE)的资助下,在美国专利第6387337B1(2002.5.14)中用碱金属或碱土金属沉积在载体上,在93-1093℃下通过脱碳和再生捕集CO2。在第6280603B1 (2001.08.28)中用沉淀法制备碳酸碱金属助催化剂和含氧化镁的吸附剂,在300-500℃下捕集CO2。韩国电力公社在中国申请了专利:CN20041010564.0,提出用喷雾干燥的方法,来制备吸附剂颗粒。国内东南大学近年来也针对该项技术开展了相关研究,在 CN200820037600.5专利中提出了一种高活性钾基吸收剂干法脱除烟气中CO2的装置, 可与燃煤发电系统有机结合,利用燃煤烟气提供系统所需能量,有效的实现能源的梯级利用。在CN201810294379.X专利中提示了采用等体积浸渍法制备粉末状钠基吸附剂,再以其他钠基/胺基次活性组分溶液浸渍修饰吸附剂,得到高效钠基固体吸附剂。Under the funding of the U.S. Department of Energy (DOE), the Triangle Institute (RTI), Louisiana State University (LSU) and Cheche Dewey (C&D) used alkali metal or Alkaline earth metals are deposited on the support to capture CO2 through decarburization and regeneration at 93-1093°C. In No. 6280603B1 (2001.08.28), an alkali metal carbonate cocatalyst and an adsorbent containing magnesium oxide were prepared by precipitation method, and CO 2 was captured at 300-500°C. Korea Electric Power Corporation has applied for a patent in China: CN20041010564.0, which proposes to use spray drying method to prepare adsorbent particles. Domestic Southeast University has also carried out related research on this technology in recent years. In the CN200820037600.5 patent, a device for removing CO 2 in flue gas by dry method with high-activity potassium-based absorbent is proposed, which can be organically integrated with coal-fired power generation systems. In combination, the coal-fired flue gas is used to provide the energy required by the system, effectively realizing the cascade utilization of energy. In the CN201810294379.X patent, it is suggested that the powdered sodium-based adsorbent is prepared by an equal-volume impregnation method, and then the adsorbent is modified by impregnating the other sodium-based/amine-based sub-active component solution to obtain a high-efficiency sodium-based solid adsorbent.

以上专利是针对提高吸附剂的吸附性能或吸附剂反应系统,而针对钠基吸附剂的成型技术却鲜有报道,韩国电力社提出用喷雾干燥的方法,但由于此种方法,活性组分负载量较少且吸附剂粒径较小,对在流化床上具有一定的局限型。为此,针对电厂脱除 CO2,需要一种简单、方便、高效的吸附剂成型技术来确保其工业化稳定运行。The above patents are aimed at improving the adsorption performance of the adsorbent or the adsorbent reaction system, but there are few reports on the molding technology of the sodium-based adsorbent. The Korea Electric Power Corporation proposed the method of spray drying, but due to this method, the active component load The amount is small and the particle size of the adsorbent is small, which has certain limitations on the fluidized bed. Therefore, for CO 2 removal in power plants, a simple, convenient and efficient adsorbent molding technology is needed to ensure its industrial stable operation.

发明内容Contents of the invention

本发明旨在提供一种适用于碳捕集钠基吸附剂的成型方法。该方法可有效的降低吸附剂在碳捕集过程中磨损现象,是吸附剂稳定工业化运行的一种优化方案。The present invention aims to provide a molding method suitable for carbon-capturing sodium-based adsorbents. The method can effectively reduce the wear phenomenon of the adsorbent during the carbon capture process, and is an optimized scheme for the stable industrial operation of the adsorbent.

实现本发明目的在于提供一种适用于碳捕集钠基吸附剂的成型方法,该方法具体为:The object of the present invention is to provide a molding method suitable for carbon capture sodium-based adsorbent, the method is specifically:

将活性氧化铝小球粉碎后,将活性氧化铝粉末缓慢加入碳酸钠溶液浸渍搅拌,得到半干状固体进行干燥,随后煅烧;煅烧后的吸附剂块状固体进行粉碎,将吸附剂颗粒进行流化,流化后的吸附剂进行筛分,即可得到所需要的吸附剂;After pulverizing the activated alumina pellets, the activated alumina powder is slowly added to the sodium carbonate solution for immersion and stirring to obtain a semi-dry solid, which is dried and then calcined; the calcined adsorbent block solid is pulverized, and the adsorbent particles are fluidized After sieving, the fluidized adsorbent can be screened to obtain the required adsorbent;

流化过程中扬析的细粉继续粉碎后,再进行与水混合搅拌,再经过干燥、煅烧、破碎、流化及筛分,得到所需要的吸附剂。After the fine powder eluting during the fluidization process continues to be pulverized, it is mixed with water and stirred, and then dried, calcined, crushed, fluidized and sieved to obtain the required adsorbent.

进一步的,浸渍搅拌温度设定为40℃。Further, the immersion stirring temperature was set to 40°C.

进一步的,干燥温度为110℃,干燥时间为12h。Further, the drying temperature is 110° C., and the drying time is 12 hours.

进一步的,煅烧温度为400℃,升温速率为3K/min,煅烧时间为4h。Further, the calcination temperature is 400°C, the heating rate is 3K/min, and the calcination time is 4h.

进一步的,流化介质为空气,流化数为2~3,流化时间为4~12h。Further, the fluidization medium is air, the fluidization number is 2-3, and the fluidization time is 4-12 hours.

本发明相对于现有技术相比,具有以下优势:Compared with the prior art, the present invention has the following advantages:

1、本发明的适应于碳捕集钠基吸附剂的方法工艺简单,方便快捷;2、本发明制备的吸附剂颗粒球形度高,强度高,耐磨损,对设备腐蚀小,吸附剂循环利用率高。1. The method of the present invention suitable for carbon capture sodium-based adsorbent is simple in process, convenient and fast; 2. The adsorbent particles prepared by the present invention have high sphericity, high strength, wear resistance, little corrosion to equipment, and adsorbent circulation High utilization rate.

附图说明Description of drawings

图1为(a)破碎成型吸附剂SEM扫描电镜图;(b)流化成型吸附剂SEM扫描电镜图。Figure 1 is (a) the SEM scanning electron micrograph of the crushed and formed adsorbent; (b) the SEM scanning electron micrograph of the fluidized and formed adsorbent.

图2为不同成型方式吸附剂的磨损率对比图。Figure 2 is a comparison chart of the wear rate of adsorbents in different molding methods.

图3为本发明的工艺流程图。Fig. 3 is a process flow diagram of the present invention.

具体实施方式Detailed ways

对比例1Comparative example 1

1.吸附剂制备1. Adsorbent Preparation

取660g碳酸钠,在40℃下溶解于的去离子中,形成碳酸钠溶液。取1340g活性氧化铝经过球磨机研磨后,得到活性氧化铝粉末并将其缓慢加入碳酸钠溶液中,在电动搅拌机下浸渍搅拌8h得到半干状固体。得到半干状固体于干燥箱中在110℃下干燥12h,随后在马弗炉中400℃煅烧4h,升温速率为3K/min,将得到的吸附剂块状固体在破碎机中破碎,将破碎后的吸附剂在振筛机中筛分,即可得到所需要的吸附剂。Take 660g of sodium carbonate and dissolve it in deionized water at 40°C to form a sodium carbonate solution. Take 1340g of activated alumina and grind it with a ball mill to obtain activated alumina powder, which is slowly added to the sodium carbonate solution, dipped and stirred under an electric mixer for 8 hours to obtain a semi-dry solid. The obtained semi-dry solid was dried in a drying oven at 110°C for 12h, and then calcined in a muffle furnace at 400°C for 4h at a heating rate of 3K/min. The obtained adsorbent block solid was crushed in a crusher, and the crushed The final adsorbent is sieved in a vibrating sieve machine to obtain the required adsorbent.

2.磨损率测试2. Wear rate test

连接好进行试验所需要的试验装置,将装置进行检查是否有漏气现象。用电子天平称取200g粒径为0.4-0.5mm的吸附剂记为M0。将称取的吸附剂放入流化床反应器中,打开空气压缩机,控制空气流量为2m3/h。4h后,关闭空气压缩机,取出吸附剂,用电子天平测量吸附剂的质量并记下Mi。重复上述步骤,循环试验。总流化磨损时间为为 24h。并用下述公式(1)计算吸附剂的磨损率。Connect the test device required for the test, and check the device for air leakage. Weigh 200 g of the adsorbent with a particle size of 0.4-0.5 mm with an electronic balance and record it as M 0 . Put the weighed adsorbent into the fluidized bed reactor, turn on the air compressor, and control the air flow rate to 2m 3 /h. After 4 hours, turn off the air compressor, take out the adsorbent, measure the mass of the adsorbent with an electronic balance and record M i . Repeat the above steps, cycle test. The total fluidized wear time is 24h. And use the following formula (1) to calculate the wear rate of the adsorbent.

破碎成型吸附剂在流化床上磨损24h后的磨损率为0.79%/h。The attrition rate of the crushed adsorbent after 24 hours of wear on the fluidized bed is 0.79%/h.

实施例1Example 1

取660g碳酸钠,在40℃下溶解于一定量的的去离子中,形成碳酸钠溶液。取1340g活性氧化铝经过球磨机研磨后,得到活性氧化铝粉末并将其缓慢加入碳酸钠溶液中,在电动搅拌机下浸渍搅拌8h得到半干状固体。得到半干状固体于干燥箱中在110℃下干燥 12h,随后在马弗炉中400℃煅烧4h,升温速率为3K/min,将得到的吸附剂块状固体在破碎机中破碎,将得到吸附剂颗粒在鼓泡流化床流化12h,流化后的吸附剂在振筛机中筛分,即可得到所需要的吸附剂。对于在鼓泡流化床中扬析的细粉,经除尘袋收集后,置于球磨机中粉碎后,将得到的粉体吸附剂在电动搅拌机中与去离子水混合搅拌,再经过上述吸附剂制备流程,即可得到所需要的吸附剂。Take 660g of sodium carbonate and dissolve it in a certain amount of deionized water at 40°C to form a sodium carbonate solution. Take 1340g of activated alumina and grind it with a ball mill to obtain activated alumina powder, which is slowly added to the sodium carbonate solution, dipped and stirred under an electric mixer for 8 hours to obtain a semi-dry solid. The obtained semi-dry solid was dried in a drying oven at 110°C for 12h, then calcined in a muffle furnace at 400°C for 4h, the heating rate was 3K/min, and the obtained adsorbent block solid was crushed in a crusher to obtain The adsorbent particles are fluidized in the bubbling fluidized bed for 12 hours, and the fluidized adsorbent is sieved in a vibrating screen machine to obtain the required adsorbent. For the fine powder eluting in the bubbling fluidized bed, after being collected by the dust bag, it is placed in a ball mill and pulverized, and the obtained powder adsorbent is mixed with deionized water in an electric mixer, and then passed through the above adsorbent Through the preparation process, the required adsorbent can be obtained.

2.磨损率测试2. Wear rate test

连接好进行试验所需要的试验装置,将装置进行检查是否有漏气现象。用电子天平称取200g粒径为0.4-0.5mm的吸附剂记为M0。将称取的吸附剂放入流化床反应器中,打开空气压缩机,控制空气流量为2m3/h。4h后,关闭空气压缩机,取出吸附剂,用电子天平测量吸附剂的质量并记下Mi。重复上述步骤,循环试验。总流化磨损时间为为 24h。并用下述公式(1)计算吸附剂的磨损率。Connect the test device required for the test, and check the device for air leakage. Weigh 200 g of the adsorbent with a particle size of 0.4-0.5 mm with an electronic balance and record it as M 0 . Put the weighed adsorbent into the fluidized bed reactor, turn on the air compressor, and control the air flow rate to 2m 3 /h. After 4 hours, turn off the air compressor, take out the adsorbent, measure the mass of the adsorbent with an electronic balance and record M i . Repeat the above steps, cycle test. The total fluidized wear time is 24h. And use the following formula (1) to calculate the wear rate of the adsorbent.

破碎成型吸附剂在流化床上磨损24h后的磨损率为0.35%/hThe wear rate of the crushed and shaped adsorbent after wearing in the fluidized bed for 24 hours is 0.35%/h

实施例2Example 2

取660g碳酸钾,在40℃下溶解于去离子中,形成碳酸钾溶液。取1340g活性氧化铝经过球磨机研磨后,得到活性氧化铝粉末并将其缓慢加入碳酸钾溶液中,在电动搅拌机下浸渍搅拌8h得到半干状固体。得到半干状固体于干燥箱中在110℃下干燥12h,随后在马弗炉中400℃煅烧4h,升温速率为3K/min,将得到的吸附剂块状固体在破碎机中破碎,将得到吸附剂颗粒在鼓泡流化床流化12h,流化后的吸附剂在振筛机中筛分,即可得到所需要的吸附剂。对于在鼓泡流化床中扬析的细粉,经除尘袋收集后,置于球磨机中粉碎后,将得到的粉体吸附剂在电动搅拌机中与去离子水混合搅拌,再经过上述吸附剂制备流程,即可得到所需要的吸附剂。Take 660g of potassium carbonate and dissolve it in deionized water at 40°C to form a potassium carbonate solution. Take 1340g of activated alumina and grind it with a ball mill to obtain activated alumina powder, which is slowly added to potassium carbonate solution, dipped and stirred under an electric mixer for 8 hours to obtain a semi-dry solid. The obtained semi-dry solid was dried in a drying oven at 110°C for 12h, then calcined in a muffle furnace at 400°C for 4h, the heating rate was 3K/min, and the obtained adsorbent block solid was crushed in a crusher to obtain The adsorbent particles are fluidized in the bubbling fluidized bed for 12 hours, and the fluidized adsorbent is sieved in a vibrating screen machine to obtain the required adsorbent. For the fine powder eluting in the bubbling fluidized bed, after being collected by the dust bag, it is placed in a ball mill and pulverized, and the obtained powder adsorbent is mixed with deionized water in an electric mixer, and then passed through the above adsorbent Through the preparation process, the required adsorbent can be obtained.

Claims (5)

1. a kind of forming method suitable for carbon capture sodium base adsorbent, which is characterized in that after activated alumina bead is crushed, Active alumina powder is slowly added to sodium carbonate liquor dipping stirring, leather hard solid is obtained and is dried, then calcine;It forges Adsorbent blocks of solid after burning is crushed, and absorbent particles are fluidized, and the adsorbent after fluidisation is sieved Obtain required adsorbent;
After the fine powder of elutriation continues crushing in fluid mapper process, then be mixed with water, drying, calcining, broken, stream Change and sieve, obtains required adsorbent.
2. the forming method of carbon capture sodium base adsorbent according to claim 1, which is characterized in that the dipping stirring Temperature is set as 40 DEG C.
3. the forming method of carbon capture sodium base adsorbent according to claim 1, which is characterized in that the drying temperature It is 110 DEG C, drying time 12h.
4. the forming method of carbon capture sodium base adsorbent according to claim 1, which is characterized in that the calcination temperature It is 400 DEG C, heating rate 3K/min, calcination time 4h.
5. the forming method of carbon capture sodium base adsorbent according to claim 1, which is characterized in that the fluidizing agent For air, fluidization number is 2~3, and the fluidisation time is 4~12h.
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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01129093A (en) * 1987-11-13 1989-05-22 Kureha Chem Ind Co Ltd Method and apparatus for activating molded pitch
WO2002066152A2 (en) * 2001-01-05 2002-08-29 Questair Technologies, Inc. Adsorbent coating compositions, laminates and adsorber elements comprising such compositions and methods for their manufacture and use
CN101411338A (en) * 2008-12-03 2009-04-22 安徽农业大学 Beauveria bassiana granular formulation and preparation method thereof
US20100116134A1 (en) * 2007-03-08 2010-05-13 Jian Zheng High rate and high crush-strength adsorbents
CN101961638A (en) * 2010-10-22 2011-02-02 浙江大学 Method for preparing wear-resistant nano calcium oxide-based carbon dioxide reaction adsorbent
CN104759262A (en) * 2015-02-13 2015-07-08 云南中烟工业有限责任公司 Green bean porous particle and application thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01129093A (en) * 1987-11-13 1989-05-22 Kureha Chem Ind Co Ltd Method and apparatus for activating molded pitch
WO2002066152A2 (en) * 2001-01-05 2002-08-29 Questair Technologies, Inc. Adsorbent coating compositions, laminates and adsorber elements comprising such compositions and methods for their manufacture and use
US20100116134A1 (en) * 2007-03-08 2010-05-13 Jian Zheng High rate and high crush-strength adsorbents
CN101411338A (en) * 2008-12-03 2009-04-22 安徽农业大学 Beauveria bassiana granular formulation and preparation method thereof
CN101961638A (en) * 2010-10-22 2011-02-02 浙江大学 Method for preparing wear-resistant nano calcium oxide-based carbon dioxide reaction adsorbent
CN104759262A (en) * 2015-02-13 2015-07-08 云南中烟工业有限责任公司 Green bean porous particle and application thereof

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
ZHIKANG XU ET AL.: ""Understanding the CO2 sorption mechanisms of the MgO-doped Na-based sorbent at low temperatures"", 《GREENHOUSE GAS SCI TECHNOL.》 *
国帅 等: ""气固流化床新型 CO2吸附剂的制备及吸附性能"", 《青岛科技大学学报(自然科学版)》 *
张文静: ""复合型 CO2吸附剂的脱碳特性及其失效机理研究"", 《中国优秀硕士学位论文全文数据库(工程科技Ⅰ辑)》 *
江汉: ""一种球形颗粒硫磺成形技术——Kaltenbach -Thǜring 流化床转鼓造粒工艺"", 《硫酸工业》 *

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Application publication date: 20191203