KR20130118007A - Process for preparing carbon dioxide adsorbent by amine enrichment - Google Patents
Process for preparing carbon dioxide adsorbent by amine enrichment Download PDFInfo
- Publication number
- KR20130118007A KR20130118007A KR1020120040827A KR20120040827A KR20130118007A KR 20130118007 A KR20130118007 A KR 20130118007A KR 1020120040827 A KR1020120040827 A KR 1020120040827A KR 20120040827 A KR20120040827 A KR 20120040827A KR 20130118007 A KR20130118007 A KR 20130118007A
- Authority
- KR
- South Korea
- Prior art keywords
- carbon dioxide
- amine
- methanol
- solution
- concentration
- Prior art date
Links
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
- 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/62—Carbon oxides
-
- 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
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28002—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
- B01J20/28004—Sorbent size or size distribution, e.g. particle size
-
- 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
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28054—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
- B01J20/28057—Surface area, e.g. B.E.T specific surface area
- B01J20/28066—Surface area, e.g. B.E.T specific surface area being more than 1000 m2/g
-
- 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
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
- B01J20/3202—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the carrier, support or substrate used for impregnation or coating
- B01J20/3204—Inorganic carriers, supports or substrates
-
- 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
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
- B01J20/3214—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the method for obtaining this coating or impregnating
- B01J20/3217—Resulting in a chemical bond between the coating or impregnating layer and the carrier, support or substrate, e.g. a covalent bond
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/40—Capture or disposal of greenhouse gases of CO2
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/151—Reduction of greenhouse gas [GHG] emissions, e.g. CO2
Landscapes
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- General Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Environmental & Geological Engineering (AREA)
- Gas Separation By Absorption (AREA)
- Treating Waste Gases (AREA)
Abstract
Description
본 발명은 아민 농축법을 이용한 이산화탄소 흡착제의 제조방법에 관한 것이다. 보다 구체적으로, 본 발명은 이산화탄소에 대한 선택적 포집능이 우수한 이산화탄소 흡착제를 아민 농축법을 이용하여 간단하고 효율적으로 제조하는 방법에 관한 것이다. The present invention relates to a method for producing a carbon dioxide adsorbent using amine concentration. More specifically, the present invention relates to a method for producing a carbon dioxide adsorbent having excellent selective capturing ability to carbon dioxide simply and efficiently by using an amine concentration method.
이산화탄소는 실내 공기의 질을 저하시키고 지구 온난화의 주범이므로, 이산화탄소의 농도를 제어할 수 있는 기술 개발이 절실히 요구되고 있다. Since carbon dioxide deteriorates the quality of indoor air and is a major culprit of global warming, there is an urgent need to develop a technology that can control the concentration of carbon dioxide.
활성탄(activated carbon, AC)은 넓은 비표면적을 가지고 있어 악취를 비롯한 기체분자에 대한 흡착용량이 크며, 발달된 미세공이 세공표면에 노출되어 있어 흡착속도가 빠른 장점을 가지고 있기 때문에 기체상 오염물질의 제거능력이 높은 편이다. 또한 잘 알려진 이산화탄소 흡수제인 제올라이트와는 달리 상대적으로 수분에 대한 영향이 적고 저렴한 가격으로 널리 사용되고 있다. 그러나 온실가스이며 실내공기 오염물질 가운데 하나인 이산화탄소에 대한 포집능력이 매우 낮기 때문에 다양한 표면개질을 통하여 이를 극복하고자 하는 노력이 이루어지고 있다. Activated carbon (AC) has a large specific surface area, which has a large adsorption capacity for gas molecules including odors, and developed micropores are exposed to the surface of pores, so adsorption speed is high. Removal ability is high. In addition, unlike zeolite, a well-known carbon dioxide absorbent, it has a relatively low effect on moisture and is widely used at a low price. However, since the capturing ability of carbon dioxide, which is a greenhouse gas and one of indoor air pollutants, is very low, efforts have been made to overcome it through various surface modifications.
구체적으로 산-염기 반응에 의한 개질이나 아민 또는 암모니아 표면처리를 통한 알칼리 작용기 형성과 같은 연구개발이 진행되고 있다. 그러나 대부분의 기술은 습식 이온교환이나 함침법을 이용하는데, 이는 제조시간이 매우 길고, 함침 후 세척시 발생하는 오염물의 2차 처리가 필요할 뿐만 아니라, 흡착제 표면에 형성된 질소 작용기의 분포가 고르지 못해 이산화탄소의 선택적 포집효과를 극대화시키기 힘든 문제점이 있다. Specifically, research and development such as reforming by an acid-base reaction or forming an alkali functional group through amine or ammonia surface treatment are underway. However, most of the techniques use wet ion exchange or impregnation methods, which require very long manufacturing times, require secondary treatment of contaminants generated during washing after impregnation, and the uneven distribution of nitrogen functional groups formed on the adsorbent surface. There is a problem that is difficult to maximize the selective collection effect of.
한편 건식법은 우수한 이산화탄소 제거율을 보이는 반면, 대부분 200 내지 800℃의 열을 가해야 하기 때문에 상대적으로 높은 에너지 소비가 필요하다. On the other hand, while the dry method shows a good removal rate of carbon dioxide, it requires a relatively high energy consumption because most of the heat should be applied to 200 to 800 ℃.
본 발명자들은 상기한 바와 같은 종래의 건식법, 습식 이온교환이나 함침법의 문제점을 극복하고자 예의 연구 검토한 결과, 액상 아민 농축법을 사용할 경우 과도한 에너지의 소비 없이 단시간 내에 이산화탄소 포집능이 우수한 활성탄 표면에 질소 작용기를 가지는 이산화탄소 흡착제를 제조할 수 있음을 알아내고 본 발명을 완성하게 되었다.The present inventors have diligently studied to overcome the problems of the conventional dry method, wet ion exchange or impregnation method as described above. The present invention was completed by finding out that a carbon dioxide adsorbent having a functional group can be prepared.
따라서, 본 발명의 목적은 이산화탄소에 대한 선택적 포집능이 우수한 이산화탄소 흡착제를 간단하고 효율적으로 제조하는 방법을 제공하는 것이다.Accordingly, it is an object of the present invention to provide a method for the simple and efficient preparation of a carbon dioxide adsorbent having an excellent selective capture capacity for carbon dioxide.
본 발명은 질소 작용기를 가지는 이산화탄소 흡착제의 제조방법에 관한 것으로서, 본 발명의 제조방법은The present invention relates to a method for producing a carbon dioxide adsorbent having a nitrogen functional group, the method of the present invention
(i) 활성탄과 아민 용액을 혼합하고 교반시키는 단계; 및(i) mixing and stirring the activated carbon and amine solution; And
(ii) 교반된 혼합액을 로터리 증류기로 감압 농축시키는 단계를 포함한다.(ii) concentrating the stirred liquid mixture under reduced pressure with a rotary still.
상기 단계 (i)에서 활성탄으로는 비표면적이 1200 내지 1500 m2/g이고 입자 크기가 5 내지 10 mm인 활성탄을 사용할 수 있으나, 이에 한정되는 것은 아니다.The activated carbon in step (i) may be activated carbon having a specific surface area of 1200 to 1500 m 2 / g and a particle size of 5 to 10 mm, but is not limited thereto.
상기 단계 (i)에서 아민 용액은 아민을 물, 에탄올 또는 메탄올에 용해시킨 용액을 포함하며, 메탄올에 용해시킨 용액이 바람직하다. 아민 용액의 농도는 1.0 내지 3.0 M이 바람직하다.The amine solution in step (i) includes a solution of amine dissolved in water, ethanol or methanol, preferably a solution dissolved in methanol. The concentration of the amine solution is preferably 1.0 to 3.0 M.
상기 아민으로는 모노에탄올아민(monoethanolamine: MEA), 디에탄올아민(diethanolamine: DEA), 트리에탄올아민(triethanolamine), 에틸렌디아민(ethylenediamine) 등을 사용할 수 있으며, 모노에탄올아민이 바람직하다.The amine may be monoethanolamine (MEA), diethanolamine (DEA), triethanolamine (triethanolamine), ethylenediamine (ethylenediamine), and the like, and monoethanolamine is preferable.
활성탄과 아민 용액의 혼합비는 1:1 내지 1:3(w/v)일 수 있다. The mixing ratio of the activated carbon and the amine solution may be 1: 1 to 1: 3 (w / v).
상기 단계 (i) 및 (ii)에서 교반 및 농축 온도는 30 내지 50℃가 바람직하다.In the above steps (i) and (ii), the stirring and concentration temperature is preferably 30 to 50 ° C.
상기 단계 (ii)에서는 끓는점 차를 이용하여 용매를 단시간에 제거함으로써 질소 작용기의 유실을 최소화하면서 질소 작용기를 활성탄 입자에 함침시킬 수 있게 된다. In step (ii), the boiling point difference is used to remove the solvent in a short time so that the nitrogen functional group can be impregnated into the activated carbon particles while minimizing the loss of the nitrogen functional group.
본 발명의 제조방법은 상기 단계 (i) 및 (ii)를 2회 이상 반복하여 질소 작용기의 함량을 증가시킬 수 있다. In the production method of the present invention, the steps (i) and (ii) may be repeated two or more times to increase the content of nitrogen functional groups.
본 발명에 따라 제조된 이산화탄소 흡착제는 바람직하게는 40 내지 60℃에서 건조시켜 사용한다. The carbon dioxide adsorbent prepared according to the present invention is preferably used after drying at 40 to 60 ℃.
본 발명에 따라 제조된 이산화탄소 흡착제는 입자상 활성탄 표면에 질소 작용기가 균일하게 분포되어 있어, 이산화탄소 포집능이 매우 우수하다. The carbon dioxide adsorbent prepared according to the present invention has a uniform distribution of nitrogen functional groups on the surface of the granular activated carbon, so that the carbon dioxide trapping ability is very excellent.
본 발명에 따른 아민 농축법을 이용한 이산화탄소 흡착제의 제조방법에 따르면, 과도한 에너지의 소비 없이 단시간 내에 우수한 선택성과 높은 이산화탄소 포집능을 가지는 이산화탄소 흡착제를 제조할 수 있다. 또한 본 발명에 따른 제조방법은 종래의 함침법과 달리 별도의 세척 단계를 필요로 하지 않아 오염물의 발생이 적다. 아울러, 본 발명에 따라 제조된 이산화탄소 흡착제는 이산화탄소 흡착능이 미처리 활성탄 뿐만 아니라 종래의 함침법을 이용하여 제조된 이산화탄소 흡착제 보다 현저히 우수하다. According to the manufacturing method of the carbon dioxide adsorbent using the amine concentration method according to the present invention, it is possible to produce a carbon dioxide adsorbent having excellent selectivity and high carbon dioxide trapping ability in a short time without excessive energy consumption. In addition, unlike the conventional impregnation method, the manufacturing method according to the present invention does not require a separate washing step, thereby reducing the generation of contaminants. In addition, the carbon dioxide adsorbent prepared according to the present invention is significantly better than the carbon dioxide adsorbent prepared by using the conventional impregnation method as well as untreated activated carbon.
이하, 실시예에 의해 본 발명을 보다 구체적으로 설명하고자 한다. 이들 실시예는 오직 본 발명을 설명하기 위한 것으로, 본 발명의 범위가 이들 실시예에 국한되지 않는다는 것은 당업자에게 있어서 자명하다.
Hereinafter, the present invention will be described in more detail with reference to Examples. It is to be understood by those skilled in the art that these embodiments are for illustrative purpose only and that the scope of the present invention is not limited to these embodiments.
실시예 1-5: 농축법을 이용한 흡착제 제조 (I)Example 1-5 Preparation of Adsorbents Using Concentration (I)
모노에탄올아민(MEA)를 하기 용매에 하기 농도로 용해시켜 MEA 용액을 제조하였다.Monoethanolamine (MEA) was dissolved in the following solvent at the following concentration to prepare a MEA solution.
코코넛 활성탄(비표면적: 1369.60 m2/g, 크기: 5∼10 mm, WSC-470, Calgon, USA) 10 g과 상기와 같이 제조한 MEA 용액 20 ml를 혼합한 후, 온도를 40 ℃로 유지시킨 로터리 증류기(Rotary Evaporator, Heidolph)에서 20분간 교반하였다. 교반이 종료된 후 냉각기와 진공펌프를 작동시켜 끓는점 차이를 이용하여 활성탄 표면에 질소 작용기를 농축시켰다. 반응이 종료된 후 흡착제를 50 ℃에서 건조하였다.
After mixing 10 g of coconut activated carbon (specific surface area: 1369.60 m 2 / g, size: 5-10 mm, WSC-470, Calgon, USA) with 20 ml of the MEA solution prepared as described above, the temperature was maintained at 40 ° C. The resultant was stirred for 20 minutes in a rotary evaporator (Heidolph). After the stirring was completed, the nitrogen functional group was concentrated on the surface of the activated carbon using a boiling point difference by operating a cooler and a vacuum pump. After the reaction was completed, the adsorbent was dried at 50 ° C.
실시예 6-8: 농축법을 이용한 흡착제 제조 (II)Example 6-8 Preparation of Adsorbents Using Concentration (II)
모노에탄올아민(MEA)을 하기 용매에 하기 농도로 용해시켜 MEA 용액을 제조하였다.Monoethanolamine (MEA) was dissolved in the following solvent at the following concentration to prepare a MEA solution.
코코넛 활성탄(비표면적: 1369.60 m2/g, 크기: 5∼10 mm, WSC-470, Calgon, USA) 10 g과 상기와 같이 제조한 MEA 용액 20 ml를 혼합한 후, 온도를 40 ℃로 유지시킨 로터리 증류기(Rotary Evaporator, Heidolph)에서 20분간 교반하였다. 교반이 종료된 후 냉각기와 진공펌프를 작동시켜 끓는점 차이를 이용하여 활성탄 표면에 질소 작용기를 농축시켰다. After mixing 10 g of coconut activated carbon (specific surface area: 1369.60 m 2 / g, size: 5-10 mm, WSC-470, Calgon, USA) with 20 ml of the MEA solution prepared as described above, the temperature was maintained at 40 ° C. The resultant was stirred for 20 minutes in a rotary evaporator (Heidolph). After the stirring was completed, the nitrogen functional group was concentrated on the surface of the activated carbon using a boiling point difference by operating a cooler and a vacuum pump.
그런 다음, 농축된 흡착제에 상기 MEA 용액을 가하고 상기한 과정을 반복하였다. 반응이 종료된 후 흡착제를 50 ℃에서 건조하였다. Then, the MEA solution was added to the concentrated adsorbent and the above procedure was repeated. After the reaction was completed, the adsorbent was dried at 50 ° C.
비교예 1-3: 함침법을 이용한 흡착제 제조Comparative Example 1-3: Preparation of Adsorbent Using Impregnation Method
모노에탄올아민(MEA)를 하기 용매에 하기 농도로 용해시켜 MEA 용액을 제조하였다.Monoethanolamine (MEA) was dissolved in the following solvent at the following concentration to prepare a MEA solution.
코코넛 활성탄(비표면적: 1369.60 m2/g, 크기: 5∼10 mm, WSC-470, Calgon, USA) 10 g과 상기와 같이 제조한 MEA 용액 20 ml를 혼합한 후, 40 ℃로 유지되는 반응조에서 중탕법을 이용하여 24시간 함침하였다. 함침이 충분히 이루어진 후, 감압여과장치를 통해 입상의 활성탄 흡착제를 분리한 후 50 ℃에서 건조하였다. 10 g of coconut activated carbon (specific surface area: 1369.60 m 2 / g, size: 5 to 10 mm, WSC-470, Calgon, USA) and 20 ml of the MEA solution prepared as described above are mixed and the reactor is maintained at 40 ° C. It was impregnated for 24 hours using a hot water bath at. After sufficient impregnation, the granular activated carbon adsorbent was separated through a vacuum filter and then dried at 50 ° C.
시험예 1: 질소함량 분석 Test Example 1: Nitrogen Content Analysis
실시예 1 내지 8 및 비교예 1 내지 3에서 제조된 흡착제 표면의 질소함량을 X-선 광전자 분광법(XPS: K-Alpha, Thermo Electron)을 이용하여 정량적으로 분석하고, 그 결과를 하기 표 4에 나타내었다. The nitrogen content of the surface of the adsorbents prepared in Examples 1 to 8 and Comparative Examples 1 to 3 was quantitatively analyzed using X-ray photoelectron spectroscopy (XPS: K-Alpha, Thermo Electron), and the results are shown in Table 4 below. Indicated.
상기 표 4의 결과로부터 MEA 용액 처리를 통해 질소함량이 증가되었음을 확인할 수 있다. 함침법을 이용하여 흡착제를 제조한 비교예 1 내지 3의 경우, 용매의 종류에 따라 질소함량이 1.8 내지 2.0%인 반면, 본 발명에 따른 농축법을 이용하여 흡착제를 제조한 실시예 1 내지 8의 경우, 용매의 종류와 MEA 농도 및 농축횟수에 따라 질소함량이 2.4 내지 4.6%인 것으로 관찰되었다. 특히 MEA 농도를 2.0 및 3.0 M로 1회 또는 2회 농축하였을 경우 질소함량이 크게 증가함을 볼 수 있었다.
It can be seen from the results of Table 4 that the nitrogen content was increased through the MEA solution treatment. In Comparative Examples 1 to 3, in which the adsorbent was prepared using the impregnation method, the nitrogen content was 1.8 to 2.0% depending on the type of the solvent, whereas Examples 1 to 8 prepared the adsorbent using the concentration method according to the present invention. In the case of nitrogen, it was observed that the nitrogen content of 2.4 to 4.6% depending on the type of solvent and the concentration of MEA and the number of concentrations. In particular, when the MEA concentration was concentrated once or twice to 2.0 and 3.0 M, the nitrogen content was significantly increased.
시험예 2: 이산화탄소 흡착시험Test Example 2: Carbon Dioxide Adsorption Test
흡착제의 이산화탄소 포집량을 확인하기 위하여, 시험가스 공급부, 흡착 반응부 및 가스 분석부로 구성된 흡착시험 장치를 준비하였다. In order to confirm the carbon dioxide trapped amount of the adsorbent, an adsorption test apparatus including a test gas supply unit, an adsorption reaction unit, and a gas analyzer was prepared.
내경 10 mm인 스테인레스 스틸로 제작된 고정층 반응기에 실시예 1 내지 8 및 비교예 1 내지 3에서 제조된 흡착제 각각을 3 g 충진하고, 포집하고자 하는 대상물질인 이산화탄소의 부피 기준 농도가 3000 ppm이 되는 공기흐름을 공급하였다. 공급속도는 2 LPM(liter/min)이 유지되도록 하였고, 희석용 가스는 건조 공기를 선택하였다. 흡착시험은 상온, 상압 분위기에서 반응기 전후 이산화탄소의 농도변화를 이산화탄소 분석기(SenseAir, ASEN ALARM)로 실시간 측정하였다. 그 결과를 하기 표 5에 나타내었다. A fixed bed reactor made of stainless steel with an inner diameter of 10 mm was filled with 3 g of each of the adsorbents prepared in Examples 1 to 8 and Comparative Examples 1 to 3, and the volume-based concentration of carbon dioxide, a target material to be collected, was 3000 ppm. Air flow was supplied. The feed rate was maintained at 2 LPM (liter / min), and the diluent gas was selected as dry air. In the adsorption test, the concentration change of carbon dioxide before and after the reactor was measured by a carbon dioxide analyzer (SenseAir, ASEN ALARM) at room temperature and atmospheric pressure. The results are shown in Table 5 below.
상기 표 5의 결과로부터, 미처리된 활성탄의 경우 0.016 mmol/g의 낮은 이산화탄소 흡착량을 확인할 수 있었다. 이는 산성가스인 이산화탄소에 대한 친화력이 낮아 단순한 물리적 흡착만이 존재하기 때문인 것으로 생각된다. 함침법을 이용하여 흡착제를 제조한 비교예 1 내지 3의 경우, 이산화탄소 흡착량이 0.022 내지 0.028 mmol/g인 반면, 본 발명에 따른 농축법을 이용하여 흡착제를 제조한 실시예 1 내지 8의 경우, 이산화탄소 흡착량이 0.119 내지 0.564 mmol/g이었다. 특히 메탄올을 용매로 이용한 경우 세 용매 중 가장 높은 흡착량을 보여주었다. 이는 낮은 끓는점(64.7 ℃)으로 상대적으로 짧은 시간 내에 용매가 휘발하면서 메탄올의 휘발과 다량의 질소 작용기의 함침을 동시에 유도할 수 있었던 것으로 추측된다. From the results in Table 5, it was confirmed that the carbon dioxide adsorption amount of 0.016 mmol / g in the case of untreated activated carbon. This is thought to be due to the low affinity for carbon dioxide, which is an acid gas, with only physical adsorption. In Comparative Examples 1 to 3, in which the adsorbent was prepared using the impregnation method, the adsorption amount of carbon dioxide was 0.022 to 0.028 mmol / g, whereas in Examples 1 to 8, which prepared the adsorbent using the concentration method according to the present invention, The carbon dioxide adsorption amount was 0.119 to 0.564 mmol / g. In particular, when methanol was used as the solvent, it showed the highest adsorption amount among the three solvents. It is presumed that this was able to induce the volatilization of methanol and the impregnation of a large amount of nitrogen functionalities at the same time as the solvent volatilized at a relatively low boiling point (64.7 ° C.).
Claims (10)
(ii) 교반된 혼합액을 로터리 증류기로 감압 농축시키는 단계를 포함하는 질소 작용기를 가지는 이산화탄소 흡착제의 제조방법.(i) mixing and stirring the activated carbon and amine solution; And
(ii) a method of producing a carbon dioxide adsorbent having a nitrogen functional group, comprising the step of concentrating the stirred mixed solution under reduced pressure with a rotary still.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020120040827A KR20130118007A (en) | 2012-04-19 | 2012-04-19 | Process for preparing carbon dioxide adsorbent by amine enrichment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020120040827A KR20130118007A (en) | 2012-04-19 | 2012-04-19 | Process for preparing carbon dioxide adsorbent by amine enrichment |
Publications (1)
Publication Number | Publication Date |
---|---|
KR20130118007A true KR20130118007A (en) | 2013-10-29 |
Family
ID=49636505
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR1020120040827A KR20130118007A (en) | 2012-04-19 | 2012-04-19 | Process for preparing carbon dioxide adsorbent by amine enrichment |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR20130118007A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US9682865B2 (en) | 2014-10-27 | 2017-06-20 | Hyundai Motor Company | Active carbon and method for preparation of the same |
-
2012
- 2012-04-19 KR KR1020120040827A patent/KR20130118007A/en not_active Application Discontinuation
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US9682865B2 (en) | 2014-10-27 | 2017-06-20 | Hyundai Motor Company | Active carbon and method for preparation of the same |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP5877922B1 (en) | Absorption type removal and concentration equipment | |
TWI702080B (en) | Absorption removal/concentration device | |
Tan et al. | Adsorption of carbon dioxide by sodium hydroxide-modified granular coconut shell activated carbon in a fixed bed | |
Aschenbrenner et al. | Comparative study of solvent properties for carbon dioxide absorption | |
CN107413161B (en) | Copper oxide/graphene composite material and preparation method and application thereof | |
CN104117343A (en) | Preparation method of renewable low concentration CO2 high efficient absorption material | |
CN105236405B (en) | A kind of convenient preparation method of biomass-based nitrating activated carbon | |
CN104324692A (en) | Preparation method of active carbon capable of removing formaldehyde | |
CN105502384A (en) | Preparation method of shaddock-peel-base activated carbon and application of shaddock-peel-base activated carbon to phenol-containing wastewater and waste gas | |
CN106964316A (en) | A kind of zeolite imidazole ester skeleton functionalized ion liquid composite and its preparation and application | |
CN102963876A (en) | Preparation method of microporous carbon material | |
CN102500324A (en) | Organic-inorganic composite carbon dioxide adsorbing material and preparation method thereof | |
KR20090048085A (en) | A production method of aminated sorbent | |
CN113926426A (en) | Method for adsorbing phthalate pollutants in wastewater by using functionalized mesoporous carbon | |
KR20130040273A (en) | Absorbent for purifying air, filter comprising the absorbent and method for preparing the filter | |
CN108176415A (en) | A kind of air purification raw material of wood-charcoal cleans regenerative use technology | |
CN106064053A (en) | A kind of flue gas demercuration adsorbent and preparation method thereof | |
CN110201661A (en) | A kind of manganese base charcoal of porous array structure and its preparation method and application | |
CN107497478B (en) | Catalyst for removing VOCs (volatile organic compounds) through ultraviolet catalysis and preparation method thereof | |
KR20130118007A (en) | Process for preparing carbon dioxide adsorbent by amine enrichment | |
CN110368897B (en) | Coal tar-based nitrogen-containing porous carbon with ultrahigh specific surface area as well as preparation method and application thereof | |
CN108404595A (en) | A method of preparing formaldehyde adsorbent using grape distiller's wass | |
CN116282328B (en) | Method for efficiently regenerating mineralized synergistic activated carbon by catalyzing perfluorinated compounds at low temperature | |
CN110559992B (en) | Preparation process of inorganic strong acid ammonium salt modified coconut shell activated carbon for removing formaldehyde in air at normal temperature, product and application thereof | |
CN106984152B (en) | It is a kind of for trapping the two-phase mixture of carbon dioxide |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
E902 | Notification of reason for refusal | ||
E601 | Decision to refuse application |