JP2005087932A - Method for regenerating carbon dioxide absorbent - Google Patents

Method for regenerating carbon dioxide absorbent Download PDF

Info

Publication number
JP2005087932A
JP2005087932A JP2003327148A JP2003327148A JP2005087932A JP 2005087932 A JP2005087932 A JP 2005087932A JP 2003327148 A JP2003327148 A JP 2003327148A JP 2003327148 A JP2003327148 A JP 2003327148A JP 2005087932 A JP2005087932 A JP 2005087932A
Authority
JP
Japan
Prior art keywords
carbon dioxide
regenerating
absorbing substance
carbonate
aqueous solution
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.)
Granted
Application number
JP2003327148A
Other languages
Japanese (ja)
Other versions
JP3937016B2 (en
Inventor
Hisaaki Hanaoka
寿明 花岡
Takahiro Yoshida
貴紘 吉田
Shinji Fujimoto
真司 藤本
Tomoaki Minowa
智朗 美濃輪
Shinya Yokoyama
伸也 横山
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
National Institute of Advanced Industrial Science and Technology AIST
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by National Institute of Advanced Industrial Science and Technology AIST filed Critical National Institute of Advanced Industrial Science and Technology AIST
Priority to JP2003327148A priority Critical patent/JP3937016B2/en
Publication of JP2005087932A publication Critical patent/JP2005087932A/en
Application granted granted Critical
Publication of JP3937016B2 publication Critical patent/JP3937016B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for regenerating a carbon dioxide absorbent by decomposing a carbonate-forming carbon dioxide absorbent chemically without high-temperature heating to gasify and thereby desorb the dioxide. <P>SOLUTION: This method comprises treating the carbonate-forming carbon dioxide absorbent sequentially with an acid aqueous solution together with an alcohol aqueous solution or separately with the acid aqueous solution followed by the alcohol aqueous solution to decompose the carbonate chemically and remove the yielded carbon dioxide and then forming a hydroxide to regenerate the absorbent in a wet manner at a normal temperature. The method permits the treatment under a pressure of the dioxide desorbing process of equal to or lower than the atmospheric pressure. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、炭酸塩を含有する二酸化炭素吸収物質中の炭酸塩を分解し、二酸化炭素吸収物質を再生する二酸化炭素吸収物質の再生方法に関する。更に詳しくは、炭酸塩を含有する二酸化炭素吸収物質中の炭酸塩を高温加熱することなく湿式で化学的に分解して、発生する二酸化炭素を効果的に脱離させて、二酸化炭素吸収物質を再生する二酸化炭素吸収物質の方法に関する。   The present invention relates to a carbon dioxide-absorbing material regeneration method for decomposing a carbonate in a carbon dioxide-absorbing material containing carbonate to regenerate the carbon dioxide-absorbing material. More specifically, the carbonate in the carbon dioxide-absorbing material containing carbonate is chemically decomposed in a wet manner without heating at high temperature, and the generated carbon dioxide is effectively desorbed. It relates to a method of carbon dioxide absorbing material to be regenerated.

従来の炭酸塩を形成する二酸化炭素吸収物質を再生する方法としては、炭酸塩含有する二酸化吸収物質を高温で熱分解して二酸化炭素を脱離して酸化物にする方法が広く知られている。例えば、二酸化炭素吸収物質としてよく知られている水酸化カルシウムや酸化カルシウムは、二酸化炭素を吸収して生成する炭酸カルシウムを熱分解して酸化カルシウム(CaO)を生成するには、800℃以上の加熱が必要である。従って、この方法は、一般に外部から多量の熱を加える必要があり、エネルギーの消費量が大きいという問題があるばかりでなく、表面積が小さくなり二酸化炭素吸収性能が低下する。   As a conventional method for regenerating a carbon dioxide-absorbing substance that forms a carbonate, a method in which a carbonate-containing dioxide-absorbing substance is thermally decomposed at a high temperature to desorb carbon dioxide to form an oxide is widely known. For example, calcium hydroxide or calcium oxide, which is well known as a carbon dioxide-absorbing substance, is not less than 800 ° C. in order to thermally decompose calcium carbonate generated by absorbing carbon dioxide to produce calcium oxide (CaO). Heating is required. Therefore, this method generally requires a large amount of heat from the outside, and not only has a problem of large energy consumption, but also reduces the surface area and reduces the carbon dioxide absorption performance.

一方、特許文献1では、より省エネルギーで炭酸カルシウムから水酸化カルシウムを製造する方法として、塩化アンモニウムを用い、水溶性の塩化カルシウム(CaCl)を形成し、二酸化炭素(CO)とアンモニア(NH)を発生させ、アンモニアと二酸化炭素との混合ガスからアンモニアを分離し、塩化カルシウムと反応させて水酸化カルシウム(Ca(OH))を生成する、以下の反応式(1)、(2)で表されるような方法が開示されている。 On the other hand, in Patent Document 1, as a method for producing calcium hydroxide from calcium carbonate with more energy saving, ammonium chloride is used to form water-soluble calcium chloride (CaCl 2 ), and carbon dioxide (CO 2 ) and ammonia (NH 2 ). 3 ) is generated, ammonia is separated from a mixed gas of ammonia and carbon dioxide, and reacted with calcium chloride to generate calcium hydroxide (Ca (OH) 2 ). The following reaction formulas (1), (2 ) Is disclosed.

CaCO+2NHCl→CaCl+2NH↑+CO↑+HO …(1) CaCO 3 + 2NH 4 Cl → CaCl 2 + 2NH 3 ↑ + CO 2 ↑ + H 2 O (1)

CaCl+2NH↑+2HO→Ca(OH)↓+2NHCl …(2) CaCl 2 + 2NH 3 ↑ + 2H 2 O → Ca (OH) 2 ↓ + 2NH 4 Cl (2)

しかし、この方法は、炭酸カルシウム(CaCO)が水に対して溶解度が低いという問題の他に、上記のようにアンモニアと二酸化炭素との混合ガスからアンモニアを分離する必要もある。その上、この反応を効果的に行うためには、反応式(1)では温度70〜200℃、圧力400mmHgないし水蒸気飽和圧という(CaCO溶解槽の)反応条件が、反応式(2)では、温度100〜200℃、圧力0.5MPa〜2.0MPa(5〜20kgf/cm2)の反応条件が必要である。 However, in this method, in addition to the problem that calcium carbonate (CaCO 3 ) has low solubility in water, it is also necessary to separate ammonia from the mixed gas of ammonia and carbon dioxide as described above. In addition, in order to carry out this reaction effectively, the reaction conditions (temperature of 70 to 200 ° C., pressure of 400 mmHg or water vapor saturation pressure in the reaction formula (1) (CaCO 3 dissolution tank) are The reaction conditions of a temperature of 100 to 200 ° C. and a pressure of 0.5 MPa to 2.0 MPa (5 to 20 kgf / cm 2 ) are necessary.

また、特許文献2は、炭酸カルシウム含有鉱物を酢酸と水溶性アルコール混合水溶液の蒸気に暴露させ、含有炭酸カルシウムと該蒸気との反応生成物を加熱処理して炭酸カルシウムから水酸化カルシウムを形成する方法を開示しているが、この方法では、加熱を伴い、含有鉱物の膨潤、多孔化を目的にしている。このように、現状では炭酸塩含有二酸化炭素吸収物質を省エネルギーで且つ簡便に再生する方法は見出されていない。   Further, Patent Document 2 exposes a calcium carbonate-containing mineral to vapor of a mixed aqueous solution of acetic acid and a water-soluble alcohol, and heat-treats a reaction product of the contained calcium carbonate and the vapor to form calcium hydroxide from calcium carbonate. Although a method is disclosed, this method is accompanied by heating and is intended to swell and make the contained mineral porous. Thus, at present, no method for regenerating the carbonate-containing carbon dioxide-absorbing material in an energy saving and simple manner has been found.

特開昭59−30720号公報JP 59-30720 A 特開平9−295878号公報Japanese Patent Laid-Open No. 9-295878

本発明は、上記の問題点を克服するために下記の目的で発明されたものである。
本発明の目的は、炭酸塩を形成する二酸化炭素吸収物質の炭酸塩を常温で化学的に分解し、生成した二酸化炭素を効果的に気相中に脱離させることにより、炭酸塩を水酸化物に変換することにより、省エネルギーで且つ簡便に二酸化炭素吸収物質を再生する方法を提供することである。
The present invention has been invented for the following purposes in order to overcome the above problems.
The object of the present invention is to chemically decompose the carbonate of the carbon dioxide-absorbing substance that forms the carbonate at room temperature, and to effectively desorb the generated carbon dioxide into the gas phase, thereby hydroxylating the carbonate. An object is to provide a method for regenerating a carbon dioxide-absorbing material in an energy-saving and simple manner by converting it into a product.

本発明者は、このような課題を背景に対して、鋭意研究を重ねた結果、炭酸塩を形成する二酸化炭素吸収物質を酸水溶液で処理して炭酸塩を分解して生成する二酸化炭素を完全に除去した後、アルコール水溶液、又はアンモニア水溶液で順次処理して、炭酸塩を分解して生成する二酸化炭素を完全に除去して、水酸化物を形成することにより、高効率且つ省エネルギーで二酸化炭素吸収物質を再生することを見出し、この知見に基づいて本発明を完成させた。   As a result of intensive research on the background of such problems, the present inventor has completely treated carbon dioxide generated by decomposing carbonate by treating a carbon dioxide-absorbing substance that forms carbonate with an acid aqueous solution. After removing the carbon dioxide, it is treated with an aqueous alcohol solution or an aqueous ammonia solution in order to completely remove the carbon dioxide produced by decomposing the carbonate, thereby forming a hydroxide. The present inventors have found that the absorbent material is regenerated and completed the present invention based on this finding.

即ち、本発明1の二酸化炭素吸収物質を再生する方法は、炭酸塩を形成する二酸化炭素吸収物質を酸水溶液で処理して炭酸塩を分解する炭酸塩分解工程と、生成した二酸化炭素を気相に脱離させる二酸化炭素脱離工程と、該二酸化炭素脱離工程後に、アルコール水溶液で処理して水酸化物を生成する水酸化物生成工程とを有することを特徴とする。   That is, the method for regenerating a carbon dioxide-absorbing substance of the present invention includes a carbonate decomposition step in which a carbon dioxide-absorbing substance that forms a carbonate is treated with an acid aqueous solution to decompose the carbonate, and the generated carbon dioxide is vapor-phased. A carbon dioxide desorption step for desorbing the carbon dioxide and a hydroxide generation step for generating a hydroxide by treatment with an aqueous alcohol solution after the carbon dioxide desorption step.

本発明2の二酸化炭素吸収物質を再生する方法は、炭酸塩を形成する二酸化炭素吸収物質を酸水溶液で処理して炭酸塩を分解する炭酸塩分解工程と、生成する二酸化炭素を気相に脱離させる二酸化炭素脱離工程と、該二酸化炭素脱離工程後に、アンモニア水溶液で処理して、水酸化物を生成する水酸化物生成工程とを有することを特徴とする。   The method for regenerating a carbon dioxide-absorbing substance of the present invention comprises a carbonate decomposition step of treating a carbon dioxide-absorbing substance forming a carbonate with an acid aqueous solution to decompose the carbonate, and desorbing the generated carbon dioxide to the gas phase. It is characterized by having a carbon dioxide desorption step of separating, and a hydroxide generation step of generating a hydroxide by treatment with an aqueous ammonia solution after the carbon dioxide desorption step.

本発明3の二酸化炭素吸収物質を再生する方法は、本発明1又は本発明2に記載の二酸化炭素吸収物質を再生する方法において、前記二酸化炭素脱離工程時の圧力が大気圧以下であることを特徴とする。
本発明4の二酸化炭素吸収物質を再生する方法は、本発明1〜3から選択される1発明の二酸化炭素吸収物質を再生する方法において、前記二酸化炭素脱離工程時の温度が常温であることを特徴とする。
The method for regenerating a carbon dioxide-absorbing substance according to the third aspect of the present invention is the method for regenerating a carbon dioxide-absorbing substance according to the first or second aspect, wherein the pressure during the carbon dioxide desorption step is equal to or lower than atmospheric pressure. It is characterized by.
The method for regenerating a carbon dioxide-absorbing substance according to the present invention 4 is the method for regenerating a carbon dioxide-absorbing substance according to one invention selected from the first to third aspects, wherein the temperature during the carbon dioxide desorption step is normal temperature. It is characterized by.

本発明5の二酸化炭素吸収物質を再生する方法は、本発明1〜4から選択される1発明の二酸化炭素吸収物質を再生する方法において、前記炭酸塩分解工程と前記二酸化炭素脱離工程を同時に行うことを特徴とする。
本発明6の二酸化炭素吸収物質を再生する方法は、本発明5の二酸化炭素吸収物質を再生する方法において、前記炭酸塩分解工程、及び前記二酸化炭素脱離工程時の圧力が大気圧以下であることを特徴とする。
The method for regenerating a carbon dioxide-absorbing substance according to the present invention 5 is the method for regenerating a carbon dioxide-absorbing substance according to one invention selected from the present inventions 1 to 4, wherein the carbonate decomposition step and the carbon dioxide desorption step are simultaneously performed. It is characterized by performing.
The method for regenerating a carbon dioxide-absorbing substance of the present invention 6 is the method for regenerating a carbon dioxide-absorbing substance of the present invention 5, wherein the pressure during the carbonate decomposition step and the carbon dioxide desorption step is equal to or lower than atmospheric pressure. It is characterized by that.

本発明7の二酸化炭素吸収物質を再生する方法は、本発明5の二酸化炭素吸収物質を再生する方法において、前記炭酸塩分解工程、及び前記二酸化炭素脱離工程時の温度が常温であることを特徴とする。
本発明8の二酸化炭素吸収物質を再生する方法は、本発明1〜7から選択される1発明の二酸化炭素吸収物質を再生する方法において、前記酸水溶液が硝酸、塩酸、酢酸、硫酸、リン酸から選択される1種以上の水溶液であることを特徴とする。
The method for regenerating a carbon dioxide-absorbing substance of the present invention 7 is the method for regenerating a carbon dioxide-absorbing substance of the present invention 5, wherein the temperature during the carbonate decomposition step and the carbon dioxide desorption step is normal temperature. Features.
The method for regenerating a carbon dioxide-absorbing material according to the present invention 8 is the method for regenerating a carbon dioxide-absorbing material according to one invention selected from the present invention 1-7, wherein the acid aqueous solution is nitric acid, hydrochloric acid, acetic acid, sulfuric acid, phosphoric acid. It is 1 or more types of aqueous solution selected from these, It is characterized by the above-mentioned.

本発明9の二酸化炭素吸収物質を再生する方法は、本発明1〜8から選択される1発明の二酸化炭素吸収物質を再生する方法において、前記二酸化炭素吸収物質が、アルカリ金属、アルカリ土類金属、鉄、マグネシウムから選択される1種以上の酸化物若しくは水酸化物、又はカルシウムを含む生物体を出発物とする酸化物若しくは水酸化物であることを特徴とする。   The method for regenerating a carbon dioxide-absorbing material according to the present invention 9 is the method for regenerating a carbon dioxide-absorbing material according to one invention selected from the present inventions 1 to 8, wherein the carbon dioxide-absorbing material is an alkali metal or an alkaline earth metal. It is characterized by being one or more oxides or hydroxides selected from iron, magnesium, or oxides or hydroxides starting from organisms containing calcium.

[アルコール水溶液による水酸化物生成工程]
本発明1で用いるアルコール水溶液は、メチルアルコール及び/又はエチルアルコールを水で薄めたものである。メチルアルコールを使用する場合は、再生する二酸化炭素吸収物質として炭酸カルシウム(CaCO)、酸水溶液として酢酸を用いた場合には、以下の反応式(3)及び(4)により、炭酸カルシウム(CaCO)を化学的に分解して、カルシウム(Ca)を溶解して、同時に生成する二酸化炭素を完全に気相に脱離させた後に、メチルアルコール水溶液で処理して水酸化カルシウム(Ca(OH))を沈殿生成することにより、二酸化炭素吸収物質が再生される。
[Hydroxide generation process with aqueous alcohol solution]
The alcohol aqueous solution used in the present invention 1 is obtained by diluting methyl alcohol and / or ethyl alcohol with water. When methyl alcohol is used, calcium carbonate (CaCO 3 ) is used as the carbon dioxide absorbing material to be regenerated, and when acetic acid is used as the acid aqueous solution, calcium carbonate (CaCO 3 ) is obtained by the following reaction formulas (3) and (4). 3 ) is chemically decomposed to dissolve calcium (Ca), and simultaneously generated carbon dioxide is completely desorbed to the gas phase, and then treated with an aqueous methyl alcohol solution to obtain calcium hydroxide (Ca (OH 2 ) The carbon dioxide absorbing material is regenerated by precipitating 2 ).

CaCO+2CHCOOH→Ca2++2CHCOO+CO↑+HO …(3) CaCO 3 + 2CH 3 COOH → Ca 2+ + 2CH 3 COO + CO 2 ↑ + H 2 O (3)

Ca(CHCOO)+2CHOH→ Ca(OH)↓+2CHCOOCH …(4) Ca (CH 3 COO) 2 + 2CH 3 OH → Ca (OH) 2 ↓ + 2CH 3 COOCH 3 (4)

本発明1において、二酸化炭素吸収物質の再生には、二酸化炭素吸収物質の炭酸塩を完全に分解して、溶解することと、発生する二酸化炭素を完全に気相に脱離することが重要である。従って、溶解度が低い場合は、溶液の温度を常温以上にすることもできるし、多量の水溶液を用いることもできる。発生する二酸化炭素を効果的に気相に脱離するには、常温以上にすることも有効であるが、溶液を撹拌しながら、大気圧以下にするのがより効果的である。   In the present invention 1, for the regeneration of the carbon dioxide absorbing material, it is important to completely decompose and dissolve the carbonate of the carbon dioxide absorbing material and to completely desorb the generated carbon dioxide to the gas phase. is there. Therefore, when the solubility is low, the temperature of the solution can be raised to room temperature or higher, and a large amount of aqueous solution can be used. In order to effectively desorb the generated carbon dioxide to the gas phase, it is effective to set the temperature to room temperature or higher, but it is more effective to reduce the pressure to atmospheric pressure or lower while stirring the solution.

[アンモニア水溶液による水酸化物生成工程]
本発明2のアンモニア水溶液を用いる場合の具体的な1例として、再生する二酸化炭素吸収物質として炭酸カルシウム(CaCO)、酸水溶液として硝酸(HNO)を用いた場合には、以下の反応式(5)及び(6)より、炭酸カルシウムを化学的に分解して、カルシウム(Ca)を溶解して、同時に生成する二酸化炭素を完全に気相に脱離させた後に、アンモニア水溶液で処理して水酸化カルシウム(Ca(OH))を沈殿生成することにより、二酸化炭素吸収物質が再生される。
CaCO+2HNO→ Ca2++2NO +CO↑+HO …(5)
Ca(NO+2NHOH→ Ca(OH)↓+2NH +2NO …(6)
[Hydroxide generation process with aqueous ammonia solution]
Specific example of the case of using an aqueous ammonia solution of the present invention 2, calcium carbonate as a carbon dioxide absorbing materials to be reproduced (CaCO 3), in the case of using the nitric acid (HNO 3) as an acid aqueous solution, the following reaction formula From (5) and (6), calcium carbonate is chemically decomposed, calcium (Ca) is dissolved, and simultaneously generated carbon dioxide is completely desorbed into the gas phase, followed by treatment with an aqueous ammonia solution. Thus, the carbon dioxide-absorbing substance is regenerated by forming calcium hydroxide (Ca (OH) 2 ) by precipitation.
CaCO 3 + 2HNO 3 → Ca 2+ + 2NO 3 + CO 2 ↑ + H 2 O (5)
Ca (NO 3 ) 2 + 2NH 4 OH → Ca (OH) 2 ↓ + 2NH 4 + + 2NO 3 (6)

本発明では、炭酸塩を形成する二酸化炭素吸収物質の炭酸塩を常温で化学的に分解し、生成した二酸化炭素を効果的に気相中に脱離させることにより、炭酸塩を水酸化物や酸化物に変換することにより、省エネルギーで且つ簡便に二酸化炭素吸収物質を再生することができる。   In the present invention, the carbonate of the carbon dioxide-absorbing substance that forms the carbonate is chemically decomposed at room temperature, and the produced carbon dioxide is effectively desorbed into the gas phase, so that the carbonate is converted to hydroxide or By converting to an oxide, it is possible to regenerate the carbon dioxide-absorbing material with energy saving and simple.

以下、本発明の実施の形態を実施例をあげて更に具体的に説明する。本実施例では、二酸化炭素吸収物質として最も使用されている酸化カルシウム(CaO)、水酸化カルシウム(Ca(OH))が二酸化炭素(CO)を吸収して生成される炭酸カルシウムの再生について述べる。 Hereinafter, the embodiment of the present invention will be described more specifically with reference to examples. In the present embodiment, calcium carbonate (CaO) and calcium hydroxide (Ca (OH) 2 ), which are most used as carbon dioxide-absorbing substances, regenerate calcium carbonate produced by absorbing carbon dioxide (CO 2 ). State.

60w%の硝酸10gと蒸留水100mlを混合して、硝酸水溶液(0.92モル/リットル、pH:0.3)を作成する。この硝酸水溶液を撹拌させながらこれに溶解しうる炭酸カルシウムを添加して、以下の式のように完全に溶解させ、二酸化炭素を発生させる。   An aqueous nitric acid solution (0.92 mol / liter, pH: 0.3) is prepared by mixing 10 g of 60 w% nitric acid and 100 ml of distilled water. While this nitric acid aqueous solution is stirred, soluble calcium carbonate is added to the nitric acid solution and completely dissolved as shown in the following formula to generate carbon dioxide.

CaCO+2HNO→ Ca2++2NO +CO↑+HCaCO 3 + 2HNO 3 → Ca 2+ + 2NO 3 + CO 2 ↑ + H 2 O

次に、この水溶液を撹拌しながらアスピレータ(水流ポンプ)で気相を400mmHgの圧力に保って排気しながら、生成した二酸化炭素を完全に気相に脱離させる。この二酸化炭素を完全に気相に脱離させた後、28wt%のアンモニア水を添加し、以下の反応を進行させる。   Next, the produced carbon dioxide is completely desorbed into the gas phase while this aqueous solution is stirred and evacuated with an aspirator (water flow pump) while maintaining the gas phase at a pressure of 400 mmHg. After the carbon dioxide is completely desorbed into the gas phase, 28 wt% ammonia water is added to proceed with the following reaction.

Ca(NO+2NHOH→ Ca(OH)↓+2NH +2NO
約1時間後、水酸化カルシウムの白色沈殿を得た。この沈殿物の濾過・洗浄を3回繰り返した後、これを120℃で乾燥した。
Ca (NO 3 ) 2 + 2NH 4 OH → Ca (OH) 2 ↓ + 2NH 4 + + 2NO 3
After about 1 hour, a white precipitate of calcium hydroxide was obtained. This filtration and washing of the precipitate was repeated three times, and then this was dried at 120 ° C.

60w%の硝酸10gと蒸留水100mlを混合して、硝酸水溶液(0.92モル/リットル、pH:0.3)を作成する。この硝酸水溶液を撹拌させて、アスピレータ(水流ポンプ)で気相を400mmHgの圧力に保って排気しながら、溶解しうる炭酸カルシウムを添加して、完全に溶解させ、同時に生成した二酸化炭素を完全に気相に脱離させた。   An aqueous nitric acid solution (0.92 mol / liter, pH: 0.3) is prepared by mixing 10 g of 60 w% nitric acid and 100 ml of distilled water. While stirring this nitric acid aqueous solution and exhausting it while keeping the gas phase at a pressure of 400 mmHg with an aspirator (water flow pump), soluble calcium carbonate is added and completely dissolved, and at the same time, the generated carbon dioxide is completely removed. Desorbed into the gas phase.

CaCO+2HNO→ Ca2++2NO +CO↑+HO …(3) CaCO 3 + 2HNO 3 → Ca 2+ + 2NO 3 + CO 2 ↑ + H 2 O (3)

この二酸化炭素(CO)を気相に完全に脱離させた後、28wt%のアンモニア水を添加し、以下の反応を進行させる。 After the carbon dioxide (CO 2 ) is completely desorbed into the gas phase, 28 wt% ammonia water is added to proceed with the following reaction.

Ca(NO+2NHOH→ Ca(OH)↓+2NH +2NO
…(4)
約1時間後、水酸化カルシウムの白色沈殿を得た。実施例1と同様にこの沈殿物の濾過・洗浄を3回繰り返した後、これを120℃で乾燥した。
Ca (NO 3 ) 2 + 2NH 4 OH → Ca (OH) 2 ↓ + 2NH 4 + + 2NO 3
(4)
After about 1 hour, a white precipitate of calcium hydroxide was obtained. The precipitate was filtered and washed three times in the same manner as in Example 1, and then dried at 120 ° C.

酢酸水溶液100mlを撹拌させながら炭酸カルシウムを添加して、完全に溶解出来る程度の酢酸カルシウムを生成させる。   While stirring 100 ml of an acetic acid aqueous solution, calcium carbonate is added to produce calcium acetate that can be completely dissolved.

CaCO+2CHCOOH→ Ca2++2CHCOO+CO↑+HCaCO 3 + 2CH 3 COOH → Ca 2+ + 2CH 3 COO + CO 2 ↑ + H 2 O

次に、この水溶液を撹拌しながらアスピレータ(水流ポンプ)で気相を400mmHgに排気し、生成した二酸化炭素を完全に気相に脱離させる。二酸化炭素が気相に完全に脱離させた後、メチルアルコール水溶液を添加し、以下の反応を進行させる。   Next, while stirring the aqueous solution, the gas phase is exhausted to 400 mmHg by an aspirator (water flow pump), and the generated carbon dioxide is completely desorbed to the gas phase. After carbon dioxide is completely desorbed into the gas phase, an aqueous methyl alcohol solution is added to proceed with the following reaction.

Ca2++2CHCOO+CHOH→Ca(OH)↓+2CHCOOCH Ca 2+ + 2CH 3 COO + CH 3 OH → Ca (OH) 2 ↓ + 2CH 3 COOCH 3

得られた水酸化カルシウムの白色沈殿の濾過・洗浄を3回繰り返した後、120℃で乾燥した。実施例1〜3で得られた水酸化カルシウムは、二酸化炭素吸収物質として使用することができるが、この水酸化カルシウムを500℃近傍まで加熱処理をして酸化カルシウムにして二酸化炭素吸収物質として使用することもできる。   The obtained white precipitate of calcium hydroxide was repeatedly filtered and washed three times, and then dried at 120 ° C. The calcium hydroxide obtained in Examples 1 to 3 can be used as a carbon dioxide-absorbing substance, but this calcium hydroxide is heated to around 500 ° C. to form calcium oxide and used as a carbon dioxide-absorbing substance. You can also

一般に、二酸化炭素吸収物質は、二酸化炭素を吸収して炭酸塩を形成するが、高温処理により炭酸塩は分解される、二酸化炭素の吸収と再生を繰り返すと、次第に二酸化炭素吸収性能は低下してくる。物性的には、二酸化炭素吸収と再生を繰り返すことにより表面積、ポア容積(細孔容積)は低下していく。従って、二酸化炭素吸収性能の低下はこれらの物性変化によると考えられる。本発明では二酸化炭素吸収性能の低下した二酸化炭素吸収物質から生じた炭酸カルシウムを使用して、本発明による方法で再生を行うと、水酸化カルシウム、酸化カルシウムの初期の表面積、ポア容積が再生され、初期の二酸化炭素吸収性能も得られた。
In general, carbon dioxide-absorbing substances absorb carbon dioxide to form carbonates, but carbonates are decomposed by high-temperature treatment. When carbon dioxide absorption and regeneration are repeated, the carbon dioxide absorption performance gradually decreases. come. In terms of physical properties, the surface area and pore volume (pore volume) decrease as carbon dioxide absorption and regeneration are repeated. Therefore, the decrease in carbon dioxide absorption performance is considered to be due to these physical property changes. In the present invention, when calcium carbonate generated from a carbon dioxide-absorbing substance having reduced carbon dioxide absorption performance is used and regenerated by the method according to the present invention, the initial surface area and pore volume of calcium hydroxide and calcium oxide are regenerated. The initial carbon dioxide absorption performance was also obtained.

Claims (9)

炭酸塩を形成する二酸化炭素吸収物質を酸水溶液で処理して炭酸塩を分解する炭酸塩分解工程と、
生成した二酸化炭素を気相に脱離させる二酸化炭素脱離工程と、
該二酸化炭素脱離工程後に、アルコール水溶液で処理して水酸化物を生成する水酸化物生成工程と
を有することを特徴とする二酸化炭素吸収物質を再生する方法。
A carbonate decomposition step in which a carbon dioxide-absorbing substance that forms carbonate is treated with an acid aqueous solution to decompose carbonate;
A carbon dioxide desorption process for desorbing the generated carbon dioxide into the gas phase;
A method for regenerating a carbon dioxide-absorbing substance, comprising: a hydroxide generation step of generating a hydroxide by treatment with an aqueous alcohol solution after the carbon dioxide desorption step.
炭酸塩を形成する二酸化炭素吸収物質を酸水溶液で処理して炭酸塩を分解する炭酸塩分解工程と、
生成する二酸化炭素を気相に脱離させる二酸化炭素脱離工程と、
該二酸化炭素脱離工程後に、アンモニア水溶液で処理して、水酸化物を生成する水酸化物生成工程と
を有することを特徴とする二酸化炭素吸収物質を再生する方法。
A carbonate decomposition step in which a carbon dioxide-absorbing substance that forms carbonate is treated with an acid aqueous solution to decompose carbonate;
A carbon dioxide desorption process for desorbing the generated carbon dioxide into the gas phase;
A method of regenerating a carbon dioxide-absorbing substance, comprising: a hydroxide generation step of generating a hydroxide by treating with an aqueous ammonia solution after the carbon dioxide desorption step.
請求項1又は2に記載の二酸化炭素吸収物質を再生する方法において、
前記二酸化炭素脱離工程時の圧力が大気圧以下である
ことを特徴とする二酸化炭素吸収物質を再生する方法。
The method for regenerating a carbon dioxide-absorbing substance according to claim 1 or 2,
A method for regenerating a carbon dioxide-absorbing substance, wherein the pressure during the carbon dioxide desorption step is equal to or lower than atmospheric pressure.
請求項1〜3から選択される1項に記載の二酸化炭素吸収物質を再生する方法において、
前記二酸化炭素脱離工程時の温度が常温である
ことを特徴とする二酸化炭素吸収物質を再生する方法。
The method for regenerating a carbon dioxide-absorbing substance according to claim 1 selected from claims 1 to 3,
A method for regenerating a carbon dioxide-absorbing substance, wherein the temperature during the carbon dioxide desorption step is room temperature.
請求項1〜4から選択される1項に記載の二酸化炭素吸収物質を再生する方法において、
前記炭酸塩分解工程と前記二酸化炭素脱離工程を同時に行う
ことを特徴とする二酸化炭素吸収物質を再生する方法。
The method for regenerating a carbon dioxide-absorbing substance according to claim 1 selected from claims 1 to 4,
The method for regenerating a carbon dioxide-absorbing substance, wherein the carbonate decomposition step and the carbon dioxide desorption step are performed simultaneously.
請求項5に記載の二酸化炭素吸収物質を再生する方法において、
前記炭酸塩分解工程、及び前記二酸化炭素脱離工程時の圧力が大気圧以下である
ことを特徴とする二酸化炭素吸収物質を再生する方法。
The method for regenerating a carbon dioxide-absorbing substance according to claim 5,
A method for regenerating a carbon dioxide-absorbing substance, wherein the pressure during the carbonate decomposition step and the carbon dioxide desorption step is equal to or lower than atmospheric pressure.
請求項5に記載の二酸化炭素吸収物質を再生する方法において、
前記炭酸塩分解工程、及び前記二酸化炭素脱離工程時の温度が常温である
ことを特徴とする二酸化炭素吸収物質を再生する方法。
The method for regenerating a carbon dioxide-absorbing substance according to claim 5,
A method for regenerating a carbon dioxide-absorbing substance, wherein the temperature during the carbonate decomposition step and the carbon dioxide desorption step is room temperature.
請求項1〜7から選択される1項に記載の二酸化炭素吸収物質を再生する方法において、
前記酸水溶液が硝酸、塩酸、酢酸、硫酸、リン酸から選択される1種以上の水溶液であることを特徴とする二酸化炭素吸収物質を再生する方法。
The method for regenerating a carbon dioxide-absorbing substance according to claim 1 selected from claims 1 to 7,
A method for regenerating a carbon dioxide-absorbing substance, wherein the acid aqueous solution is at least one aqueous solution selected from nitric acid, hydrochloric acid, acetic acid, sulfuric acid, and phosphoric acid.
請求項1〜8から選択される1項に記載の二酸化炭素吸収物質を再生する方法において、
前記二酸化炭素吸収物質が、アルカリ金属、アルカリ土類金属、鉄、マグネシウムから選択される1種以上の酸化物若しくは水酸化物、又はカルシウムを含む生物体を出発物とする酸化物若しくは水酸化物であることを特徴とする二酸化炭素吸収物質を再生する方法。
The method for regenerating a carbon dioxide-absorbing substance according to claim 1 selected from claims 1 to 8,
The carbon dioxide-absorbing substance is one or more oxides or hydroxides selected from alkali metals, alkaline earth metals, iron and magnesium, or oxides or hydroxides starting from organisms containing calcium A method for regenerating a carbon dioxide-absorbing substance, characterized in that
JP2003327148A 2003-09-19 2003-09-19 Regeneration method of carbon dioxide absorbing material Expired - Lifetime JP3937016B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2003327148A JP3937016B2 (en) 2003-09-19 2003-09-19 Regeneration method of carbon dioxide absorbing material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2003327148A JP3937016B2 (en) 2003-09-19 2003-09-19 Regeneration method of carbon dioxide absorbing material

Publications (2)

Publication Number Publication Date
JP2005087932A true JP2005087932A (en) 2005-04-07
JP3937016B2 JP3937016B2 (en) 2007-06-27

Family

ID=34457092

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2003327148A Expired - Lifetime JP3937016B2 (en) 2003-09-19 2003-09-19 Regeneration method of carbon dioxide absorbing material

Country Status (1)

Country Link
JP (1) JP3937016B2 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20100186591A1 (en) * 2007-06-21 2010-07-29 Statoil Asa System and process for handling a co2 comprising waste gas and separation of co2
GB2467921A (en) * 2009-02-19 2010-08-25 Origo Ind Ltd Carbon dioxide absorption and desorption
US8435330B2 (en) 2007-11-01 2013-05-07 Alstom Technology Ltd Carbon capture system and process
WO2019211714A1 (en) * 2018-04-30 2019-11-07 National Cheng Kung University Method for regeneration of carbon dioxide absorbent
CN116832580A (en) * 2023-08-21 2023-10-03 天府永兴实验室 Low energy carbon dioxide capture composition with hydrogen ion self-regulating property, capture method and application

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20100186591A1 (en) * 2007-06-21 2010-07-29 Statoil Asa System and process for handling a co2 comprising waste gas and separation of co2
US8435330B2 (en) 2007-11-01 2013-05-07 Alstom Technology Ltd Carbon capture system and process
KR101329149B1 (en) * 2007-11-01 2013-11-14 알스톰 테크놀러지 리미티드 Carbon capture system and process
GB2467921A (en) * 2009-02-19 2010-08-25 Origo Ind Ltd Carbon dioxide absorption and desorption
WO2019211714A1 (en) * 2018-04-30 2019-11-07 National Cheng Kung University Method for regeneration of carbon dioxide absorbent
CN116832580A (en) * 2023-08-21 2023-10-03 天府永兴实验室 Low energy carbon dioxide capture composition with hydrogen ion self-regulating property, capture method and application
CN116832580B (en) * 2023-08-21 2024-03-15 天府永兴实验室 Low energy carbon dioxide capture composition with hydrogen ion self-regulating property, capture method and application

Also Published As

Publication number Publication date
JP3937016B2 (en) 2007-06-27

Similar Documents

Publication Publication Date Title
TW510819B (en) Method and apparatus for treating a waste gas containing fluorine-containing compounds
TW200916181A (en) Method of treating emission gas
CN105363451B (en) One kind is used to decompose N2O effective catalyst and its preparation method and application
CN110548514B (en) Hierarchical porous cobalt/iron bimetallic oxide nanosheet catalyst with rich oxygen vacancies and preparation method and application thereof
JP5009746B2 (en) Chemical fixation of carbon dioxide in flue gas
CN105883859A (en) Waste salt treatment method
JP3937016B2 (en) Regeneration method of carbon dioxide absorbing material
KR101189075B1 (en) Carbon dioxide separating method comprising regenerating process of absorption and system using the same
JP3114775B2 (en) Manufacturing method of aqueous sodium carbonate solution
CN103143336A (en) Regeneration method of activated carbon catalyst used for preparing glyphosate
KR101527452B1 (en) Method for Preventing Ammonia Slip Using Carbonic Acid Washing Water
JP3525184B2 (en) Catalyst for producing hydrogen and method for producing hydrogen
TWI577642B (en) Method of recycling ammonia from wastewater and preparing solid calcium sulfate and calcium chloride solution
CN111359398B (en) Method for denitration and whitening of flue gas
JP2001348346A (en) Method for purifying methane fermentation gas
CN109045963B (en) Method for removing gaseous selenium dioxide in coal-fired flue gas through oxidation-absorption
JP2004172016A (en) Fuel cell power generating system
KR20120074139A (en) Method for prevention of ammonia slip using metal salts
KR101797744B1 (en) Reduction Solution for the Removal of Nitrogen Oxide Using TNT Wastewater and Manufacturing Method the Same
JP3083463B2 (en) Regeneration method of catalyst for wet oxidation treatment
JPH0521610B2 (en)
JP2009254979A (en) Method of manufacturing ammonia decomposing catalyst
JP4314647B2 (en) SOx removal method in exhaust gas
JP2010005583A (en) Device for removing trace component in exhaust gas and method
JP2000296311A (en) ABSORBENT FOR REMOVING SOx, NOx AND CO2 IN WASTE GAS, REGENERATION AND RECYCLE USE OF ABSORBENT AND EFFECTIVE USE OF BY-PRODUCT (CHEMICALS) BY REACTION PRODUCT WITH WASTE GAS COMPONENT

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20050315

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20070215

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20070223

R150 Certificate of patent or registration of utility model

Ref document number: 3937016

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

EXPY Cancellation because of completion of term