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TW201023969A - Adsorbent, regenerative cycle operation of the same and apparatus of regeneration the same - Google Patents

Adsorbent, regenerative cycle operation of the same and apparatus of regeneration the same Download PDF

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TW201023969A
TW201023969A TW97149765A TW97149765A TW201023969A TW 201023969 A TW201023969 A TW 201023969A TW 97149765 A TW97149765 A TW 97149765A TW 97149765 A TW97149765 A TW 97149765A TW 201023969 A TW201023969 A TW 201023969A
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adsorbent
metal
reactor
weight
gas
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TW97149765A
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TWI476042B (en
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Chin-Ming Huang
Wang Chen
Jui-Yen Cheng
Jyh-Feng Hwang
Wan-Hsia Liu
Heng-Wen Hsu
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Ind Tech Res Inst
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Abstract

An adsorbent is provided. The adsorbent includes metal oxide having porous with pore diameter of 0.1 nm to 100 nm, the specific surface of 0.5 to 38.28 cm<SP>2</SP>/g and the adsorption capacity of 0.25g CO2/1g metal oxide.

Description

IW 29621twf.doc/n 201023969 九、發明說明: 【發明所屬之技術領域】 本發明是有關於一種吸附劑、其再生循環方法及其再 生設備。 ^ 【先前技術】 氣候變化國際間審查小組(The intergovernmentg ❹ Panel on climate Change,IPCC)於西元2001年的科學評估 報告中顯示.如果二氧化碳排放量維持目前的排放水準, 到西兀2100年時全球平均的環境溫度將上升攝氏14到 5.8度,這種快速升溫情況在過去的千年間從未被發現, 而這項結果將會導致海平面上升9至88公分。從氣候變化 的觀點來看’這是過去-萬年以來的最大增溢幅度,目前 氣溫與上次冰河時期也不過相差攝氏4度,和上次lpcc 1995年评估報告攝氏丨.5度至3度的增溫幅度相比,攝氏 1.4至5.8度的預測結果應該是令人們所震驚的,其所延伸 ® 的氣象災害也必定是災情惨重的。IPCC 2001年報告預 估,全球暖化所弓丨發的氣象災害將造成每年將超過三千億 美元的損失’因此減少大氣中的二氧化碳為目前人類所必 須共同面對且極需要趕快解決的一個大問題。 【發明内容】 本發明提供-種吸附劑可以有效吸附二氧化破。 本發明提供一種吸附劑的製造方法,可以減少能源的 4 201023969 —.-——1A W 2962 ltwf,doc/n 損耗,節省成本。 本發明提供一種吸附劑的再生循環的方法,可 μ 便的製程使吸附劑再生。 以間 本發明&amp;供一種再生吸附劑的設備,其設備簡軍 取得且成本低廉。 本發明提出一種吸附劑,包括金屬氧化物,其具有 徑為0.1奈米〜100奈米的多個孔洞,比表面積為0^二38 28 • 平方公尺/克’吸附量至少為0.25克二氧化碳/1克金屬氧化 物。 依照本發明實施例所述,上述之吸附劑之轉化率至 少0.3,而且可以反覆吸脫附二氧化碳至少1〇次的循環。 依知、本發明實施例所述,上述之吸附劑中,金屬氧化 物包括鹼土族元素的氧化物、鹼金族元素的氧化物或其混 合物。 依照本發明實施例所述,上述之吸附劑更包括金屬氫 氧化物’其中金屬氧化物的含量為40重量%〜80重量%, 〇 金屬氫氧化物的含量為20重量%[〜6〇重量%。 依照本發明實施例所述,上述之吸附劑中,金屬氫氧 化合物包括驗土族元素的氫氧化合物或鹼金族元素的氫氧 化合物或其混合物。 依照本發明實施例所述’上述之吸附劑更包括金屬碳 酸化合物’其中金屬氧化物的含量為75重量%〜95重量 % ’金屬碳酸化合物的含量為5重量%〜25重量%。 依本發明實施例所述’上述之吸附劑中,金屬碳酸 201023969IW 29621twf.doc/n 201023969 IX. Description of the Invention: [Technical Field of the Invention] The present invention relates to an adsorbent, a method for recycling the same, and a regenerating device thereof. ^ [Previous Technology] The Intergovernmentg ❹ Panel on Climate Change (IPCC) showed in the 2001 Western Science Assessment Report that if CO2 emissions maintain current emissions levels, they will be global to Xiqiao in 2100. The average ambient temperature will rise by 14 to 5.8 degrees Celsius. This rapid warming has never been seen in the past millennium, and this result will cause sea levels to rise by 9 to 88 cm. From the point of view of climate change, 'this is the biggest increase in the past - the past year, the current temperature is only 4 degrees Celsius from the last ice age, and the last lpcc 1995 assessment report 摄 5 degrees to 3 degrees Celsius Compared with the temperature increase of 1.4 to 5.8 degrees Celsius, the predicted results should be shocking. The meteorological disasters of the extended ® must also be severe. The IPCC 2001 report predicts that meteorological disasters caused by global warming will result in more than $300 billion in annual losses. Therefore, reducing carbon dioxide in the atmosphere is a common problem that human beings must face and need to solve quickly. Big problem. SUMMARY OF THE INVENTION The present invention provides an adsorbent that can effectively adsorb dioxide. The invention provides a method for manufacturing an adsorbent, which can reduce the energy consumption of the energy consumption of the 2010A 129, which is 1A W 2962 ltwf, doc/n loss. The present invention provides a method of regenerating a sorbent which regenerates the adsorbent in an easy process. The apparatus of the present invention &amp; for a regenerative adsorbent is simple in equipment and low in cost. The invention provides an adsorbent comprising a metal oxide having a plurality of pores having a diameter of from 0.1 nm to 100 nm, and a specific surface area of 0^2 38 28 • m ^ 2 /g of adsorbed amount of at least 0.25 g of carbon dioxide /1 gram of metal oxide. According to an embodiment of the present invention, the conversion rate of the above adsorbent is at least 0.3, and the cycle of adsorbing and desorbing carbon dioxide at least 1 time can be repeated. According to the present invention, in the above adsorbent, the metal oxide includes an oxide of an alkaline earth element, an oxide of an alkali gold element, or a mixture thereof. According to an embodiment of the invention, the adsorbent further comprises a metal hydroxide, wherein the content of the metal oxide is 40% by weight to 80% by weight, and the content of the cerium metal hydroxide is 20% by weight [~6〇 weight %. According to an embodiment of the present invention, in the above adsorbent, the metal hydroxide compound includes a hydroxide of a soil member element or a hydroxide of an alkali gold group element or a mixture thereof. The adsorbent according to the embodiment of the present invention further comprises a metal carbonic acid compound wherein the content of the metal oxide is from 75% by weight to 95% by weight. The content of the metal carbonate compound is from 5% by weight to 25% by weight. According to the embodiment of the present invention, the above adsorbent, metal carbonic acid 201023969

1W 29621twf.doc/n 化合物包括鹼土族元素的碳酸化合物、鹼金族元素的碳酸 化合物或其混合物。 依照本發明實施例所述,上述之吸附劑中,吸附劑更 包括金屬氫氧化物與金屬碳酸化合物,其中金屬氧化物的 含量為30重量%〜75重量%,金屬氫氧化物的含量為20 重量%〜50重量%以及金屬碳酸化合物的含量為5重量% 〜25重量%。 本發明又提出一種吸附劑之再生循環的方法,包括提 供含金屬氧化物之吸附劑,此吸附劑已吸附二氧化複。然 後,將吸附劑在含有飽和水蒸氣與至少一種氣體的環境中 進行椴燒製程’以使吸附劑再生。之後,以已再生之吸附 劑吸附二氧化碳。 依照本發明實施例所述,上所述之吸附劑之再生循環 的方法中’金屬氧化物包括鹼土族元素的氧化物、鹼金族 元素的氧化物或其混合物。 依照本發明實施例所述,上所述之吸附劑之再生循環 • 的方法中,飽和水蒸汽和氣體的體積比值(飽和水蒸汽/氣 體)在2〜20之間。 依照本發明實施例所述,上所述之吸附劑之再生循環 的方法中’飽和水蒸汽的流量為165〜1650毫升/分鐘公 克。 依如本發明實施例所述,上所述之吸附劑之再生循環 的方法中’氣體的流量為8.25〜825毫升/分鐘公克。 依照本發明實施例所述,上所述之吸附劑之再生循環 6 201023969· 29621twf.doc/n 的方法中,氣體包括氮氣、 或其混合氣體。 依照本發明實施例所述,上所述之吸附劑之再生循環 的方法中,煅燒製程的溫度為25(rc〜1〇〇〇t&gt; 衣 依照本發明實施例所述,上所述之吸附劑之再生循環 的方法中,煅燒製程的維持時間為1〇〜4〇分鐘。 义1W 29621twf.doc/n The compound includes a carbonate compound of an alkaline earth element, a carbonic acid compound of an alkali gold group element, or a mixture thereof. According to the embodiment of the present invention, in the adsorbent, the adsorbent further comprises a metal hydroxide and a metal carbonate compound, wherein the content of the metal oxide is 30% by weight to 75% by weight, and the content of the metal hydroxide is 20%. The weight % to 50% by weight and the content of the metal carbonate compound are 5% by weight to 25% by weight. The present invention further provides a method of regenerating a sorbent comprising providing a metal oxide-containing adsorbent which has adsorbed the oxidized complex. Then, the adsorbent is subjected to a calcining process in an environment containing saturated steam and at least one gas to regenerate the adsorbent. Thereafter, carbon dioxide is adsorbed by the regenerated adsorbent. In the method of the regeneration cycle of the adsorbent described above, the metal oxide includes an oxide of an alkaline earth element, an oxide of an alkali gold element, or a mixture thereof. In the method of the regeneration cycle of the adsorbent described above, the volume ratio of saturated water vapor to gas (saturated water vapor/gas) is between 2 and 20, in accordance with an embodiment of the present invention. According to an embodiment of the present invention, the flow rate of the saturated steam in the regeneration cycle of the adsorbent described above is 165 to 1650 ml/min. According to the embodiment of the present invention, the flow rate of the gas in the regeneration cycle of the adsorbent described above is 8.25 to 825 ml/min. In the method of the regeneration cycle of the adsorbent described above in the embodiment of the present invention, the gas includes nitrogen gas or a mixed gas thereof. According to the embodiment of the present invention, in the method for regenerating the adsorbent, the temperature of the calcination process is 25 (rc~1〇〇〇t), according to the embodiment of the present invention, the adsorption is as described above. In the method of regeneration cycle of the agent, the maintenance time of the calcination process is 1 〇 to 4 〇 minutes.

依照本發明實施例所述,上所述之吸附劑之再生循環 的方法中,舞X燒製程是在常壓下進行。本發明又提出一種 再生吸附劑組成物的設備,包括反應器、溫度控制裝置、 蒸汽產生裝置、氣體供應裝置以及蒸汽分離裝置別與 反應器連接。反應器用以使已吸附二氧化碳之吸附劑2 應。溫度控制裝置用以控制反應器的溫度。蒸汽產生裝置 用以提供飽和水蒸氣至反應器中。氣體供應裝置用以提供 至少一氣體至上述反應器中。蒸汽分離裝置用以分離上述 反應器所排出之飽和水蒸氣與氣體。According to the embodiment of the present invention, in the method of regenerating the adsorbent described above, the dance X firing process is carried out under normal pressure. The present invention further provides an apparatus for regenerating a composition of a sorbent comprising a reactor, a temperature control device, a steam generating device, a gas supply device, and a vapor separation device connected to the reactor. The reactor is used to administer the adsorbent 2 to which carbon dioxide has been adsorbed. A temperature control device is used to control the temperature of the reactor. A steam generating device is used to supply saturated steam to the reactor. A gas supply means is used to supply at least one gas to the reactor. A vapor separation unit is used to separate the saturated water vapor and gas discharged from the reactor.

-氧化碳、氦氣、氖氣、氬氣 依照本發明實施例所述,上述再生吸附劑組成物的設 備中’上述反應器包括固定床型式、流體化床型式、擾動 床型式或耐高溫爐。 依照本發明實施例所述’上述再生吸附劑組成物的設 備中’上述蒸汽分離裝置包括蒸汽冷凝裝置以及流量計。 本發明提供一種吸附劑組成物具有足夠大的孔徑且 具有較高的比表面積,因此’本發明之吸附劑組成物具有 相當高的吸附量,而且可以反覆吸脫附多次的循環’並且 具有當高的轉化率,故,可以有效吸附二氧化碳。 201023969 ---------*1W 29621twf.doc/n 本發明之吸附劑的再生循環的方法,可以減少能源的 損耗’節省成本。 本發明之吸附劑的再生循環的方法,可以以簡便的製 程來製備之。 本發明之再生吸附劑的設備,其設備簡單,易取得且 成本低廉。 為讓本發明之上述特徵和優點能更明顯易懂,下文特 舉較佳實施例’並配合所附圖式,作詳細說明如下。 【實施方式】 金屬氧化物具有吸附的特性,是目前用來捕獲煙氣中 —氧化碳的一種技術。以含有金屬氧化物之吸附劑吸附二 氧化碳之後’吸附劑中的金屬氧化物將會與二氧化碳反 應’而生成金屬碳酸化合物。而金屬碳酸化合物(mco3) 於高溫下(25(TC〜1000。〇锻燒則可再生成金屬氧化物(MO) 與二氧化碳。依據此現象可以進行二氧化碳的捕獲與分 離。提濃之二氧化碳可經由壓縮於地殼内封存,或與蛇紋 石(Mg3Si205(OH)4)進行化學反應而形成穩定的礦物石, 如下式所示:- oxidizing carbon, helium, neon, argon, according to an embodiment of the present invention, in the apparatus for regenerating the adsorbent composition, the reactor comprises a fixed bed type, a fluidized bed type, a disturbed bed type or a high temperature resistant furnace. . In the apparatus for regenerating the adsorbent composition described above in accordance with an embodiment of the present invention, the vapor separation device comprises a vapor condensation device and a flow meter. The present invention provides a sorbent composition having a sufficiently large pore size and a high specific surface area, so that the sorbent composition of the present invention has a relatively high adsorption amount and can be repeatedly adsorbed and desorbed multiple times and has When the conversion rate is high, carbon dioxide can be effectively adsorbed. 201023969 ---------*1W 29621twf.doc/n The method of the regeneration cycle of the adsorbent of the present invention can reduce energy loss and save cost. The method of regenerating the adsorbent of the present invention can be prepared in a simple process. The apparatus for regenerating an adsorbent of the present invention is simple in equipment, easy to obtain, and low in cost. The above described features and advantages of the present invention will become more apparent from the following description. [Embodiment] Metal oxides have an adsorption property and are currently used to capture carbon monoxide in smoke. After adsorbing carbon dioxide with a metal oxide-containing adsorbent, the metal oxide in the adsorbent will react with carbon dioxide to form a metal carbonate compound. The metal carbonate compound (mco3) is at a high temperature (25 (TC~1000.) calcined to regenerate metal oxides (MO) and carbon dioxide. According to this phenomenon, carbon dioxide can be captured and separated. Compressed in the earth's crust or chemically reacted with serpentine (Mg3Si205(OH)4) to form a stable mineral stone, as shown in the following formula:

Mg3Si205(0H)4+ 3C02(g) 3MgC03 + 2Si02 +2H20(1) -63.6 kJ/mole C02 以氧化鈣(CaO)為例,其化學穩定性高,多次反覆利用 後仍具有較高的吸收活性。CaO捕獲二氧化碳之吸收負 載,理論上最高可達0.7857克(:02^克0&amp;0,而實際上在理 29621twf.doc/n 201023969 ,wMg3Si205(0H)4+ 3C02(g) 3MgC03 + 2Si02 +2H20(1) -63.6 kJ/mole C02 Taking calcium oxide (CaO) as an example, its chemical stability is high, and it has high absorption after repeated use. active. CaO captures the absorption load of carbon dioxide, theoretically up to 0.7857 grams (: 02^g0&amp;0, but actually in the sense of 29621twf.doc/n 201023969,w

3lW 想狀態下約有0.393克CCyi克CaO ,相對其他化學吸收劑 (0.06克C02/1克單乙醇胺(MEA),〇〇88克c〇2/1克活性 厌’ 0132克C〇2/l克石夕膠(silicagel))而言’可以以少量之 吸收體積,吸收較多的二氧化碳。而且,氧化鈣可直接在 煙氣環境下分離二氧化碳,比較沒有傳統吸收程序之易受 硫的氧化物(SOx)干擾之限制,反而可以在高溫下一併 去除SOx,且處理後煙氣中二氧化碳濃度低,再生時可以 • 產生尚純度的一氧化碳。此外,沒有危險物質存在,所用. 之CaO (生石灰)與CaC〇3 (熟石灰)較其他化學吸收劑 而言安全許多。另一方面,氧化鈣捕獲二氧化碳之設備簡 單,處理量大,目前雖未有商業化之實績,但各部分獨立 之操作,於工業界已有大型機組正在運轉,商業化較易達 成。然而,CaO經多次重複使用後有活性慢慢減弱的現象, 因此’必須時常添加新鮮的CaO以補償損失。雖然’ CaO 價格便宜、產地多可以大規模生產且取得容易,可以添加 新鮮的CaO以補償損失,但是,若能透過簡易的程序進行 Φ CaO的改質,降低活性減弱的速度,將能夠大幅降低捕獲 成本。 為能使金屬氧化物改質,減緩活性減弱之速度’本發 明在使已吸附二氧化碳之吸附劑再生的過程中,不僅利用 高溫(250°C〜1000°C)加熱的方式,並且在加熱時還通入了 飽和水蒸氣以及氣體,例如氮氣、二氧化碳、氦氣、氖氣、 氬氣或其混合氣體在常壓下(此處所述的「常壓」是指一大 氣壓或±10%左右的壓力)以進行锻燒。 9 2010239693lW thinks about 0.393g CCyi gram CaO compared to other chemical absorbents (0.06g C02/1g monoethanolamine (MEA), 〇〇88g c〇2/1g active disgusting' 0132g C〇2/l In the case of silica gel, it can absorb more carbon dioxide with a small amount of absorption. Moreover, calcium oxide can directly separate carbon dioxide in the flue gas environment, compared with the sulfur-free oxide (SOx) interference without the traditional absorption procedure, but can remove SOx at high temperature and treat carbon dioxide in the flue gas. Low concentration, can produce carbon monoxide of pure purity during regeneration. In addition, there is no hazardous material present, and CaO (lime) and CaC〇3 (slaked lime) are much safer than other chemical absorbents. On the other hand, the equipment for capturing carbon dioxide by calcium oxide is simple and has a large amount of processing. Although there is no commercialization at present, the independent operation of each part has already been operated by large units in the industrial sector, and commercialization is easier. However, CaO has a tendency to slowly decrease after repeated use, so it is necessary to add fresh CaO from time to time to compensate for the loss. Although 'CaO is cheap and the production area can be mass-produced and easy to obtain, fresh CaO can be added to compensate for the loss. However, if the Φ CaO can be modified by a simple procedure, the speed of activity reduction can be greatly reduced. Capture costs. In order to modify the metal oxide, the speed of the activity is reduced. The present invention uses not only high temperature (250 ° C ~ 1000 ° C) heating, but also heating during the regeneration of the adsorbed carbon dioxide adsorbent. Also supplied with saturated steam and a gas such as nitrogen, carbon dioxide, helium, neon, argon or a mixture thereof at normal pressure (the "normal pressure" as used herein means atmospheric pressure or ±10%) Pressure) for calcination. 9 201023969

JIW 29621twf.doc/n 更詳細地說,本發明實施例之方法可以用於已吸附二 氧化碳之吸附劑,其吸附劑中的金屬氧化物吸附二氧化碳 之後可能會形成金屬碳酸化合物。金屬碳酸化合物例如是 驗土族元素的碳酸化合物或驗金族元素的碳酸化合物或其 混合物。驗土族元素的碳酸化合物例如是碳酸鎂或碳酸約 等。鹼金族元素的碳酸化合物例如是碳酸鈉或碳酸鉀等。 在已吸附二氧化碳之吸附劑進行锻燒時,控制升溫速 度,以到達設定的锻燒溫度。到達設定的锻燒溫度之後, 仍維持在常壓,並依據不同金屬氧化物的種類’維持锻燒 一段時間,使已吸附二氧化碳之吸附劑中的金屬碳酸化合 物與飽和水蒸氣以及氣體充分反應,形成具有可以有效吸 附及脫附一乳化碳的改質的金屬氧化物,達到吸附劑再生 之目的。 在煅燒的過程中,所通入的飽和水蒸汽的流量例如是 165〜1650毫升/分鐘公克;氣體的流量例如是8 25〜825 毫升/分鐘公克。在一實施例中,飽和水蒸汽和氣體的體積 ® 比值(飽和水療汽/氣體)例如是控制在2〜20之間。在另一 實施例中,飽和水蒸汽和氣體的體積比值(飽和水蒸汽/氣 體)例如是控制在6〜14之間。升溫速度例如是在25〜4〇〇c/ 分鐘,使速度到達設定的煅燒溫度。煅燒溫度依據吸附劑 之種類的不同而有所不同,通常例如是在25〇。〇〜1〇〇〇。〇。 到達設定的煅燒溫度之後,維持煅燒的時間例如是丨分鐘 〜600分鐘。在一實施例中,吸附劑中含有氧化鈣,其吸附 二氧化碳之後形成碳酸鈣,煅燒溫度例如是75〇°c〜95〇 201023969 -------&gt;JW 29621twf.doc/n C,維持煅燒的時間為1〇分鐘〜4〇分鐘。在另一實施例中, 吸附劑中含有氧化鎂,其吸附二氧化碳之後形成碳酸鎂, 锻燒溫度例如是50(rc〜70(rc ’維持煅燒的時間為10分鐘 〜40分鐘。 a再生後之吸附劑中含有金屬氧化物。金屬氧化物例如 疋鹼土族元素的氧化物或鹼金族元素的氧化物或其混合 ,I鹼土族兀素的氧化物例如是氧化鎂或氧化鈣等。鹼金 • 族元素的氧化物例如是氧化鈉或氧化鉀耸。金屬氧化物具 有多個孔洞,孔洞的直徑例如是01奈米〜100奈米,比表 面巧為0.5〜38.28平方公尺/克。再生之吸附劑再次吸附二氧 化碳時’其吸附量至少可達到〇 25克二氧化碳八克金屬氧 化物,且可以反覆吸脫附至少1〇次的循環,轉化率可至少 達到0.3。 再生之吸附劑的形狀可以是粒狀或是粉狀。再者,再 生之吸附劑除了包括金屬氧化物之外,還可再包括殘存的 金屬碳酸化合物或金屬氫氧化物。換言之,再生之吸附劑 ❹ $括金屬氧化物及殘存的金屬碳酸化合物,或是包括金屬 氧=物及金屬氫氧化物’或是包括金屬氧化物、殘存的金 屬石反酸化合物及金屬氫氧化物。殘存的金屬碳酸化合物例 如是驗土族元素的或驗金族元素的碳酸化合物或其混合 物。鹼土族元素的碳酸化合物例如是碳酸鎂或碳酸鈣等。 驗金族元素的石炭酸化合物例如是碳酸納或礙酸鉀等。吸附 劑^金屬氫氧化合物例如是驗土族元素的或驗金族元素 的虱氧化合物或其混合物。在一實施例中,粒狀吸附劑包 11 201023969 iW 29621twf.doc/n 括75%〜95%的金屬氧化物及5%〜25%的金屬碳酸化合 物。在另一實施例中,粒狀吸附劑包括40%〜80%的金屬氧 化物及20%〜60%的金屬氫氧化物。在又一實施例中,粒狀 吸附劑包括30%〜75%的金屬氧化物以、20%〜50%的金屬 氳氧化物及5%〜25%的金屬碳酸化合物。本發明所述的 「%」,是指重量百分比。 圖1為依照本發明實施例所繪示之一種用於製備吸附 劑的設備。此設備100包括反應器10、溫度控制裝置12、 ® 蒸汽產生裝置14、氣體供應裝置16與蒸汽分離裝置18。 反應器10内用以放置已吸附二氧化碳之吸附劑。反應器 10可以採用固定床型式、流體化床型式、擾動床型式或耐 高溫爐。蒸汽產生裝置14與反應器10之間藉由管件連接, 用以提供飽和水蒸氣,以通入於反應器10中,與已吸附二 氧化碳之吸附劑反應。氣體供應裝置16與反應器1〇之間 藉由管件連接’用以將氮氣、二氧化碳、氦氣、氖氣、氬 氣或其混合氣體供應至反應器10中,與已吸附二氧化碳之 • 吸附劑反應。蒸汽產生裝置14所供應的飽和水蒸氣以及氣 體供應裝置16所供應的氣體,可以分別通入反應器1〇中 (如虛線24a與24b所示之管路),也可在通入於反應器1〇 之前先行混合(如實線26a與26b所示之管路)。為能有效 控制通入於反應器10中飽和水蒸氣或是氣體的流量,可以 在管件上設置控制閥件(未繪示)。溫度控制裝置12用以控 制反應器10的溫度,以在適當的溫度環境中,使反應器 10中已吸附二氧化碳之吸附劑與所通入的飽和水蒸氣以 12 201023969 lW 29621twf.doc/n 及氣體反應。蒸汽分離裝置18藉由管件與反應器10連接, 用以移除反應器10排出的飽和水蒸氣與氣體。在一實施例 中,在進行反應時,所通入的飽和水蒸氣以及氣體的壓力 大於常壓,反應器10中常壓的飽和水蒸氣以及氣體因正壓 而經由蒸汽分離裝置排出’因此’其蒸汽分離裝置18可不 包括泵,例如是包括蒸汽冷凝裝置20以及流量計22,即 可達到所需功效。蒸汽冷凝裝置20可用以冷凝反應器10 中所排出的飽和水蒸氣,流量計22則可測量反應器1〇所 ... ' . 排出之氣體以及無法被蒸汽冷凝裝置20冷凝的飽和水蒸 氣的流量。 由於本發明之使吸附劑再生的方法可以在常壓下進 行’系統不需要維持真空,因此,可以減少能源的損耗。 再者’由於本發明僅需使用飽和的水蒸氣和氣體來煅燒, 且锻燒的溫度可以在較低的溫度下進行,不需要使用過熱 水蒸氣’也不需要過高的煅燒溫度,或取出再磨碎等繁瑣 的程序,因此,不僅可以節省成本以及能源的損耗,且製 程相當簡便。此外,本發明上述實施例之製造吸附劑的設 備簡單、易取得且成本低廉。 實例1 將12.25克的碳酸約置於反應器中。之後,由氣體供 應裝置提供氮氣。氮氣的流量為276毫升/分鐘。反應器 的壓力為常壓,煅燒的溫度與升溫時間可以例-積分-微分 (PID)控制器設定之。煅燒的溫度為85〇。〇,升溫時間為 13 W 29621twf.doc/n 201023969 30分鐘。當反應器升溫至20(TC後,將蒸汽產生襞置所提 供的飽和蒸汽導入。飽和水蒸氣的流量為525亳升/分鐘。 萬反應斋的溫度達到850°C時,維持锻燒的時間為3〇分 鐘。結束烺燒後持續通入氮氣’直到反應管溫度降至4⑽。◦ 再取出產品。之後,對所製得的產品以掃描式電子顯微鏡 (Scanning Electron Microscope, SEM)切片分析並進行吸脫 附測試。吸脫附測試是以熱重分析儀(TGA)來分析所形成 之吸附劑(其孔控為10〜丨〇〇奈米)的氧化鈣的重量變化。 脫附是在850 c的氮氣下進行1分鐘。吸附則是在6 人 有1〇%(體積百分比,v/v)的二氧化碳下進行u分鐘。3 由SEM的結果顯示吸附劑中氧化鈣的孔徑為ι〇奈米 〜100奈米。比表面積測試儀測試’其表面積最高可達3^ 平方公y克。以TGA分析本發明實施例之氧化舞吸附劑吸 脫附一氧化碳1〇次循環的重量變化圖如圖2所示,轉化率 的變化圖如圖3所示。其結果顯示本發明之吸附劑可以反 覆吸脫附二氧化碳至少1〇次的循環,且轉化率可至少達到 0 0.3,吸附量至少為,克二氧化礙A克金屬氧化物。 比較例1 j類似^實例i的方法製造吸賴,但,不通入飽和 水蒸氣,而是直接通入氮氣。氮氣的流量為525毫升/分 鐘。 #圖4為比車又例!以及實例i所製得之吸附劑吸脫附二 氧化礙11 *循環之吸附量變化比較圖。由圖4的結果顯示 201023969JI W 29621 twf.doc/n In more detail, the method of the embodiment of the present invention can be applied to an adsorbent which has adsorbed carbon dioxide, and a metal carbonate compound may be formed after the metal oxide in the adsorbent adsorbs carbon dioxide. The metal carbonate compound is, for example, a carbonic acid compound of a soil member element or a carbonic acid compound of a gold group element or a mixture thereof. The carbonic acid compound of the soil member element is, for example, magnesium carbonate or carbonic acid. The carbonic acid compound of the alkali gold group element is, for example, sodium carbonate or potassium carbonate. When the adsorbent having adsorbed carbon dioxide is calcined, the temperature increase rate is controlled to reach the set calcination temperature. After reaching the set calcination temperature, it is maintained at normal pressure, and the calcination is maintained for a period of time according to the type of different metal oxides, so that the metal carbonate compound in the adsorbent adsorbing carbon dioxide is sufficiently reacted with saturated water vapor and gas. Forming a metal oxide having an improved adsorption and desorption of an emulsified carbon to achieve the purpose of regeneration of the adsorbent. In the calcination process, the flow rate of the saturated steam introduced is, for example, 165 to 1650 ml/min g; the flow rate of the gas is, for example, 8 25 to 825 ml/min. In one embodiment, the volume ratio of saturated steam and gas (saturated spa steam/gas) is controlled, for example, between 2 and 20. In another embodiment, the volume ratio of saturated steam and gas (saturated water vapor/gas) is controlled, for example, between 6 and 14. The temperature increase rate is, for example, 25 to 4 〇〇 c / minute, and the speed is brought to the set calcination temperature. The calcination temperature varies depending on the kind of the adsorbent, and is usually, for example, at 25 Torr. 〇~1〇〇〇. Hey. After reaching the set calcination temperature, the time for maintaining the calcination is, for example, 丨 minute to 600 minutes. In one embodiment, the adsorbent contains calcium oxide, which forms calcium carbonate after adsorbing carbon dioxide, and the calcination temperature is, for example, 75〇°c~95〇201023969-------&gt; JW 29621twf.doc/n C, The time for maintaining the calcination is 1 minute to 4 minutes. In another embodiment, the adsorbent contains magnesium oxide, which forms carbonic acid after adsorbing carbon dioxide, and the calcination temperature is, for example, 50 (rc~70 (rc' maintains the calcination time of 10 minutes to 40 minutes. The adsorbent contains a metal oxide such as an oxide of an alkalinium earth element or an oxide of an alkali gold group element or a mixture thereof, and an oxide of the alkaline earth element is, for example, magnesium oxide or calcium oxide. • The oxide of the group element is, for example, sodium oxide or potassium oxide. The metal oxide has a plurality of pores, and the diameter of the pore is, for example, 01 nm to 100 nm, and the specific surface is 0.5 to 38.28 m ^ 2 /g. When the adsorbent adsorbs carbon dioxide again, its adsorption amount can reach at least 25 grams of carbon dioxide and 8 grams of metal oxide, and can be repeatedly sucked and desorbed for at least 1 cycle, and the conversion rate can be at least 0.3. The shape of the regenerated adsorbent It may be in the form of granules or powder. In addition, the regenerated adsorbent may include, in addition to the metal oxide, residual metal carbonate or metal hydroxide. The regenerated adsorbent 括 comprises a metal oxide and a residual metal carbonate compound, or includes a metal oxygen compound and a metal hydroxide, or includes a metal oxide, a residual metalloid acid compound, and a metal hydroxide. The remaining metal carbonate compound is, for example, a carbonic acid compound of a soil group element or a gold group element or a mixture thereof. The carbonic acid compound of the alkaline earth element is, for example, magnesium carbonate or calcium carbonate, etc. The carbolic acid compound of the gold group element is, for example, sodium carbonate or Potassium acid sulphate, etc. The adsorbent metal hydroxide is, for example, an earthworm or a gold component of a gold group element or a mixture thereof. In one embodiment, the particulate adsorbent pack 11 201023969 iW 29621twf.doc/n 75%~95% metal oxide and 5%~25% metal carbonic acid compound. In another embodiment, the granular adsorbent comprises 40%~80% metal oxide and 20%~60% metal In another embodiment, the particulate adsorbent comprises 30% to 75% metal oxide, 20% to 50% metal cerium oxide, and 5% to 25% metal carbonic acid compound. Said "%" means weight percent. Figure 1 is an apparatus for preparing an adsorbent according to an embodiment of the present invention. The apparatus 100 includes a reactor 10, a temperature control device 12, a steam generating device 14, and a gas. The supply device 16 and the steam separation device 18. The adsorbent 10 is used to place the adsorbent having adsorbed carbon dioxide in the reactor 10. The reactor 10 may be a fixed bed type, a fluidized bed type, a disturbed bed type or a high temperature resistant furnace. The steam generating device 14 and The reactors 10 are connected by a tube for supplying saturated water vapor to be introduced into the reactor 10 to react with the adsorbent which has adsorbed carbon dioxide. The gas supply device 16 and the reactor 1 are connected by a pipe. 'To supply nitrogen, carbon dioxide, helium, neon, argon or a mixture thereof to the reactor 10 to react with the adsorbent which has adsorbed carbon dioxide. The saturated water vapor supplied by the steam generating device 14 and the gas supplied from the gas supply device 16 may be respectively introduced into the reactor 1 (as shown by the broken lines 24a and 24b) or may be passed into the reactor. Mix before 1〇 (as shown by the solid lines 26a and 26b). In order to effectively control the flow rate of saturated water vapor or gas introduced into the reactor 10, a control valve member (not shown) may be provided on the pipe member. The temperature control device 12 is configured to control the temperature of the reactor 10 to cause the adsorbent having adsorbed carbon dioxide in the reactor 10 and the saturated water vapor to be passed in the appropriate temperature environment to be 12 201023969 lW 29621 twf.doc/n and Gas reaction. The vapor separation unit 18 is connected to the reactor 10 by means of a tube for removing saturated water vapor and gas discharged from the reactor 10. In one embodiment, when the reaction is carried out, the saturated water vapor and the pressure of the gas are greater than the normal pressure, and the saturated water vapor at a normal pressure in the reactor 10 and the gas are discharged through the steam separation device due to the positive pressure. The steam separation unit 18 may include a pump, such as a steam condensing unit 20 and a flow meter 22, to achieve the desired efficiency. The steam condensing unit 20 can be used to condense the saturated water vapor discharged from the reactor 10, and the flow meter 22 can measure the reactor 1'. The discharged gas and the saturated water vapor which cannot be condensed by the steam condensing unit 20 flow. Since the method for regenerating the adsorbent of the present invention can be carried out under normal pressure, the system does not need to maintain a vacuum, and therefore, the loss of energy can be reduced. Furthermore, 'because the present invention only needs to use saturated steam and gas for calcination, and the temperature of calcination can be carried out at a lower temperature, without using superheated steam' and without excessively high calcination temperature, or taking out More complicated procedures such as grinding, so that not only cost and energy consumption can be saved, but the process is quite simple. Further, the apparatus for producing an adsorbent of the above embodiment of the present invention is simple, easy to obtain, and low in cost. Example 1 12.25 grams of carbonic acid was placed in the reactor. Thereafter, nitrogen gas is supplied from the gas supply device. The flow rate of nitrogen gas was 276 ml/min. The reactor pressure is atmospheric, and the calcination temperature and temperature rise time can be set by an example-integral-derivative (PID) controller. The calcination temperature was 85 Torr. 〇, the heating time is 13 W 29621twf.doc/n 201023969 30 minutes. When the reactor is heated to 20 (TC, the saturated steam supplied by the steam generation is introduced. The flow rate of the saturated steam is 525 liters/min. When the temperature of the reaction reaches 850 °C, the calcination time is maintained. After 3 minutes, the nitrogen gas was continuously supplied until the temperature of the reaction tube was lowered to 4 (10). The product was taken out, and then the product was analyzed by Scanning Electron Microscope (SEM). The adsorption and desorption test was carried out. The adsorption and desorption test was performed by a thermogravimetric analyzer (TGA) to analyze the weight change of calcium oxide formed by the adsorbent (having a pore size of 10 to 丨〇〇 nanometer). The reaction was carried out for 1 minute under nitrogen at 850 c. The adsorption was carried out for 5 minutes at 6% by volume (v/v) of carbon dioxide. 3 The results of SEM showed that the pore size of the calcium oxide in the adsorbent was ι〇 Nano ~100 nm. The specific surface area tester test 'its surface area up to 3 ^ square y grams. TGA analysis of the oxidative dance adsorbent of the embodiment of the present invention adsorption and desorption of carbon monoxide 1 〇 cycle weight change diagram Figure 2 shows the change in conversion rate The figure is shown in Figure 3. The results show that the adsorbent of the present invention can repeatedly adsorb and desorb carbon dioxide for at least one cycle, and the conversion rate can be at least 0 0.3, the adsorption amount is at least, and the gram dioxide hinders the A gram metal. Oxide. Comparative Example 1 j is similar to the method of Example i to make a wicking, but does not pass saturated steam, but directly passes nitrogen. The flow rate of nitrogen is 525 cc / min. # Figure 4 is a case of a car! And a comparison chart of the adsorption amount change of the adsorbent by the adsorption and desorption of the adsorbent prepared in the example i. The cycle of FIG. 4 shows 201023969

?iW 29621twf.doc/n 本發明實例1之朗劑可以吸瞻彡量的二氧化碳,降低 活性減弱的速度,大幅降低捕獲成本。 實例2iW 29621twf.doc/n The sizing agent of Example 1 of the present invention can absorb the amount of carbon dioxide, reduce the rate of activity reduction, and greatly reduce the cost of capture. Example 2

將12.25克的碳酸鎂置於反應器中。之後,由氣體供 應裝置提供氮氣。氮氣的流量為Μ紐/分鐘。以例_積 分-微分(PID)控制器設定反應器的目標溫度與升溫時間。 锻燒的^度為6GG°C ’升溫時間為3σ分鐘。當反應器升溫 至20巧後’將蒸汽產生裝置所提供的飽和蒸汽導入。飽 和水瘵氣的流量為525毫升/分鐘。當反應器的溫度達到 60^# ’維持锻燒的時間為3G分鐘。結束锻燒後持續通 入氮氣體,直到反應管溫度降至4〇(rc再取出產品。之後, 對所製得的產品以掃描式電子顯微鏡(Sc_ing12.25 grams of magnesium carbonate was placed in the reactor. Thereafter, nitrogen gas is supplied from the gas supply device. The flow rate of nitrogen is ΜNews/minute. The target temperature and temperature rise time of the reactor are set by the example_integration-derivative (PID) controller. The degree of calcination was 6 GG ° C 'the heating time was 3 σ minutes. When the reactor is warmed up to 20, the saturated steam supplied from the steam generating device is introduced. The flow rate of saturated helium gas was 525 ml/min. When the temperature of the reactor reached 60^#', the calcination time was maintained at 3G minutes. After the end of the calcination, the nitrogen gas was continuously introduced until the temperature of the reaction tube was lowered to 4 Torr (rc was taken out again. Thereafter, the obtained product was subjected to scanning electron microscopy (Sc_ing).

Electron Μ刪scope,SEM)切片分析並進行吸脫附測試。吸脫附測 試是以熱重分析儀(TGA)來分析吸附劑(其孔徑為〇卜刚Electron Μ cut scope, SEM) slice analysis and perform suction and desorption test. The adsorption and desorption test is a thermogravimetric analyzer (TGA) to analyze the adsorbent (the pore size is 〇卜刚

奈米)的氧化賴重量變化。脫岐在的氮氣下進 1分鐘。吸附則是在250。(:含有10%(v/v)的二氧化碳 行11分鐘。 . $ 由SEM的結果顯示吸附劑中氧化鈣的孔徑為〇 i奈米 〜1〇〇奈米。比表面積測試儀測試,其表面積最高可^ :方公尺/克。吸附量至少為心克二氧化前克金屬氧化 雖然本發明已以實施·露如上,然其並_ 本發明’任何賴赫賴巾具有通常知識者,在不脫離 15 296211wf. doc/n 201023969 &gt; 本發明之精神和範圍内,當可作些許之更動與潤飾,因此 本發明之保護範圍當視後附之申請專利範圍所界定者為 準。 【圖式簡單說明】 圖1為依照本發明實施例所繪示之一種用於製備吸附 劑的設備。 、圖一2,以TGA分析本發明—實關之氧蝴吸附劑 吸脫附一氧化碳10次循環的重量變化圖。 圖3是以TGA分析本發明—實_之氧响吸附劑 吸脫附二氧化碳10次循環的轉化率的變化圖。 圖4為比較例1以及本發明—實施例所製得化妈 吸附劑吸脫附二氧化碳n次循環之吸附量變化的比較圖。 【主要元件符號說明】 10 反應器 12 溫度控制裝置 14 蒸汽產生裝置 16 氣體供應裝置 18 蒸汽分離裝置 20 蒸汽冷凝裝置 22 流量計 24a、24b、26a、26b :管路 100 :製備吸附劑的設備 16The oxidation weight change of nano). Discharge in nitrogen for 1 minute. The adsorption is at 250. (: Contains 10% (v/v) of carbon dioxide for 11 minutes. . The results from SEM show that the pore size of calcium oxide in the adsorbent is 〇i nanometer ~1 〇〇 nanometer. Surface area tester test, its surface area The highest can be: square meters / gram. The adsorption amount is at least gram of oxidized metal before oxidation. Although the present invention has been implemented, the above is disclosed, and the present invention - any of the Reich Lai towels have the usual knowledge, in Doc/n 201023969 &gt; </ RTI> </ RTI> <RTIgt; </ RTI> <RTIgt; </ RTI> <RTIgt; </ RTI> <RTIgt; </ RTI> <RTIgt; </ RTI> <RTIgt; BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a schematic diagram of an apparatus for preparing an adsorbent according to an embodiment of the present invention. FIG. 1 is a TGA analysis of the present invention--------------------------------------- Figure 3 is a graph showing the change in conversion rate of the oxygen-absorbing adsorbent of the present invention by the TGA analysis for 10 cycles of adsorption and desorption of carbon dioxide. Figure 4 is a comparison of Comparative Example 1 and the present invention. Huama adsorbent absorbs and desorbs carbon dioxide Comparison of changes in adsorption amount of the cycle. [Explanation of main component symbols] 10 Reactor 12 Temperature control device 14 Steam generation device 16 Gas supply device 18 Vapor separation device 20 Steam condensing device 22 Flowmeters 24a, 24b, 26a, 26b: Tube Road 100: Apparatus for preparing adsorbents 16

Claims (1)

29621twf.doc/n 201023969 十、申請專利範園: ,1.種吸附劑,包括金屬氧化物,其具有直徑為〇i 奈米〜100奈米的多個孔洞,比表面積為0.5〜38.28平方公 尺/克及附至少為G.25克二氧化碳/1克金屬氧化物。 2·如申請專利範圍第1項所述之吸附劑,其中該吸附 劑之轉化率至少0.3 ’而且可以反覆吸脫附二氧化碳 10次的循環。 3. 如申請專利範圍第1項所述之吸附劑,其中該金屬 氧化物包括鹼土族元素的氧化物、鹼金族元素的氧化物 其混合物。 / 4. 如申請專利範圍第1項所述之吸附劑,更包括金屬 氫氧化物,其中該金屬氧化物的含量為40重量%〜80重 量%,該金屬氫氧化物的含量為2〇重量%〜6〇重量%。 5. 如申请專利範圍第4項所述之吸附劑,其中該金屬 氫氧化合物包括鹼土族元素的氫氧化合物或驗金族元素的 氫氧化合物或其混合物。 ® 6.如申請專利範圍第丨項所述之吸附劑,更包括金屬 奴酸化合物’其中該金屬氧化物的含量為75重量%〜95 重量%’該金屬碳酸化合物的含量為5重量%〜25重量%。 7.如申请專利範圍第6項所述之吸附劑,其中該金屬 碳酸化合物包括鹼土族元素的碳酸化合物、鹼金族元素的 碳酸化合物或其混合物。 8_如申睛專利範圍第1項所述之吸附劑,其中該吸附 劑更包括金屬氫氧化物與金屬碳酸化合物,其中該金屬氧 17 201023969, iW 29621twf.doc/n 化物的含量為30重量%〜75重量%,該金屬氫氧化物的 含量為20重量%〜5〇重量%以及該金屬碳酸化合物的含 量為5重量%〜25重量%,且其中該金屬氫氧化合物包括 驗土族元素的氫氧化合物或驗金族元素的氫氧化合物或其 混合物’該金屬碳酸化合物包括驗土族元素的碳酸化合 物、鹼金族元素的碳酸化合物或其混合物。 9. 一種吸附劑之再生循環的方法,包括: 提供含金屬氧化物之一吸附劑,該吸附劑已吸附二氧 •化碳; 將該吸附劑在含有飽和水蒸氣與至少一種氣體的環境 中進行煅燒製程,以使該吸附劑再生;以及 以已再生之該吸附劑吸附二氧化碳。 10. 如申請專利範圍第9項所述之吸附劑之再生循環 的方法’其中該金屬氧化物包括鹼土族元素的氧化物、鹼 金族元素的氧化物或其混合物。 11. 如申請專利範圍第9項所述之吸附劑之再生循環 Φ 的方法’其中該飽和水蒸汽和該氣體的體積比值(飽和水蒸 汽/氣體)在2〜20之間。 12. 如申請專利範圍第9項所述之吸附劑之再生循環 的方法,其中該飽和水蒸汽的流量為165〜1650毫升/分鐘 公克。 13. 如申請專利範圍第9項所述之吸附劑之再生循環 的方法’其中該氣體的流量為8.25〜825毫升/分鐘公克。 14. 如申請專利範圍第9項所述之吸附劑之再生循環 18 201023969,w 2962Itwf.doc/n 的方法,其中該氣體包括氮氣、 氬氣或其混合氣體。 K如申請專利範圍第9項所述之吸附劑之再生循環 的方法,其中該锻燒製程的溫度為25〇u⑼。 16. 如申請專利範圍第9項所述之吸附劑之再生循環 的方法’其巾該锻燒製輯轉時間為1G〜4〇分鐘。29621twf.doc/n 201023969 X. Application for Patent Park: 1. A kind of adsorbent, including metal oxide, which has a plurality of pores with a diameter of 〇i nm~100 nm, and a specific surface area of 0.5~38.28 square Ruler / gram and attached at least G.25 grams of carbon dioxide / 1 gram of metal oxide. 2. The adsorbent of claim 1, wherein the adsorbent has a conversion of at least 0.3 ′ and can be repeatedly adsorbed and desorbed with carbon dioxide for 10 cycles. 3. The adsorbent of claim 1, wherein the metal oxide comprises an oxide of an alkaline earth element, an oxide of an alkali gold element, and a mixture thereof. 4. The adsorbent according to claim 1, further comprising a metal hydroxide, wherein the metal oxide is contained in an amount of 40% by weight to 80% by weight, and the metal hydroxide is present in an amount of 2% by weight. %~6〇% by weight. 5. The adsorbent of claim 4, wherein the metal hydroxide comprises a hydroxide of an alkaline earth element or a hydroxide of a gold group element or a mixture thereof. 6. The adsorbent according to claim 2, further comprising a metal niacin compound wherein the content of the metal oxide is from 75% by weight to 95% by weight, and the content of the metal carbonate compound is 5% by weight. 25 wt%. 7. The adsorbent according to claim 6, wherein the metal carbonate compound comprises a carbonate compound of an alkaline earth element, a carbonic acid compound of an alkali gold element or a mixture thereof. The adsorbent according to claim 1, wherein the adsorbent further comprises a metal hydroxide and a metal carbonate compound, wherein the metal oxygen 17 201023969, iW 29621twf.doc/n compound content is 30 weight %〜75重量%, the content of the metal hydroxide is 20% by weight to 5% by weight, and the content of the metal carbonate compound is 5% by weight to 25% by weight, and wherein the metal hydroxide comprises a soil-receiving element A hydroxide or a gold hydroxide of a gold group element or a mixture thereof. The metal carbonate compound includes a carbonic acid compound of a soil group element, a carbonic acid compound of an alkali gold group element, or a mixture thereof. 9. A method of regenerating a sorbent comprising: providing an adsorbent comprising a metal oxide, the adsorbent having adsorbed dioxin carbon; the adsorbent being in an environment containing saturated steam and at least one gas A calcination process is performed to regenerate the adsorbent; and carbon dioxide is adsorbed by the adsorbent that has been regenerated. 10. The method of the regeneration cycle of the adsorbent according to claim 9 wherein the metal oxide comprises an oxide of an alkaline earth element, an oxide of an alkali metal element or a mixture thereof. 11. The method of the regeneration cycle Φ of the adsorbent according to claim 9 wherein the volume ratio of the saturated steam to the gas (saturated water vapor/gas) is between 2 and 20. 12. The method of regenerating a sorbent according to claim 9, wherein the saturated water vapor has a flow rate of 165 to 1650 ml/min. 13. The method of the regeneration cycle of the adsorbent according to claim 9 wherein the flow rate of the gas is 8.25 to 825 ml/min. 14. The method of claim 9, wherein the gas comprises nitrogen, argon or a mixture thereof. K. A method of regenerating a sorbent according to claim 9 wherein the temperature of the calcination process is 25 〇u (9). 16. The method of regenerating the adsorbent according to claim 9 of the patent application, wherein the smelting cycle time is 1 G to 4 minutes. 17. 如申請專利範圍第9項所述之吸附劑之再生循環 的方法,其中該煅燒製程是在常壓下進行。 18. —種再生吸附劑的設備,包括: 一反應器,用以使一已吸附二氧化碳之吸附劑反應; 一溫度控制裝置,與該反應器連接,用以控制該反應 器的溫度; 一蒸汽產生裝置,與該反應器連接,用以提供一飽和 水蒸氣至該反應器中; 一氣體供應裝置,與該反應器連接,用以提供至少一 氣體至該反應器中;以及17. The method of regenerating a sorbent according to claim 9, wherein the calcining process is carried out under normal pressure. 18. An apparatus for regenerating an adsorbent, comprising: a reactor for reacting an adsorbent having adsorbed carbon dioxide; a temperature control device coupled to the reactor for controlling a temperature of the reactor; a generating device coupled to the reactor for supplying a saturated water vapor to the reactor; a gas supply device coupled to the reactor for supplying at least one gas to the reactor; —氧化碳、氦氣、氖氣、 一蒸汽分離裝置,與該反應器連接,用以分離該反應 器所排出之該飽和水蒸氣與該氣體。 19. 如申請專利範圍第18項所述之再生吸附劑的設 備,其中該反應器包括固定床型式、流體化床型式、擾動 床型式或耐高溫爐。 20.如申請專利範圍第18項所述之再生吸附劑的設 備’其中該蒸汽分離裝置包括蒸汽冷凝裝置以及流量計。 19- Carbon oxide, helium, neon, and a vapor separation unit connected to the reactor for separating the saturated water vapor and the gas discharged from the reactor. 19. The apparatus for regenerating an adsorbent of claim 18, wherein the reactor comprises a fixed bed type, a fluidized bed type, a disturbed bed type or a high temperature resistant furnace. 20. The apparatus for regenerating a sorbent according to claim 18, wherein the vapor separation device comprises a vapor condensing device and a flow meter. 19
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