JP6760583B2 - How to make activated carbon - Google Patents

How to make activated carbon Download PDF

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JP6760583B2
JP6760583B2 JP2016120071A JP2016120071A JP6760583B2 JP 6760583 B2 JP6760583 B2 JP 6760583B2 JP 2016120071 A JP2016120071 A JP 2016120071A JP 2016120071 A JP2016120071 A JP 2016120071A JP 6760583 B2 JP6760583 B2 JP 6760583B2
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activated carbon
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alkali
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岡本 正行
正行 岡本
奥谷 猛
猛 奥谷
充 大西
充 大西
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Japan Aerospace Exploration Agency JAXA
Shinwa Corp
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Description

本発明は、シリカを含む植物原料(ケイ素集積バイオマス)から活性炭を製造する方法、及び活性炭製造システムに関する。 The present invention relates to a method for producing activated carbon from a plant raw material (silicon-accumulated biomass) containing silica, and an activated carbon production system.

活性炭は気体および液体中の有害物質の吸着剤、触媒担体、イオン分子を吸脱着させて充電と放電を繰り返すことができるキャパシターなどに利用されている。 Activated carbon is used as an adsorbent for harmful substances in gases and liquids, a catalyst carrier, and a capacitor capable of repeatedly charging and discharging by adsorbing and desorbing ionic molecules.

活性炭は、有機物を炭化および賦活させて製造される。原料の有機物としては、植物系、たとえば木材、鋸屑、やし殻、パルプ廃液など、ならびに石炭・石油系、たとえば石炭、石油重質油、石炭および石油系ピッチ、合成高分子などがある。これらの有機物は、炭素のほかに酸素、水素などの元素を含む。 Activated carbon is produced by carbonizing and activating organic matter. Organic substances as raw materials include plant-based substances such as wood, sawdust, coconut shells, and pulp waste liquid, as well as coal-petroleum-based substances such as coal, petroleum heavy oil, coal and petroleum-based pitch, and synthetic polymers. In addition to carbon, these organic substances contain elements such as oxygen and hydrogen.

炭化工程は、原料の有機物を熱処理して炭素が濃縮された炭化物を作製し、活性炭の基本的な孔隙構造を作るために行われる。賦活工程は、上記炭化物から、より発達した孔隙構造をもつ多孔質の活性炭を作製するために行われる。賦活法には、薬品賦活法とガス賦活法とがある。 The carbonization step is performed to heat-treat the organic matter of the raw material to produce a carbon-concentrated carbide to form the basic pore structure of the activated carbon. The activation step is carried out to prepare a porous activated carbon having a more developed pore structure from the above-mentioned carbide. The activation method includes a chemical activation method and a gas activation method.

薬品賦活法は、炭化物に、塩化亜鉛、リン酸、塩化カルシウム、硫化カルシウムなどの賦活薬品を適切な質量比で含浸させ、不活性ガス中で加熱して、脱水および炭素引き抜きを伴う酸化反応により細孔を増加させる方法である。 In the chemical activation method, carbides are impregnated with an activator such as zinc chloride, phosphoric acid, calcium chloride, and calcium sulfide in an appropriate mass ratio, heated in an inert gas, and subjected to an oxidation reaction involving dehydration and carbon extraction. This is a method of increasing pores.

ガス賦活法は、炭化物を、水蒸気、二酸化炭素、酸素などのガスと接触反応させる方法である。ガス賦活法では以下のような経過をたどって炭化物の孔隙構造が発達する。まず、初期の加熱過程で、炭化物は未組織化部分(細孔が発達していない部分)が選択的に分解され、炭化物内部の閉ざされた細孔が開放されることによって内部表面積の増加がもたらされる。次に、微細な細孔の周囲の炭素が反応して、孔径の大きな細孔が形成される。 The gas activation method is a method in which a carbide is contact-reacted with a gas such as water vapor, carbon dioxide, or oxygen. In the gas activation method, the pore structure of carbide develops through the following process. First, in the initial heating process, the unassembled portion (the portion where the pores are not developed) of the carbide is selectively decomposed, and the closed pores inside the carbide are opened, so that the internal surface area is increased. Brought to you. Next, the carbon around the fine pores reacts to form pores with a large pore diameter.

優れた活性炭吸着剤は、単位量当たりの吸着容量が大きく、吸着速度が大きいことが好ましく、そのためには比表面積が大きく、吸着種に適した径の細孔を均一に多数有することが望ましい。 An excellent activated carbon adsorbent preferably has a large adsorption capacity per unit amount and a large adsorption rate, and for that purpose, it is desirable that it has a large specific surface area and uniformly has a large number of pores having a diameter suitable for the adsorbed species.

たとえば、石油コークスから水酸化カリウムを用いた薬品賦活法により、3000m/g以上のBET比表面積をもつ活性炭が製造されることが報告されている(非特許文献1、特許文献1)。 For example, it has been reported that activated carbon having a BET specific surface area of 3000 m 2 / g or more is produced from petroleum coke by a chemical activation method using potassium hydroxide (Non-Patent Document 1 and Patent Document 1).

また、原料である籾殻などのケイ素集積バイオマスをアルカリ金属化合物と混合して焼成してアルカリ賦活し、シリカをケイ酸アルカリとして溶出除去させることにより、2000〜4000m/gの比表面積をもつ多孔質シリカ−炭素複合材料を製造する方法が知られている(特許文献2)。また、ケイ素を含む植物由来の材料を酸またはアルカリで処理することによって多孔質炭素材料を製造する方法が知られている(特許文献3)。なお、薬品賦活法であるKOH賦活と、ガス賦活法であるHO(水蒸気)賦活とを比較すると、以下のような違いがあることが知られている。すなわち、KOH賦活では、炭素を消費しなくても比表面積が増加し、細孔径2nm以上の細孔が多くなる。 In addition, silicon-accumulated biomass such as rice husks, which is a raw material, is mixed with an alkali metal compound and fired to activate alkali, and silica is eluted and removed as alkali silicate to form a porous material with a specific surface area of 2000 to 4000 m 2 / g. A method for producing a quality silica-carbon composite material is known (Patent Document 2). Further, a method for producing a porous carbon material by treating a plant-derived material containing silicon with an acid or an alkali is known (Patent Document 3). Note that the KOH activation is chemical activation method, comparing the H 2 O (steam) activation is a gas activation method, it is known that there are differences as follows. That is, in KOH activation, the specific surface area increases without consuming carbon, and the number of pores having a pore diameter of 2 nm or more increases.

一方、HO賦活では、炭素を消費することによってのみ比表面積が増加し、細孔径2nm以下の細孔が生成しやすいが、細孔径2nm以上の細孔はほとんど生成しない(非特許文献2)。 On the other hand, the H 2 O activated, increases the specific surface area only by consuming carbon, easily generates the following pore pore diameter 2nm, but pores over pore diameter 2nm does not generate almost (Non-Patent Document 2 ).

米国特許第4082694号明細書U.S. Pat. No. 4,082,694 特許第2506600号公報Japanese Patent No. 2506600 特許第4618308号公報Japanese Patent No. 4618308

H.Marsh,D.Crawford,Carbon,20,419(1982)H. Marsh, D.M. Crawford, Carbon, 20,419 (1982) 真田雄三、鈴木基之、藤本薫編、新版活性炭 基礎と応用、講談社サイエンティフィク、p.68(2000)Yuzo Sanada, Motoyuki Suzuki, Kaoru Fujimoto, New Edition Activated Carbon Basics and Applications, Kodansha Scientific, p. 68 (2000)

優良な活性炭は、高比表面積で吸着速度が大きく、吸着種に適した径をもつ細孔が多く存在する。活性炭の細孔分布は、原料、炭化の温度などの条件、賦活方法と温度などの条件に左右される。従来の方法に従って、ケイ素集積バイオマスを炭化し、得られた炭化物とアルカリ金属化合物(水酸化カリウムなど)とを混合し、炭素分をアルカリ賦活し、かつシリカを除去することにより、高比表面積の活性炭を得ることができる。得られる活性炭の細孔は、マクロ孔(細孔径50nm以上)、メソ孔(細孔径2〜50nm)、およびミクロ孔(細孔径2nm以下)の領域に広く分布している。 A good activated carbon has a high specific surface area, a high adsorption rate, and many pores having a diameter suitable for the adsorbed species. The pore distribution of activated carbon depends on conditions such as raw material, carbonization temperature, activation method and temperature. A high specific surface area is obtained by carbonizing silicon-accumulated biomass according to a conventional method, mixing the obtained carbide with an alkali metal compound (potassium hydroxide, etc.), activating the carbon component with an alkali, and removing silica. Activated carbon can be obtained. The pores of the obtained activated carbon are widely distributed in the regions of macropores (pore diameter 50 nm or more), mesopores (pore diameter 2 to 50 nm), and micropores (pore diameter 2 nm or less).

しかし、このような活性炭では、細孔径2nm以下のミクロ孔の比率が小さいため、ガス吸着には適していない。そこで、本発明の課題は、ガス吸着に適した活性炭を製造することができる方法、及び活性炭製造システムを提供することにある。 However, such activated carbon is not suitable for gas adsorption because the ratio of micropores having a pore diameter of 2 nm or less is small. Therefore, an object of the present invention is to provide a method capable of producing activated carbon suitable for gas adsorption and an activated carbon production system.

本発明に係る活性炭の製造方法は、ケイ素集積バイオマスを炭化して炭化物を得る工程と、前記炭化物にアルカリ化合物を混合してアルカリ賦活するとともにケイ素を反応させてケイ酸アルカリを生成させた後、前記ケイ酸アルカリを除去して多孔質炭素材料を得る工程と、前記多孔質炭素材料をガス賦活して、活性炭を得る工程とを有することを特徴とする。また、本発明においては活性炭製造システムを提供する。 The method for producing activated carbon according to the present invention comprises a step of carbonizing silicon-accumulated biomass to obtain carbides, and mixing an alkali compound with the carbides to activate alkali and reacting silicon to generate alkali silicate. It is characterized by having a step of removing the alkali silicate to obtain a porous carbon material and a step of gas-activating the porous carbon material to obtain activated carbon. The present invention also provides an activated carbon production system.

本発明では、籾殻などのケイ素集積バイオマスを炭化し、次に炭化物をアルカリ金属化合物で賦活し、シリカをケイ酸アルカリとして除去することによって高比表面積の活性炭を得た後、さらにガス賦活を行うことによって高比表面積をもち、かつミクロ孔が発達した活性炭を製造することができる。したがって、本発明の方法によれば、高比表面積で、ミクロ孔の比率が高いので、ガス吸着に適した活性炭を製造することができる。 In the present invention, silicon-accumulated biomass such as rice husks is carbonized, then the carbides are activated with an alkali metal compound, and activated carbon having a high specific surface area is obtained by removing silica as an alkali silicate, and then gas activation is further performed. As a result, activated carbon having a high specific surface area and developed micropores can be produced. Therefore, according to the method of the present invention, since the specific surface area is high and the ratio of micropores is high, activated carbon suitable for gas adsorption can be produced.

以下、本発明の実施形態を説明する。
原料としては、高比表面積活性炭が期待できる、籾殻、稲藁、サトウキビ、トウモロコシ、竹などのケイ素集積バイオマスを用いる。ここでは、籾殻を例に説明する。籾殻は、質量%で、71〜87%の有機物(セルロース、ヘミセルロース、リグニンなど)、13〜29%の無機質を含む組成を有する。無機質は、87〜97%のシリカ、3〜13%の他の酸化物(酸化ナトリウム、酸化カリウム、アルミナなど)を含む。これらの成分の割合は、稲の種類、産地に依存しない(L.Sun,K.Gong,Silicon−Based Materials from Rice Hucks and Their Application,Ind.Eng.Chem.Res.2001,40,5861−5877)。
Hereinafter, embodiments of the present invention will be described.
As a raw material, silicon-accumulated biomass such as rice husk, rice straw, sugar cane, corn, and bamboo, which can be expected to have a high specific surface area activated carbon, is used. Here, rice husks will be described as an example. Rice husks have a composition containing 71-87% organic matter (cellulose, hemicellulose, lignin, etc.) and 13-29% inorganic matter in mass%. Inorganic substances include 87-97% silica and 3-13% other oxides (sodium oxide, potassium oxide, alumina, etc.). The ratio of these components does not depend on the type of rice and the place of origin (L. Sun, K. Kong, Silicon-Based Materials from Rice Hucks and Their Application, Ind. Eng. Chem. Res. 2001, 40, 5861-5877. ).

本発明においては、ケイ素集積バイオマス中のシリカの含有率は、質量%で0.1%以上であればよい。まず、原料であるケイ素集積バイオマスに含まれる有機物を非酸化性ガス中で熱処理することによって炭化して炭化物を得る。なお、炭化処理の前に原料中の有機質以外の不純物を酸洗浄によって除去してもよいし、酸洗浄を行わずに原料をそのまま炭化処理してもよい。炭化処理により、セルロースなどの有機物が分解して気体状の分解物が生成する。 In the present invention, the content of silica in the silicon-accumulated biomass may be 0.1% or more in mass%. First, the organic matter contained in the silicon-accumulated biomass, which is a raw material, is heat-treated in a non-oxidizing gas to carbonize it to obtain a carbide. Impurities other than organic substances in the raw material may be removed by acid cleaning before the carbonization treatment, or the raw material may be carbonized as it is without acid cleaning. The carbonization treatment decomposes organic substances such as cellulose to produce gaseous decomposition products.

炭化処理は、静止または空間速度0.1min−1以上好ましくは0.3〜1min−1の、不活性ガス気流中または酸素が消費された燃焼ガス中で行う。炭化処理の温度は、500〜1000℃、好ましくは500〜800℃とする。所定温度まで、1℃/min以上好ましくは5〜20℃/minの昇温速度で昇温する。所定温度到達後の保持時間は0〜5時間、好ましくは0〜2時間とする。こうした炭化処理の結果として得られる炭化物中の炭素とシリカとの含有率は、不純物を含む炭化物では炭素50〜60%、シリカ50〜40%、不純物を除去した炭化物では炭素約50%、シリカ約50%となる。 The carbonization treatment is carried out in an inert gas stream or in a combustion gas in which oxygen is consumed, at rest or at a space velocity of 0.1 min -1 or more, preferably 0.3 to 1 min -1 . The temperature of the carbonization treatment is 500 to 1000 ° C, preferably 500 to 800 ° C. The temperature is raised to a predetermined temperature at a rate of 1 ° C./min or more, preferably 5 to 20 ° C./min. The holding time after reaching the predetermined temperature is 0 to 5 hours, preferably 0 to 2 hours. The content of carbon and silica in the carbides obtained as a result of such carbide treatment is 50 to 60% carbon and 50 to 40% silica for carbides containing impurities, and about 50% carbon and about 50% silica for carbides from which impurities have been removed. It will be 50%.

次に、得られた炭化物とアルカリ化合物とを混合して熱処理することによって、アルカリ賦活を行うとともに、シリカをアルカリ化合物と反応させてケイ酸アルカリを生成させる。 Next, the obtained carbide and the alkali compound are mixed and heat-treated to activate the alkali, and the silica is reacted with the alkali compound to generate an alkali silicate.

アルカリ化合物としては、カリウム、ナトリウム、リチウムなどの、水酸化物、炭酸物、炭酸水素物、塩化物、硫酸物、硝酸物などが挙げられる。アルカリ化合物の形態は、水溶液状、粉末状、または径が5mm以下の粒状のいずれでもよい。炭化物へのアルカリ化合物の添加量は、シリカ除去のためには、炭化物中のシリカ1molに対してアルカリ化合物中に含まれるアルカリ金属換算で2〜10当量、好ましくは2〜5当量、アルカリ賦活のためには、炭化物中の炭素1molに対してアルカリ化合物中に含まれるアルカリ金属換算で0.1〜10当量、好ましくは1〜4当量である。炭化物へのアルカリ化合物の添加量は、シリカ除去のために添加量とアルカリ賦活のための添加量との合計とする。 Examples of the alkaline compound include hydroxides, carbonates, hydrogencarbonates, chlorides, sulfates, nitric acids and the like such as potassium, sodium and lithium. The form of the alkaline compound may be an aqueous solution, a powder, or a granular compound having a diameter of 5 mm or less. The amount of the alkali compound added to the carbide is 2 to 10 equivalents, preferably 2 to 5 equivalents, of alkali activation, in terms of alkali metal contained in the alkali compound, with respect to 1 mol of silica in the carbide for removing silica. For this purpose, it is 0.1 to 10 equivalents, preferably 1 to 4 equivalents, in terms of alkali metal contained in the alkali compound with respect to 1 mol of carbon in the carbide. The amount of the alkaline compound added to the carbide is the sum of the amount added for removing silica and the amount added for alkali activation.

炭化物とアルカリ化合物との混合物をニッケルるつぼに入れて熱処理する。この熱処理は、静止または空間速度0.1min−1以上好ましくは空間速度0.3〜1min−1の窒素、アルゴンなどの不活性ガス中で行う。熱処理温度は、アルカリ化合物の融点以上、好ましくは500℃以上で1000℃以下、より好ましくは700〜900℃とする。所定温度まで、1℃/min以上好ましくは5〜20℃/minの昇温速度で昇温する。所定温度到達後の保持時間は0〜5時間、好ましくは0〜2時間とする。 A mixture of carbide and alkaline compound is placed in a nickel crucible and heat treated. This heat treatment is carried out at rest or in an inert gas such as nitrogen or argon having a space velocity of 0.1 min -1 or more, preferably a space velocity of 0.3 to 1 min -1 . The heat treatment temperature is equal to or higher than the melting point of the alkaline compound, preferably 500 ° C. or higher and 1000 ° C. or lower, more preferably 700 to 900 ° C. The temperature is raised to a predetermined temperature at a rate of 1 ° C./min or more, preferably 5 to 20 ° C./min. The holding time after reaching the predetermined temperature is 0 to 5 hours, preferably 0 to 2 hours.

シリカとアルカリ化合物との反応は、アルカリ化合物が水酸化カリウムまたは水酸化ナトリウムである場合でそれぞれ下記の反応式で表される。
SiO+2KOH → KSiO+H
SiO+2NaOH → NaSiO+H
The reaction between silica and an alkaline compound is represented by the following reaction formula when the alkaline compound is potassium hydroxide or sodium hydroxide, respectively.
SiO 2 + 2KOH → K 2 SiO 3 + H 2 O
SiO 2 + 2 NaOH → Na 2 SiO 3 + H 2 O

これらの反応によりシリカからケイ酸アルカリが生成する。ケイ酸アルカリは水に可溶なので、炭素から分離できる。熱処理後、室温まで放冷する。試料に水を加えて煮沸し、ケイ酸アルカリを溶解させる。煮沸はケイ酸アルカリが溶解するまで行う。煮沸時間は30分〜2時間、好ましくは30分〜1時間とする。その後、ろ過して活性炭を残渣として得る。得られた活性炭を、水で洗浄して乾燥する。洗浄には、30℃程度の温水を用いることが好ましい。洗浄はろ液のpHが約7.0になるまで行う。乾燥は、80〜100℃、30分〜2時間、大気圧下または0.01013MPa(0.1atm)以下の減圧下、好ましくは100℃、30分〜1時間、約0.01013MPaの減圧下で行う。 Alkali silicate is produced from silica by these reactions. Alkali silicate is soluble in water and can be separated from carbon. After heat treatment, allow to cool to room temperature. Add water to the sample and boil to dissolve the alkali silicate. Boil until the alkali silicate dissolves. The boiling time is 30 minutes to 2 hours, preferably 30 minutes to 1 hour. Then, it is filtered to obtain activated carbon as a residue. The obtained activated carbon is washed with water and dried. It is preferable to use warm water of about 30 ° C. for washing. Washing is performed until the pH of the filtrate reaches about 7.0. Drying is performed at 80 to 100 ° C. for 30 minutes to 2 hours under atmospheric pressure or under reduced pressure of 0.01013 MPa (0.1 atm) or less, preferably at 100 ° C. for 30 minutes to 1 hour under reduced pressure of about 0.01013 MPa. Do.

得られた多孔質炭素材料(アルカリ賦活活性炭)は、比表面積が2000〜4000m/gであり、細孔がマクロ孔(細孔径50nm以上)、メソ孔(細孔径2〜50nm)、およびミクロ孔(細孔径2nm以下)の領域に広く分布した細孔分布を示す。 The obtained porous carbon material (alkali-activated activated carbon) has a specific surface area of 2000 to 4000 m 2 / g, and has macropores (pore diameter of 50 nm or more), mesopores (pore diameter of 2 to 50 nm), and micropores. It shows a pore distribution widely distributed in a region of pores (pore diameter 2 nm or less).

次に、得られたアルカリ賦活活性炭にガス賦活を施す。ガス賦活は、水蒸気、二酸化炭素、酸素などのガスを含む雰囲気中の熱処理することによって行う。
炭素とこれらのガスとの反応は以下のとおりである。
水蒸気の場合
C+HO → CO+H C+2HO → CO+2H
二酸化炭素の場合
C+CO → 2CO
酸素の場合
C+O → CO 2C+O → 2CO
Next, the obtained alkali-activated activated carbon is gas-activated. Gas activation is performed by heat treatment in an atmosphere containing a gas such as water vapor, carbon dioxide, or oxygen.
The reaction between carbon and these gases is as follows.
In the case of water vapor C + H 2 O → CO + H 2 C + 2H 2 O → CO 2 + 2H 2
In the case of carbon dioxide C + CO 2 → 2CO
In the case of oxygen C + O 2 → CO 2 2C + O 2 → 2CO

これらの反応によりアルカリ賦活活性炭から炭素を引き抜くことによって、径が2nm以下である細孔を増加させる。上記の反応のうち、水蒸気または二酸化炭素を用いる反応は吸熱反応であるが、酸素を用いる反応は発熱反応である。発熱反応は温度制御が難しいので、水蒸気または二酸化炭素を用いてガス賦活を行うことが好ましい。 By abstracting carbon from the alkaline activated carbon by these reactions, the pores having a diameter of 2 nm or less are increased. Of the above reactions, the reaction using water vapor or carbon dioxide is an endothermic reaction, while the reaction using oxygen is an exothermic reaction. Since it is difficult to control the temperature of the exothermic reaction, it is preferable to activate the gas using steam or carbon dioxide.

反応は水蒸気または二酸化炭素が炭素と接触することによって開始される。この際、HOまたはCOの分子径が、生成する細孔の径に影響を及ぼす。HOおよびCOのファンデルヴァールス径は、それぞれ4.82Åおよび5.26Åなので、径の小さい細孔を作るためには、HOを用いることが好ましい。 The reaction is initiated by the contact of water vapor or carbon dioxide with carbon. At this time, the molecular diameter of H 2 O or CO 2 affects the diameter of the pores to be formed. Since the van der Waals diameters of H 2 O and CO 2 are 4.82 Å and 5.26 Å, respectively, it is preferable to use H 2 O in order to form pores having a small diameter.

これらの点を考慮して、ガス賦活を不活性ガス−水蒸気混合ガス気流中で行う場合には以下のような条件を採用する。不活性ガス−水蒸気混合ガスの流量は、空間速度0.01〜100min−1以上、好ましくは1〜50min−1とする。水蒸気の供給量は炭素1molに対して、毎分0.01〜1mol、好ましくは毎分0.05〜0.5molとする。ガス賦活の温度は、500〜1000℃とする。500℃未満ではガス賦活が不十分になる。500〜1000℃の範囲でガス賦活を行うと、高い比表面積を得るのに有利になる。これは、ミクロ孔の比率が高くなるためであると考えられる。ただし、1000℃を超える温度でガス賦活しても、ミクロ孔の比率を高める効果は飽和する。好ましいガス賦活の温度は、700〜900℃である。所定温度まで、1℃/min以上好ましくは5〜20℃/minの昇温速度で昇温する。所定温度到達後の保持時間は0〜5時間、好ましくは1分〜2時間とする。保持時間が長くなるほど細孔径が大きくなる傾向があるので、保持時間を長くすることは避けることが好ましい。 In consideration of these points, the following conditions are adopted when the gas activation is performed in an inert gas-steam mixed gas stream. Inert gas - flow rate of the water vapor mixed gas space velocity 0.01~100Min -1 or higher, preferably 1~50min -1. The amount of water vapor supplied is 0.01 to 1 mol per minute, preferably 0.05 to 0.5 mol per minute, relative to 1 mol of carbon. The temperature of gas activation is 500 to 1000 ° C. Below 500 ° C, gas activation becomes insufficient. Gas activation in the range of 500 to 1000 ° C. is advantageous for obtaining a high specific surface area. It is considered that this is because the ratio of micropores is high. However, even if the gas is activated at a temperature exceeding 1000 ° C., the effect of increasing the ratio of micropores is saturated. The preferred gas activation temperature is 700-900 ° C. The temperature is raised to a predetermined temperature at a rate of 1 ° C./min or more, preferably 5 to 20 ° C./min. The holding time after reaching the predetermined temperature is 0 to 5 hours, preferably 1 minute to 2 hours. Since the pore diameter tends to increase as the holding time increases, it is preferable to avoid lengthening the holding time.

以上のようにして得られる活性炭(アルカリ賦活−ガス賦活活性炭)は、高比表面積で、ガス吸着に適したミクロ孔の比率が高いので、ガス吸着に有利に適用することができる。得られた活性炭粉体は、用途に応じて造粒、成形してもよい。また、当該活性炭は、ケイ素集積バイオマスを炭化して炭化物を得る炭化物取得部と、前記炭化物にアルカリ化合物を混合してアルカリ賦活するとともにケイ素を反応させてケイ酸アルカリを生成させた後、前記ケイ酸アルカリを除去して多孔質炭素材料を得る多孔質炭素材料取得部と、前記多孔質炭素材料をガス賦活して活性炭を得る活性炭取得部とを備える活性炭製造システムにて成形されることとなる。なお、活性炭製造システムは、炭化物取得部、多孔質炭素材料取得部及び活性炭取得部を一体的に備えて構成されていてもよく、各部が分離した状態で構成されていてもよい。また、本発明に支障を与えない範囲で、活性炭製造システムは他の機能部を備えてもよい。 The activated carbon obtained as described above (alkali-activated-gas-activated activated carbon) has a high specific surface area and a high proportion of micropores suitable for gas adsorption, and thus can be advantageously applied to gas adsorption. The obtained activated carbon powder may be granulated and molded according to the intended use. Further, the activated carbon has a carbide acquisition unit that carbonizes silicon-accumulated biomass to obtain carbides, and an alkali compound is mixed with the carbides to activate alkali, and silicon is reacted to generate alkali silicate, and then the silica is produced. It will be molded by an activated carbon production system including a porous carbon material acquisition unit for removing acid alkali to obtain a porous carbon material and an activated carbon acquisition unit for gas activating the porous carbon material to obtain activated carbon. .. The activated carbon production system may be configured by integrally including a carbide acquisition unit, a porous carbon material acquisition unit, and an activated carbon acquisition unit, or may be configured in a state in which each portion is separated. Further, the activated carbon production system may be provided with other functional parts as long as it does not interfere with the present invention.

以下、本発明の実施例を説明する。表1における実施例1Aに関して、原料として50gの生の籾殻をビーカーに採り、これに500mLの蒸留水を加えて30分洗浄し、その後1000mLの蒸留水で洗い流し、100℃のオーブンで24時間乾燥させた。乾燥させた籾殻を100℃のオーブンで1時間真空乾燥させた。乾燥質量で50gの洗浄済み籾殻に、80mLの塩酸(試薬特級)と920mLの蒸留水とを混合した濃度3%HCl(v/v)の塩酸水溶液を加えて加熱し、溶液が沸騰してから2時間還流を行い(リーチング)、溶液が冷めてから吸引ろ過を行った。その後、籾殻を、ろ液がpH7程度になるまで蒸留水約8Lで洗浄した後、100℃のオーブンで24時間乾燥させた。
Hereinafter, examples of the present invention will be described. Regarding Example 1A in Table 1, 50 g of raw rice husks were taken as a raw material in a beaker, 500 mL of distilled water was added thereto, and the mixture was washed for 30 minutes, then rinsed with 1000 mL of distilled water, and dried in an oven at 100 ° C. for 24 hours. I let you. The dried rice husks were vacuum dried in an oven at 100 ° C. for 1 hour. To 50 g of washed rice husks by dry mass, add an aqueous solution of hydrochloric acid having a concentration of 3% HCl (v / v), which is a mixture of 80 mL of hydrochloric acid (special grade reagent) and 920 mL of distilled water, and heat the solution. Distillation was carried out for 2 hours (reaching), and suction filtration was performed after the solution had cooled. Then, the rice husks were washed with about 8 L of distilled water until the filtrate became about pH 7, and then dried in an oven at 100 ° C. for 24 hours.

洗浄・リーチング処理後の乾燥質量で15g(容積150cc)の籾殻(leached rice hulls:LRH)を電気炉に入れた。電気炉の内部を窒素で3回置換した後、窒素気流100mL/min、昇温速度5℃/minで700℃まで昇温し、700℃で1時間保持し、炭化処理を行い、自然放熱することによって籾殻炭化物を得た。籾殻炭化物の組成は、炭素:48.58%、SiO:51.42%、KO等の不純物:0.05%であった。
乾燥質量で4gの籾殻炭化物と16gのKOHとをニッケルるつぼに入れて1分間混合した後、70℃のオーブンで2時間熟成させ、混合物を電気炉に入れた。電気炉の内部を窒素で3回置換した後、窒素気流100mL/min、昇温速度5℃/minで700℃まで昇温し、700℃で1時間保持し、アルカリ賦活を行うとともにシリカを反応させてケイ酸アルカリを生成させ、自然放熱させた。処理後の試料に約200mLの蒸留水を加えて30分間加熱して煮沸させ、ケイ酸アルカリを溶解させ、吸引ろ過してケイ酸アルカリを除去して固形物を得た。得られた固形物を、ろ液がpH7程度になるまで温水約8Lで洗浄した後、100℃のオーブンで1時間真空乾燥させてKOH賦活籾殻活性炭を得た。
Rice husks (leached rice hills: LRH) having a dry mass of 15 g (volume 150 cc) after the washing and leaching treatment were placed in an electric furnace. After replacing the inside of the electric furnace with nitrogen three times, the temperature is raised to 700 ° C at a nitrogen flow rate of 100 mL / min and a heating rate of 5 ° C / min, held at 700 ° C for 1 hour, carbonized, and naturally dissipated. As a result, rice husk carbide was obtained. The composition of rice husk carbide, carbon: 48.58%, SiO 2: 51.42 %, K 2 O , etc. impurities: was 0.05%.
A dry mass of 4 g of rice husk carbide and 16 g of KOH were placed in a nickel crucible and mixed for 1 minute, then aged in an oven at 70 ° C. for 2 hours, and the mixture was placed in an electric furnace. After replacing the inside of the electric furnace with nitrogen three times, the temperature is raised to 700 ° C. at a nitrogen flow rate of 100 mL / min and a heating rate of 5 ° C./min, and the temperature is maintained at 700 ° C. for 1 hour to activate alkali and react silica. The mixture was allowed to generate alkali silicate and naturally dissipated heat. About 200 mL of distilled water was added to the treated sample, and the sample was heated for 30 minutes to boil to dissolve the alkali silicate, and suction filtration was performed to remove the alkali silicate to obtain a solid substance. The obtained solid was washed with about 8 L of warm water until the filtrate reached about pH 7, and then vacuum dried in an oven at 100 ° C. for 1 hour to obtain KOH-activated rice husk activated carbon.

乾燥質量で0.3gのKOH賦活籾殻活性炭を燃焼ボートに採り、これを電気炉に入れた。電気炉の内部を窒素で3回置換した後、窒素気流100mL/min、蒸留水流入速度0.04mL/min、昇温速度5℃/minで700℃まで昇温し、700℃で1時間保持してHO賦活を行い、自然放熱させることによってKOH賦活−HO賦活籾殻活性炭を得た。 0.3 g of KOH-activated rice husk activated carbon with a dry mass was taken in a combustion boat and placed in an electric furnace. After replacing the inside of the electric furnace with nitrogen three times, the temperature is raised to 700 ° C at a nitrogen flow rate of 100 mL / min, distilled water inflow rate of 0.04 mL / min, and temperature rise rate of 5 ° C / min, and held at 700 ° C for 1 hour. Then, H 2 O activation was carried out, and natural heat was dissipated to obtain KOH activated −H 2 O activated rice husk activated carbon.

表1における実施例1B、1Cに関して、HO賦活の条件を、800℃で1時間(実施例1B)または900℃で1時間(実施例1C)に変更した以外は、実施例1Aと同一の条件で、KOH賦活−HO賦活籾殻活性炭(実施例1B、1C)を得た。 Example 1B in Table 1, with respect to 1C, except that the conditions of H 2 O activated, was changed to 1 hour at 800 ° C. (Example 1B) or 900 ° C. for 1 hour (Example 1C) are identical to Example 1A in conditions, KOH activated -H 2 O activated chaff charcoal (example 1B, 1C) was obtained.

KOH賦活籾殻活性炭(比較例1)およびKOH賦活−HO賦活籾殻活性炭(実施例1A〜1C)について、BET比表面積、窒素相対圧P/P=0.99(径が300nmまで)の全細孔容積を測定した。t−プロット法によるミクロ孔容積を測定し、ミクロ孔の全細孔容積に占める比率を求めた。
表1にその結果を示す。また、表1には、参考のために、市販のやし殻活性炭1(参考例1)の結果も示す。
For KOH activated chaff charcoal (Comparative Example 1) and KOH activated -H 2 O activated chaff charcoal (Example 1A-1C), BET specific surface area, nitrogen relative pressure P / P 0 = 0.99 for (diameter up to 300 nm) The total pore volume was measured. The micropore volume was measured by the t-plot method, and the ratio of the micropores to the total pore volume was determined.
The results are shown in Table 1. Table 1 also shows the results of commercially available coconut shell activated carbon 1 (Reference Example 1) for reference.

表1から分かるように、KOH賦活−HO賦活籾殻活性炭は、KOH賦活籾殻活性炭と比較して、全細孔容積が減少するにもかかわらず、ミクロ孔容積が増加している。KOH賦活籾殻活性炭と比較して、700℃でHO賦活したKOH賦活−HO賦活籾殻活性炭は比表面積が減少しているが、800℃または900℃でHO賦活したKOH賦活−HO賦活籾殻活性炭は比表面積が増加している。800℃または900℃でHO賦活したKOH賦活−HO賦活籾殻活性炭は、700℃でHO賦活したKOH賦活−HO賦活籾殻活性炭よりも全細孔容積とミクロ細孔容積、ミクロ孔の比率とも増加している。これらの結果は、HO賦活によってマクロ孔およびメソ孔が壊れる一方で、ミクロ孔が発達することによるものと考えられる。また、KOH賦活−HO賦活籾殻活性炭の比表面積、全細孔容積およびミクロ孔容積は、ほとんどの細孔がミクロ孔であるやし殻活性と比較して大きい。 As can be seen from Table 1, KOH activated -H 2 O activated chaff charcoal, compared with KOH activated chaff charcoal, the total pore volume despite decreases, micropore volume is increasing. Compared with KOH-activated rice husk activated carbon, H 2 O-activated KOH activated carbon at 700 ° C-H 2 O-activated rice husk activated carbon has a reduced specific surface area, but H 2 O-activated KOH activated at 800 ° C or 900 ° C- H 2 O activated chaff charcoal has increased specific surface area. 800 ° C. or 900 KOH activated -H 2 O activated chaff activated carbon H 2 O activated at ° C., the total pore volume and micropore volume than H 2 O activated the KOH activated -H 2 O activated chaff charcoal at 700 ° C. , The ratio of micropores is also increasing. These results, while macropores and mesopores are broken by H 2 O activation is thought to be due to micropores develops. The specific surface area of KOH activated -H 2 O activated chaff charcoal, total pore volume and micropore volume is large compared to most coconut shell active pores are micropores.

本発明によれば、籾殻炭化物をKOH賦活することによって、高比表面積をもちマクロ孔からミクロ孔までの広い細孔をもつ活性炭を製造でき、さらにKOH賦活籾殻活性炭をHO賦活することによって、ミクロ孔容積が増加し、全細孔中のミクロ孔の比率が高い活性炭を製造することができた。 According to the present invention, by a chaff carbide to KOH activated, can produce activated carbon having a wide pore from the macropores have a high specific surface area to micropores, by further KOH activated chaff charcoal to H 2 O activated , The volume of micropores increased, and activated carbon with a high ratio of micropores in all pores could be produced.

表2に関して、KOHをNaOHに代えた以外は実施例1と同様にしてNaOH賦活−HO賦活籾殻活性炭を製造した(実施例2)。得られたNaOH賦活−HO賦活籾殻活性炭について、BET比表面積を測定した。
With reference to Table 2, KOH was was replaced NaOH in the same manner as in Example 1 to produce a NaOH activated -H 2 O activated chaff charcoal (Example 2). The resulting NaOH activated -H 2 O activated chaff charcoal, the BET specific surface area was measured.

次に、KOH賦活−HO賦活(700℃)籾殻活性炭(実施例1A)、NaOH賦活−HO賦活(700℃)籾殻活性炭(実施例2)、および市販やし殻活性炭1(参考例1)を、それぞれ、温度20〜25℃でベンゼンを入れた密封容器に24時間放置し、質量増加量からベンゼン吸着量を算出した。 Next, KOH activated-H 2 O activated (700 ° C.) rice husk activated carbon (Example 1A), NaOH activated-H 2 O activated (700 ° C) rice husk activated carbon (Example 2), and commercially available coconut shell activated carbon 1 (reference). Each of Example 1) was left in a sealed container containing benzene at a temperature of 20 to 25 ° C. for 24 hours, and the amount of benzene adsorbed was calculated from the amount of increase in mass.

ベンゼン蒸気は径が2nm以下であるミクロ孔によく吸着されることがわかっている。表2に示したように、KOH賦活−HO賦活籾殻活性炭およびNaOH賦活−HO賦活籾殻活性炭のいずれも、やし殻活性炭と比較してベンゼン吸着量が多くなっている。 It is known that benzene vapor is well adsorbed on micropores with a diameter of 2 nm or less. As shown in Table 2, none of the KOH activated -H 2 O activated chaff charcoal and NaOH activated -H 2 O activated chaff charcoal, palm compared to shell activated carbon has many benzene adsorption.

本発明によれば、籾殻炭化物をアルカリ賦活することによって、高比表面積をもつ活性炭を製造でき、さらにアルカリ賦活籾殻活性炭をHO賦活することによって、ミクロ孔容量が増加し、全細孔中のミクロ孔の比率が高い活性炭を製造することができ、ベンゼン吸着量を増加させることができた。 According to the present invention, by alkali activation rice husk carbide, can produce activated carbon having a high specific surface area, further the alkali activation chaff charcoal by H 2 O activated, micropore volume is increased, the total pore in Activated carbon with a high proportion of micropores could be produced, and the amount of benzene adsorbed could be increased.

また、市販石炭系活性炭(参考例2A)を用意し、これを水蒸気賦活して市販石炭系活性炭−水蒸気賦活(参考例2B)を調製した。市販やし殻活性炭2(参考例3A、表1および表2に示した市販やし殻活性炭1とは異なる)を用意し、これを水蒸気賦活して市販やし殻活性炭−水蒸気賦活(参考例3B)を調製した。いずれの場合にも、水蒸気賦活の条件は、上述した実施例1Aの条件(700℃、1時間)と同一とした。参考例2A、2B、3A、3Bについて、BET比表面積および全細孔容積を測定した。
In addition, a commercially available coal-based activated carbon (Reference Example 2A) was prepared and steam-activated to prepare a commercially available coal-based activated carbon-steam activation (Reference Example 2B). Commercially available coconut shell activated carbon 2 (different from the commercially available coconut shell activated carbon 1 shown in Reference Example 3A, Table 1 and Table 2) is prepared and steam activated to activate the commercially available coconut shell activated carbon-steam activation (Reference Example). 3B) was prepared. In each case, the conditions for steam activation were the same as the conditions of Example 1A described above (700 ° C., 1 hour). For Reference Examples 2A, 2B, 3A and 3B, the BET specific surface area and the total pore volume were measured.

表3において、市販石炭系活性炭(参考例2A)および市販やし殻活性炭2(参考例3A)ともに、水蒸気賦活を行うことにより比表面積および全細孔容積が減少している。これらの市販活性炭では細孔のほとんどがミクロ孔であり、水蒸気賦活によってミクロ孔が壊れ、その結果として比表面積および細孔容積の減少を招いていると考えられる。石炭系活性炭およびやし殻活性炭は市販されている状態で比表面積および細孔容積が最大になるように最適化されている。しかし、市販石炭系活性炭または市販やし殻活性炭をさらに水蒸気賦活すると、比表面積および細孔容積が減少し、ミクロ孔は減少する。 In Table 3, the specific surface area and the total pore volume of both the commercially available coal-based activated carbon (Reference Example 2A) and the commercially available coconut shell activated carbon 2 (Reference Example 3A) are reduced by steam activation. Most of the pores of these commercially available activated carbons are micropores, and it is considered that the micropores are broken by steam activation, resulting in a decrease in specific surface area and pore volume. Carboniferous activated carbon and coconut shell activated carbon are optimized to maximize the specific surface area and pore volume in the commercially available state. However, when commercially available coal-based activated carbon or commercially available coconut shell activated carbon is further steam-activated, the specific surface area and pore volume decrease, and the micropores decrease.

以上の結果をまとめると、下記のように結論できる。籾殻活性炭をアルカリ賦活すると、ミクロ孔、メソ孔およびマクロ孔が発達し、大きな比表面積を持つようになる。さらに、アルカリ賦活籾殻活性炭をHO賦活すると、マクロ孔およびメソ孔が壊れ、その代わりにミクロ孔が発達する。水蒸気賦活を700℃で行った場合、ミクロ孔が発達するが、その発達度合は十分ではないため、結果としてマクロ孔およびメソ孔が壊れたことにより比表面積および細孔容積の減少が大きく表れる。水蒸気賦活を800℃または900℃で行った場合には、ミクロ孔の発達が著しいため、水蒸気賦活を700℃で行った場合よりも、比表面積および細孔容積ともに増加する。また、比表面積および細孔容積の増加をもたらす水蒸気賦活温度には最適条件があるように見える。本実施例の場合には、800℃での水蒸気賦活が最適であった。
以下、本願の出願当初の特許請求の範囲に記載していた発明を付記する。
[1] ケイ素集積バイオマスを炭化して炭化物を得る工程と、
前記炭化物にアルカリ化合物を混合してアルカリ賦活するとともにケイ素を反応させてケイ酸アルカリを生成させた後、前記ケイ酸アルカリを除去して多孔質炭素材料を得る工程と、
前記多孔質炭素材料をガス賦活して活性炭を得る工程とを有することを特徴とする活性炭の製造方法。
[2] 前記ケイ素集積バイオマスは質量%で0.1%以上のシリカを含むことを特徴とする[1]に記載の活性炭の製造方法。
[3] 前記ケイ素集積バイオマスを100℃以下で酸処理して不純物を除去することを特徴とする[1]または[2]に記載の活性炭の製造方法。
[4] 前記アルカリ化合物が水酸化カリウムまたは水酸化ナトリウムであることを特徴とする[1]〜[3]のいずれか1項に記載の活性炭の製造方法。
[5] 前記アルカリ賦活を、500〜1000℃で行うことを特徴とする[1]〜[4]のいずれか1項に記載の活性炭の製造方法。
[6] 前記ガス賦活を、水蒸気を含む不活性ガス雰囲気下で行うことを特徴とする[1]〜[5]のいずれか1項に記載の活性炭の製造方法。
[7] 前記ガス賦活を、500〜1000℃で行うことを特徴とする[1]〜[6]のいずれか1項に記載の活性炭の製造方法。
[8] ケイ素集積バイオマスを炭化して炭化物を得る炭化物取得部と、前記炭化物にアルカリ化合物を混合してアルカリ賦活するとともにケイ素を反応させてケイ酸アルカリを生成させた後、前記ケイ酸アルカリを除去して多孔質炭素材料を得る多孔質炭素材料取得部と、前記多孔質炭素材料をガス賦活して活性炭を得る活性炭取得部とを備える活性炭製造システム。
Summarizing the above results, we can conclude as follows. Alkali activation of rice husk activated carbon develops micropores, mesopores and macropores, resulting in a large specific surface area. Further, when the alkali activation chaff charcoal H 2 O to activation, broken macropores and mesopores, micropores develops instead. When steam activation is performed at 700 ° C., micropores develop, but the degree of development is not sufficient. As a result, the macropores and mesopores are broken, resulting in a large decrease in specific surface area and pore volume. When steam activation is carried out at 800 ° C. or 900 ° C., the development of micropores is remarkable, so that both the specific surface area and the pore volume are increased as compared with the case where steam activation is carried out at 700 ° C. Also, there appear to be optimal conditions for the water vapor activation temperature, which results in an increase in specific surface area and pore volume. In the case of this example, steam activation at 800 ° C. was optimal.
Hereinafter, the inventions described in the claims at the time of filing the application of the present application will be added.
[1] A process of carbonizing silicon-accumulated biomass to obtain carbides,
A step of mixing an alkali compound with the carbide to activate the alkali and reacting silicon to generate an alkali silicate, and then removing the alkali silicate to obtain a porous carbon material.
A method for producing activated carbon, which comprises a step of gas-activating the porous carbon material to obtain activated carbon.
[2] The method for producing activated carbon according to [1], wherein the silicon-accumulated biomass contains 0.1% or more of silica in mass%.
[3] The method for producing activated carbon according to [1] or [2], wherein the silicon-accumulated biomass is acid-treated at 100 ° C. or lower to remove impurities.
[4] The method for producing activated carbon according to any one of [1] to [3], wherein the alkaline compound is potassium hydroxide or sodium hydroxide.
[5] The method for producing activated carbon according to any one of [1] to [4], wherein the alkali activation is carried out at 500 to 1000 ° C.
[6] The method for producing activated carbon according to any one of [1] to [5], wherein the gas activation is carried out in an atmosphere of an inert gas containing water vapor.
[7] The method for producing activated carbon according to any one of [1] to [6], wherein the gas activation is carried out at 500 to 1000 ° C.
[8] A carbide acquisition unit that carbonizes silicon-accumulated biomass to obtain carbides, and an alkali compound is mixed with the carbides to activate the alkali, and silicon is reacted to generate alkali silicate, and then the alkali silicate is used. An activated carbon production system including a porous carbon material acquisition unit that is removed to obtain a porous carbon material, and an activated carbon acquisition unit that gas-activates the porous carbon material to obtain activated carbon.

Claims (1)

質量%で0.1%以上のシリカを含むケイ素集積バイオマスを100℃以下で酸処理して不純物を除去する工程と、
前記ケイ素集積バイオマスを炭化して炭化物を得る工程と、
前記炭化物に水酸化カリウムを混合して500〜1000℃でアルカリ賦活するとともにケイ素を反応させてケイ酸アルカリを生成させた後、前記ケイ酸アルカリを除去して多孔質炭素材料を得る工程と、
前記多孔質炭素材料を、水蒸気を含む不活性ガス雰囲気下、800〜900℃でガス賦活して活性炭を得る工程とを有することを特徴とする活性炭の製造方法。
A step of removing impurities by acid-treating silicon-accumulated biomass containing 0.1% or more of silica by mass at 100 ° C. or lower.
The step of carbonizing the silicon-accumulated biomass to obtain a carbide and
A step of mixing potassium hydroxide with the carbide to activate alkali at 500 to 1000 ° C. and reacting silicon to generate alkali silicate, and then removing the alkali silicate to obtain a porous carbon material.
A method for producing activated carbon, which comprises a step of activating the porous carbon material with a gas at 800 to 900 ° C. in an inert gas atmosphere containing water vapor to obtain activated carbon.
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