JPH07155609A - Production of high capacity carbon material - Google Patents

Production of high capacity carbon material

Info

Publication number
JPH07155609A
JPH07155609A JP5309385A JP30938593A JPH07155609A JP H07155609 A JPH07155609 A JP H07155609A JP 5309385 A JP5309385 A JP 5309385A JP 30938593 A JP30938593 A JP 30938593A JP H07155609 A JPH07155609 A JP H07155609A
Authority
JP
Japan
Prior art keywords
carbon material
carbonaceous material
magnesium
surface area
specific surface
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
JP5309385A
Other languages
Japanese (ja)
Other versions
JP3539435B2 (en
Inventor
Tomoji Tsuji
智次 辻
Yutaka Tamura
豊 田村
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.)
Mitsubishi Gas Chemical Co Inc
Original Assignee
Mitsubishi Gas Chemical Co Inc
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 Mitsubishi Gas Chemical Co Inc filed Critical Mitsubishi Gas Chemical Co Inc
Priority to JP30938593A priority Critical patent/JP3539435B2/en
Publication of JPH07155609A publication Critical patent/JPH07155609A/en
Application granted granted Critical
Publication of JP3539435B2 publication Critical patent/JP3539435B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PURPOSE:To produce a carbon material having a high specific surface area and showing high decomposition activity to an inorg. or org. substance by adding a magnesium or silver compd. to a carbonaceous material having pores and a predetermined specific surface area or more and heat-treating this carbonaceous material in an oxidizable gas atmosphere. CONSTITUTION:A high capadity carbon material is produced by adding a magnesium or silver compd. to a carbonaceous material having pores and a specific surface area of 100m<2>/g or more and heat-treating this carbonaceous material in an oxidizable gas atmosphere. As the carbonaceous material becoming a raw material, one with a specific surface area of at least 100m<2>/g or more is used. When a metal compd. is added, an aq. soln. of a magnesium or silver compd. is added to the sufficiently degassed raw carbonaceous material to be mixed therewith and the resulting mixture is allowed to stand to cool to uniformly infiltrate the metal compd. throughout the pores of caboneceous material. In a heat treatment process, the carbonaceous material to be treated is uniformly heated.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、COD源物質に対して
高い分解能を有し、高比表面積を有する高性能な炭素材
料の製造方法に関する。本発明の炭素材料は、COD源
物質に対して高い分解能を有し、例えば過酸化水素、ヒ
トラジン等の無機物質および有機物質に対して極めて優
れた分解活性を有することからこれらCOD源物質の分
解触媒として有用なものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for producing a high-performance carbon material having a high resolving power for a COD source material and a high specific surface area. The carbon material of the present invention has a high decomposing ability for COD source substances, and has extremely excellent decomposing activity for inorganic substances such as hydrogen peroxide and human lazine and organic substances. It is useful as a catalyst.

【0002】[0002]

【従来技術】一般に活性炭は、炭化水素の分別、工業ガ
スの精製、食品工業、化学工業における液相精製、水処
理剤等の他に、空気分子ふるい材、貴金属塩溶液からの
貴金属回収等の吸着の他に、触媒担体として、またCO
D源物質の分解触媒等に広く利用されている。
In general, activated carbon is used for separating hydrocarbons, refining industrial gas, liquid phase refining in food industry, chemical industry, water treatment agent, etc., as well as air molecule sieving material, precious metal recovery from precious metal salt solution, etc. In addition to adsorption, as a catalyst carrier and CO
It is widely used as a catalyst for decomposing D source materials.

【0003】通常、活性炭はヤシガラ、木材、石炭、石
炭および石油コク−ス、有機性樹脂等を原料にして炭化
後、酸化性ガスと接触反応させて微細な細孔を形成させ
るガス賦活法、あるいは上記のような原料からの炭素質
材料に塩化亜鉛、酸、アルカリ蒸気等の薬品を含浸させ
て不活性ガス中で加熱して薬品の脱水および酸化反応に
より微細な細孔を形成させる薬品賦活法等が広く知られ
ている。(例えば、特公昭62−61529号公報、米
国特許第3624004号、米国特許第3642657
号、米国特許第3833514号、特開平1−2304
14号公報、特開平2−97414号公報)
Generally, activated carbon is a gas activation method in which coconut husk, wood, coal, coal and petroleum cocos, organic resin, etc. are used as raw materials, carbonized, and then reacted with an oxidizing gas to form fine pores, Alternatively, chemical activation by impregnating a carbonaceous material from the above raw materials with a chemical such as zinc chloride, acid or alkali vapor and heating in an inert gas to form fine pores by dehydration and oxidation reaction of the chemical The law is widely known. (For example, Japanese Patent Publication No. 62-61529, U.S. Pat. No. 3,624,004, U.S. Pat. No. 3,642,657.
No. 3,833,514, Japanese Patent Laid-Open No. 1-2304.
No. 14, JP-A-2-97414)

【0004】また炭素粒子に金属触媒を添着して賦活
し、吸着能の高い炭素材料を短時間で得る方法が特開平
1−141814号公報、特開平1−141815号公
報に報告されている。しかしながらこのような方法で得
られる炭素材料の吸着能は公知の吸着用炭素材料と呼ば
れるものと大差がなく、これまた高性能炭素材料という
には不十分である。
Further, a method of activating a carbon catalyst by adhering a metal catalyst to the carbon particles to obtain a carbon material having a high adsorptivity in a short time has been reported in JP-A-1-141814 and JP-A-1-141815. However, the adsorption capacity of the carbon material obtained by such a method is not so different from that of the known carbon material for adsorption, and it is not sufficient to be a high performance carbon material.

【0005】また、特開平5−811号公報に示される
高活性な過酸化水素分解触媒は、かなり高い過酸化水分
解能を有するが、これは、原料として蛋白質含有の汚泥
もしくは廃棄物質が用いられるため、製造時に臭気が発
生する難点がある。
Further, the highly active hydrogen peroxide decomposition catalyst disclosed in Japanese Patent Application Laid-Open No. 5-811 has a considerably high ability to decompose peroxide water, which uses a protein-containing sludge or waste material as a raw material. Therefore, there is a problem that odor is generated during manufacturing.

【0006】例えば、過酸化水素、ヒトラジン等の無機
物質または有機物質を含有する廃液をそのまま排出した
場合CODを高めるばかりではなく、廃水処理時、生物
活性汚泥処理装置に混入した場合、過酸化水素含有排水
の場合は分解にともなって発生する酸素ガスが懸濁物を
浮上させ、処理水の水質悪化の原因となるなど種々のト
ラブルの原因となる。そこで、これらの廃液は、予め分
解処理して排出する必要があり、その分解方法として活
性炭を利用する方法がある。
For example, not only is COD increased when a waste liquid containing an inorganic substance or an organic substance such as hydrogen peroxide or human lazine is discharged as it is, but also when the waste liquid is mixed with a biological activated sludge treatment device during treatment of the waste water, hydrogen peroxide In the case of contained wastewater, oxygen gas generated by decomposition causes suspension to float, causing various troubles such as deterioration of water quality of treated water. Therefore, it is necessary to decompose and discharge these waste liquids in advance, and there is a method of utilizing activated carbon as the decomposition method.

【0007】現在、過酸化水素分解能を有する市販の活
性炭としては、1000m2 /g程度の比表面積を有す
る活性炭が知られている。 しかしながら、このような
市販の活性炭は、過酸化水素の分解活性が必ずしも充分
でなく、触媒寿命も短かく工業的に利用するには十分と
はいい難いものである。
Currently, as a commercially available activated carbon having a hydrogen peroxide decomposing ability, an activated carbon having a specific surface area of about 1000 m 2 / g is known. However, such commercially available activated carbon does not always have sufficient hydrogen peroxide decomposition activity, has a short catalyst life, and is not sufficient for industrial use.

【0008】[0008]

【発明が解決しようとする課題】しかしながら、上記の
アルカリ蒸気賦活法による高比表面積活性炭の製造は、
炭素質材料に対して水酸化カリウム等のアルカリ金属化
合物を、好適には2倍以上の大過剰を添加する必要があ
るため、焼成工程での装置の腐食をまねき、かつ炭素質
材料とアルカリ金属化合物との混合物が焼成中に粘着し
流動性が悪く装置を詰まらせる等の問題があり取扱が困
難である。 また、大過剰のアルカリを用いるため経済
面から残存アルカリを回収再使用する必要があり製造工
程が複雑になる等の欠点を有している。また、この活性
炭は、高比表面積を有するもののCOD源物質の分解性
能はほとんどない。このような状況から工業的実施が容
易な製法であって、COD源物質の分解性能の高い高性
能な炭素材料が望まれていた。
However, the production of high specific surface area activated carbon by the above-mentioned alkali vapor activation method is
Since it is necessary to add an alkali metal compound such as potassium hydroxide to the carbonaceous material, preferably in a large excess of 2 times or more, corrosion of the device in the firing step is caused, and the carbonaceous material and the alkali metal compound are added. It is difficult to handle because there is a problem that the mixture with the compound sticks during firing and the flowability is poor and the device is clogged. In addition, since a large excess of alkali is used, it is necessary to recover and reuse the residual alkali from the economical aspect, which has a drawback that the manufacturing process becomes complicated. Further, although this activated carbon has a high specific surface area, it has almost no decomposition performance for the COD source substance. Under these circumstances, there has been a demand for a high-performance carbon material which is a manufacturing method that is easy to carry out industrially and has a high decomposition performance for the COD source substance.

【0009】本発明は、このような従来方法に認められ
る種々の問題点を解決し、高比表面積でかつ過酸化水素
やヒドラジン等の無機物質または有機物質に対して高い
分解活性を持つ炭素材料を製造する方法を提供するもの
である。
The present invention solves various problems recognized in such conventional methods, and has a high specific surface area and a carbon material having a high decomposition activity for an inorganic substance or an organic substance such as hydrogen peroxide or hydrazine. To provide a method of manufacturing.

【0010】[0010]

【課題を解決するための手段】本発明者は、上記のよう
な技術の現況に鑑み、COD物質に対する高い分解性能
を有する高性能炭素材料の製法について鋭意研究を重ね
た結果、細孔を有する炭素質材料にある種の金属化合物
を添加した後、加熱処理することにより高性能炭素材料
が得られることを見い出し本発明を為した。
In view of the current state of the art as described above, the present inventor has conducted earnest research on a method for producing a high-performance carbon material having a high decomposition performance for COD substances, and as a result, has pores. It was found that a high-performance carbon material can be obtained by adding a certain kind of metal compound to a carbonaceous material and then heat-treating it, and made the present invention.

【0011】すなわち、本発明は、細孔を有する炭素質
材料にマグネシウム化合物または銀化合物を添加した
後、酸化性ガス雰囲気下で加熱処理することを特徴とす
る高性能炭素材料の製法である。
That is, the present invention is a method for producing a high-performance carbon material, which comprises adding a magnesium compound or a silver compound to a carbonaceous material having pores and then heat-treating it in an oxidizing gas atmosphere.

【0012】以下に本発明を詳細に説明する。先ず、本
発明における原料炭素質材料としては、比表面積100
m2/g以上の細孔を有することが必要である。比表面積が
100m2/g未満の炭素質材料を用いる場合は高性能炭素
材料を得ることはできない。
The present invention will be described in detail below. First, as the raw material carbonaceous material in the present invention, a specific surface area of 100
It is necessary to have pores of m 2 / g or more. If a carbonaceous material having a specific surface area of less than 100 m 2 / g is used, a high performance carbon material cannot be obtained.

【0013】本発明において原料となる炭素質材料は、
少なくとも比表面積が100m2/g以上の細孔を有するも
のが使用される。このような炭素質材料は、ヤシガラ、
麦ガラ、もみがら、のこくず、木材、及びパルプ廃液な
どの植物系、および石炭、石油、それらのコ−クス、並
びにピッチなどの重質歴青物系の炭素質材料が利用でき
る。また、この原料炭素質材料の形状は、特に制限がな
く、粉末状、破砕状、顆粒状、および、円柱状のいずれ
でも使用できる。
The carbonaceous material used as a raw material in the present invention is
A material having pores having a specific surface area of at least 100 m 2 / g is used. Such carbonaceous material is coconut husk,
Plant-based carbonaceous materials such as barley, chaff, sawdust, wood, and pulp effluent, and heavy bituminous carbonaceous materials such as coal, petroleum, cokes thereof, and pitch are available. The shape of the raw carbonaceous material is not particularly limited, and any of powdery, crushed, granular, and cylindrical shapes can be used.

【0014】また、粒度は、1〜300メッシュ通過の
大きさの範囲で粗粒または細粒のいずれも使用できるが
粒度が小さいほど、酸化性ガス雰囲気で加熱処理する賦
活の時間を短くすることができるので好ましい。しかし
ながら、粒度が大きくても加熱処理時間を充分長くすれ
ば、高性能な炭素材料を得ることができる。また本発明
の方法は、原料の形状を維持したままで高性能炭素材料
が製造できるため必ずしも成型する必要がなく、バイン
ダ−等で成型することによる比表面積の低下の問題もな
い工業的に有利な製法である。
As the particle size, either coarse particles or fine particles can be used within a size range of 1 to 300 mesh, but the smaller the particle size, the shorter the activation time for heat treatment in an oxidizing gas atmosphere. It is possible to do so, which is preferable. However, even if the particle size is large, a high performance carbon material can be obtained if the heat treatment time is sufficiently long. Further, the method of the present invention does not necessarily need to be molded because a high-performance carbon material can be produced while maintaining the shape of the raw material, and there is no problem of reduction of specific surface area due to molding with a binder or the like, which is industrially advantageous. It is a manufacturing method.

【0015】本発明において金属化合物を添加する方法
は、先ず原料炭素質材料を十分に脱気した後、マグネシ
ウム化合物または銀化合物の水溶液を脱気した原料炭素
質材料に添加し溶解混合した後、放冷して細孔内全体に
均一に金属化合物を含浸、坦持させる。上記の脱気方法
としては通常は原料炭素質材料に所定量の水を加え攪伴
下、10分ないし3時間、好ましくは20分ないし2時
間の煮沸処理を行う方法が一般であるが、炭素質材料を
真空下で脱気してもよい。
In the method of adding a metal compound in the present invention, first, the raw material carbonaceous material is sufficiently degassed, and then an aqueous solution of a magnesium compound or a silver compound is added to the degassed raw material carbonaceous material and dissolved and mixed. It is allowed to cool and the metal compound is uniformly impregnated and supported in the entire pores. As the above-mentioned degassing method, generally, a predetermined amount of water is added to the raw carbonaceous material and the mixture is boiled for 10 minutes to 3 hours, preferably 20 minutes to 2 hours with stirring. The quality material may be degassed under vacuum.

【0016】本発明におけるマグネシウム化合物あるい
は銀化合物としては、マグネシウムまたは銀の酸化物、
硫化物、ハロゲン化物、硫酸塩、硝酸塩、燐酸塩、炭酸
塩などの無機酸塩、ギ酸塩、酢酸塩、シュウ酸塩、酒石
酸塩、乳酸塩などの有機酸塩、並びにアルコラ−トが挙
げられる。
As the magnesium compound or silver compound in the present invention, magnesium or silver oxide,
Inorganic acid salts such as sulfides, halides, sulfates, nitrates, phosphates and carbonates, organic acid salts such as formates, acetates, oxalates, tartrates and lactates, and alcoholates. .

【0017】マグネシウム化合物の代表的な化合物とし
ては、塩化マグネシウム、硫酸マグネシウム、硝酸マグ
ネシウム、炭酸マグネシウム、燐酸マグネシウム、酢酸
マグネシウム、シュウ酸マグネシウム、酒石酸マグネシ
ウム、乳酸マグネシウム、およびオルトケイ酸マグネシ
ウム等が挙げられる。
Typical examples of the magnesium compound include magnesium chloride, magnesium sulfate, magnesium nitrate, magnesium carbonate, magnesium phosphate, magnesium acetate, magnesium oxalate, magnesium tartrate, magnesium lactate, and magnesium orthosilicate.

【0018】また銀化合物の代表的な化合物としては、
フッ化銀、塩素酸銀、過塩素酸銀、ヨウ化銀、硫酸銀、
硝酸銀、炭酸銀、酢酸銀、酒石酸銀、シアン化銀、ジア
ンミン銀塩、1,10フェナントロリン銀等が挙げられ
る。なお、不溶性の化合物は、均一に担時させるために
酸で溶解して使用することが好ましい。
Further, as typical compounds of silver compounds,
Silver fluoride, silver chlorate, silver perchlorate, silver iodide, silver sulfate,
Examples thereof include silver nitrate, silver carbonate, silver acetate, silver tartrate, silver cyanide, diammine silver salt, and 1,10 phenanthroline silver. The insoluble compound is preferably dissolved in an acid before use so that it can be uniformly supported.

【0019】本発明において上記マグネシウムは、炭素
質材料に対して重量比で1:0.001〜1:0.5、
好ましくは1:0.01〜1:0.3の範囲で添加され
る。
In the present invention, the magnesium is used in a weight ratio of 1: 0.001 to 1: 0.5 with respect to the carbonaceous material,
Preferably it is added in the range of 1: 0.01 to 1: 0.3.

【0020】また銀化合物は、炭素質材料に対して重量
比で1:0.001〜1:0.1、好ましくは1:0.
01〜1:0.09の範囲で添加される。
The weight ratio of the silver compound to the carbonaceous material is 1: 0.001 to 1: 0.1, preferably 1: 0.
It is added in the range of 01 to 1: 0.09.

【0021】金属化合物の添加量がそれぞれ上記の範囲
より少ない場合は充分な賦活を行うことができず目的と
する高比表面積が得られない。また上記の範囲超え多い
場合は、比表面積2800m2/g 以上を示す細孔の形成
が促進されず収量も低下することから上記範囲が実用的
である。銀化合物の場合は上記範囲を超えて使用するこ
とは、例えば上水道の抗菌用に使用した場合、銀の析出
量が多くなるなど好ましくない。
If the amount of the metal compound added is less than the above range, sufficient activation cannot be performed and the desired high specific surface area cannot be obtained. When the amount exceeds the above range, the above range is practical because the formation of pores having a specific surface area of 2800 m 2 / g or more is not promoted and the yield is reduced. In the case of a silver compound, it is not preferable to use the silver compound in an amount exceeding the above range, for example, when it is used as an antibacterial agent for waterworks, the amount of silver deposited increases.

【0022】またマグネシウム化合物、銀化合物の炭素
質材料への含浸時間は、使用される化合物の種類、溶液
の状態、炭素質材料と水の混合割合あるいは金属化合物
の添加量や濃度によりに異なるが、一般的には10分〜
30時間、好ましくは30分〜25時間の範囲である。
Further, the impregnation time of the magnesium compound and the silver compound into the carbonaceous material depends on the kind of the compound used, the state of the solution, the mixing ratio of the carbonaceous material and water, or the addition amount and concentration of the metal compound. , Generally 10 minutes ~
It is in the range of 30 hours, preferably 30 minutes to 25 hours.

【0023】このようにして、調製した混合液をろ過、
水洗し減圧乾燥して金属化合物が含浸、坦持された炭素
質材料が得られる。なお、炭素質材料に含浸、坦持され
ない余剰の金属化合物は、ろ液を循環させて再使用する
ことができる。なお所望に応じて、含浸、坦持後必ずし
も水洗、乾燥を行う必要はなく、ろ過後そのまま次の工
程に付することもできる。
The mixture thus prepared is filtered,
It is washed with water and dried under reduced pressure to obtain a carbonaceous material impregnated with and supported by a metal compound. The excess metal compound that is not impregnated in or supported by the carbonaceous material can be reused by circulating the filtrate. If desired, it is not always necessary to carry out washing with water and drying after impregnation and supporting, and it may be subjected to the next step as it is after filtration.

【0024】次に、この生成物は酸化性ガス雰囲気下
で、加熱し賦活される。酸化性ガス雰囲気としては、水
蒸気、二酸化炭素、酸素、オゾン、および、二酸化窒素
などが使用できる。また、これらのガスと燃焼ガスある
いは不活性ガスと混合して用いてもよい。特に、水蒸
気、二酸化炭素、及びこれらのガスと燃焼ガスあるいは
不活性ガスと混合して使用することが好ましい。なお、
窒素、アルゴン等の不活性ガス雰囲気下では高比表面積
を有し、かつCOD源物質に対して高い分解性能を有す
る高性能炭素材料は得られなく好ましくない。
Next, the product is heated and activated in an oxidizing gas atmosphere. Water vapor, carbon dioxide, oxygen, ozone, nitrogen dioxide and the like can be used as the oxidizing gas atmosphere. Further, these gases may be mixed with a combustion gas or an inert gas and used. In particular, it is preferable to use water vapor, carbon dioxide, and a mixture of these gases with a combustion gas or an inert gas. In addition,
In an atmosphere of an inert gas such as nitrogen or argon, a high performance carbon material having a high specific surface area and a high decomposition performance for a COD source substance cannot be obtained, which is not preferable.

【0025】本発明における賦活工程の加熱処理の温度
は、一般的には600゜C〜1200゜Cであり、好ま
しくは700゜C〜1100゜Cの範囲である。加熱処
理温度下における保持時間は、通常30分〜5時間で
り、好ましくは1〜4時間の範囲である。この処理温度
が高く保持時間が長いほど高性能炭素材料が得られる
が、収量が低下する傾向があり上記範囲が好ましい。
The temperature of the heat treatment in the activation step in the present invention is generally 600 ° C to 1200 ° C, preferably 700 ° C to 1100 ° C. The holding time at the heat treatment temperature is usually 30 minutes to 5 hours, preferably 1 to 4 hours. The higher the treatment temperature and the longer the holding time, the higher the performance carbon material can be obtained, but the yield tends to decrease, and the above range is preferable.

【0026】本発明の方法において、加熱処理の工程は
いずれの方法でも実施し得るが、被処理炭素質材料が均
一に加熱される方式であることが好ましく、移動式、回
転式、および流動式により、加熱方法は内熱式または外
熱式で実施するのがよい。また、加熱処理工程は、バッ
チ式、連続式いずれの方式でも実施し得るが、特に被処
理炭素質材料が流動性に富んでいる場合、操作が容易な
ことから連続式で実施することが実用的である。
In the method of the present invention, the heat treatment step may be carried out by any method, but it is preferable that the carbonaceous material to be treated is uniformly heated, such as a mobile type, a rotary type and a flow type. Therefore, it is preferable that the heating method be an internal heating type or an external heating type. Further, the heat treatment step can be carried out by either a batch system or a continuous system, but particularly when the carbonaceous material to be treated is rich in fluidity, it is practical to carry out it in a continuous system because the operation is easy. Target.

【0027】加熱処理終了後は、生成物を反応管から取
り出し、乾燥して目的物の高性能炭素材料が得られる。
得られる炭素材料は造粒して製品とすることもできる
が、本発明の方法では、原料の形状が維持されるので多
くの場合、使用する原料の形状を選択することで製品の
形状を任意に製造することができる利点がある。
After completion of the heat treatment, the product is taken out from the reaction tube and dried to obtain the target high-performance carbon material.
The obtained carbon material can be granulated into a product, but in the method of the present invention, since the shape of the raw material is maintained, in many cases, the shape of the raw material to be used can be selected so that the shape of the product is arbitrary. It has the advantage that it can be manufactured.

【0028】このようにして得られる本発明の高性能炭
素材料は、比表面積1800〜2800m2/gで、全細孔
容積1.3〜2.0ml/g 、平均細孔半径11〜15Å
のもので、COD源物質に対して極めて高い分解性能を
有する。
The high performance carbon material of the present invention thus obtained has a specific surface area of 1800 to 2800 m 2 / g, a total pore volume of 1.3 to 2.0 ml / g, and an average pore radius of 11 to 15Å.
It has a very high decomposition performance for COD source materials.

【0029】本発明の高性能炭素材料は、細孔を有する
炭素質材料にマグネシウム化合物または銀化合物を添加
して酸化性ガス雰囲気下で加熱処理することにより製造
することができるが、他の金属例えばカリウム化合物を
添加して同様な操作をおこなっても高性能炭素材料を得
ることはできない。このことから、本発明における高比
表面積化およびCOD源物質分解能の形成機構は明かで
はないが含浸された金属特有の触媒性能により炭素と酸
化性ガスとの酸化反応が起こり選択的なガス化を促進し
て微細孔が形成され高比表面積化すると共にCOD源物
質分解能の活性点も同時に生成するものと推察される。
The high-performance carbon material of the present invention can be produced by adding a magnesium compound or a silver compound to a carbonaceous material having pores and subjecting it to heat treatment in an oxidizing gas atmosphere. For example, even if a potassium compound is added and the same operation is performed, a high performance carbon material cannot be obtained. From this, the mechanism of formation of the high specific surface area and the ability to decompose the COD source material in the present invention is not clear, but the catalytic performance peculiar to the impregnated metal causes an oxidation reaction between carbon and an oxidizing gas to cause selective gasification. It is presumed that micropores are accelerated to form a high specific surface area, and at the same time, active sites for decomposing the COD source substance are generated.

【0030】本発明の高性能炭素材料を使用するCOD
源物質の分解として、例えば廃水中の過酸化水素の分解
がある。過酸化水素の分解は、一般に過酸化水素を含有
する水溶液、過酸化水素含有有機溶剤あるいは過酸化水
素含有の酸および塩基溶液等を、本発明の炭素材料と接
触させることによって行われるが、このような方法に限
定されるものではなく、過酸化水素のミストあるいは蒸
気の状態でも分解することができる。
COD using the high performance carbon material of the present invention
The decomposition of the source material is, for example, decomposition of hydrogen peroxide in waste water. Decomposition of hydrogen peroxide is generally carried out by bringing an aqueous solution containing hydrogen peroxide, an organic solvent containing hydrogen peroxide or an acid and base solution containing hydrogen peroxide into contact with the carbon material of the present invention. The method is not limited to such a method, and it can be decomposed even in the state of mist or vapor of hydrogen peroxide.

【0031】また、本発明の高性能炭素材料を用いて被
処理液中の過酸化水素を分解する場合、被処理液のpH
および被処理液中の過酸化水素の濃度等は格別限定され
ず、広範囲の液性で使用することができる。本発明の高
性能炭素材料を使用した過酸化水素の分解は、回分式、
連続式いずれの方式でも実施でき、処理温度、処理時間
等は、被処理液の種類により適宜選択できる。
When decomposing hydrogen peroxide in the liquid to be treated using the high performance carbon material of the present invention, the pH of the liquid to be treated is
The concentration of hydrogen peroxide in the liquid to be treated is not particularly limited, and it can be used in a wide range of liquid properties. Decomposition of hydrogen peroxide using the high performance carbon material of the present invention is carried out in a batch system,
It can be carried out by any of the continuous methods, and the treatment temperature, treatment time and the like can be appropriately selected depending on the type of the liquid to be treated.

【0032】本発明の高性能炭素材料は、その他の汚染
物質、例えばヒドラジンの分解に高い活性を示し、市販
活性炭の数十倍の分解性能がある。その他の有機物質の
分解も酸素発生剤存在下で高分解活性を示し、廃水中な
どのCODの低減化に有効である。また、着色成分、C
OD源成分の吸着除去や、オゾンおよびNOX の分解、
SO2 、CO、CO2 等有害物質の吸着除去、溶存金属
の吸着回収、メタンの吸蔵、ガソリン吸着用キャニスタ
−、電気二重層型コンデンサ−、電池の電極用、およ
び、医薬用などに用いることができる。
The high-performance carbon material of the present invention shows high activity for decomposing other pollutants such as hydrazine, and has a decomposing performance several tens of times that of commercially available activated carbon. Decomposition of other organic substances also shows high decomposition activity in the presence of an oxygen generator, and is effective in reducing COD in wastewater. Also, a coloring component, C
Adsorption and removal of OD source components, decomposition of ozone and NO x ,
Use for adsorption and removal of harmful substances such as SO 2 , CO and CO 2 , adsorption and recovery of dissolved metals, occlusion of methane, canister for adsorbing gasoline, electric double layer type capacitor, electrode of battery, and medicine You can

【0033】[0033]

【実施例】次に本発明の方法を実施例によりさらに具体
的に説明する。各炭素材料の物性は、N2 ガス吸着法に
よる吸着等温線を求め、BET比比表面積は、P/PO
=0.02〜0.3の範囲でBETプロット(多点法)
により求めた。 (湯浅アイオニクス社製のオ−トソ−
ブ−6により測定)ミクロポアは直径20Å以下の細
孔、メソポアは、直径20〜500Åの細孔である。C
OD源物質分解性能の試験例として過酸化水素の分解能
を測定した。
EXAMPLES Next, the method of the present invention will be described more specifically by way of examples. For the physical properties of each carbon material, the adsorption isotherm obtained by the N 2 gas adsorption method was determined, and the BET specific surface area was P / P O
= BET plot in the range of 0.02-0.3 (multipoint method)
Sought by. (Otoso manufactured by Yuasa Ionics
Micropores are pores having a diameter of 20 Å or less, and mesopores are pores having a diameter of 20 to 500 Å. C
As a test example of the OD source substance decomposition performance, the resolution of hydrogen peroxide was measured.

【0034】実施例 1 500ml容積のビ−カ−に12〜32メッシュ通過の
大きさの市販活性炭10gを仕込みイオン交換水250
mlを加え、攪伴しながら煮沸処理を30分行った。こ
れに、塩化マグネシウム粉末0.8g (原料炭素質材料
に対して重量比で0.08 )を添加し混合溶解させた後、放
冷し、24時間放置した。次に、この混合液をろ過し、
ろ別した活性炭素質材料をイオン交換水200mlで3
回洗浄した後、真空乾燥器で110゜C、2時間乾燥し
た。この生成物2gを反応管に仕込み二酸化炭素気流中
で室温から1000 ゜Cまで25゜C/分の昇温速度
で加熱し同温度で90分保持して賦活を行い高性能炭素
材料を得た。得られた高性能炭素材料555ppmを使
用して、4000ppmの過酸化水素溶液(pH2)を
室温下で15分間攪伴して過酸化水素分解試験を実施し
た。 表−1に、各種物性の測定および過酸化水素の分
解率の結果を示す。
Example 1 A beaker having a volume of 500 ml was charged with 10 g of commercially available activated carbon having a size of 12 to 32 mesh and ion-exchanged water 250.
After adding ml, the mixture was boiled for 30 minutes with stirring. To this, 0.8 g of magnesium chloride powder (0.08 by weight ratio to the raw carbonaceous material) was added, mixed and dissolved, then allowed to cool and left to stand for 24 hours. Then, the mixture is filtered,
Filter the activated carbonaceous material with 200 ml of deionized water to
After washing twice, it was dried in a vacuum dryer at 110 ° C. for 2 hours. 2 g of this product was charged into a reaction tube, heated in a carbon dioxide stream from room temperature to 1000 ° C. at a temperature rising rate of 25 ° C./min, and held at the same temperature for 90 minutes for activation to obtain a high-performance carbon material. . Using the obtained high-performance carbon material of 555 ppm, a hydrogen peroxide decomposition test was carried out by stirring a 4000 ppm hydrogen peroxide solution (pH 2) at room temperature for 15 minutes. Table 1 shows the results of measurement of various physical properties and decomposition rate of hydrogen peroxide.

【0035】実施例 2 塩化マグネシウムに代えて炭酸マグネシウムを添加する
こと以外は実施例1と同様にして行い高性能炭素材料を
得た。表−1に得られた高性能炭素材料の物性および過
酸化水素の分解率の結果を示す。
Example 2 A high performance carbon material was obtained in the same manner as in Example 1 except that magnesium carbonate was added instead of magnesium chloride. Table 1 shows the results of the physical properties of the obtained high performance carbon material and the decomposition rate of hydrogen peroxide.

【0036】実施例 3 塩化マグネシウムに代えて硫酸マグネシウムを添加する
ことを以外は実施例1と同様にして行い高性能炭素材料
を得た。表−1に得られた高性能炭素材料の物性および
過酸化水素の分解率の結果を示す。
Example 3 A high performance carbon material was obtained in the same manner as in Example 1 except that magnesium sulfate was added instead of magnesium chloride. Table 1 shows the results of the physical properties of the obtained high performance carbon material and the decomposition rate of hydrogen peroxide.

【0037】実施例 4 塩化マグネシウムに代えて硝酸マグネシウム6水和物を
添加すること以外は実施例1と同様にして行い高性能炭
素材料を得た。表−1に得られた高性能炭素材料の物性
および過酸化水素の分解率の結果を示す。
Example 4 A high performance carbon material was obtained in the same manner as in Example 1 except that magnesium nitrate hexahydrate was added instead of magnesium chloride. Table 1 shows the results of the physical properties of the obtained high performance carbon material and the decomposition rate of hydrogen peroxide.

【0038】実施例 5 塩化マグネシウムに代えて酢酸マグネシウムを添加する
こと以外は実施例1と同様にして行い高性能炭素材料を
得た。表−1に得られた高性能炭素材料の物性および過
酸化水素の分解率の結果を示す。
Example 5 A high performance carbon material was obtained in the same manner as in Example 1 except that magnesium acetate was added instead of magnesium chloride. Table 1 shows the results of the physical properties of the obtained high performance carbon material and the decomposition rate of hydrogen peroxide.

【表1】 [Table 1]

【0039】表−1より、各マグンネシウム化合物の添
加は、いずれも高比表面積化に有効であり、かつCOD
源物質の分解活性が高く優れた性能を有することが明か
である。
From Table 1, addition of each magnesium compound is effective in increasing the specific surface area and COD.
It is clear that the source material has high decomposition activity and excellent performance.

【0040】実施例 6 硝酸マグネシウム6水和物を、それぞれ0.01g、
0.1g、2.5g、および5.0g添加すること以外
は実施例1と同様にして行い高性能炭素材料を得た。表
−2に得られた高性能炭素材料の物性および過酸化水素
の分解率の結果を示す。
Example 6 0.01 g of magnesium nitrate hexahydrate,
A high performance carbon material was obtained in the same manner as in Example 1 except that 0.1 g, 2.5 g and 5.0 g were added. Table 2 shows the results of the physical properties of the obtained high-performance carbon material and the decomposition rate of hydrogen peroxide.

【0041】[0041]

【表2】 [Table 2]

【0042】実施例 7 硝酸銀を、それぞれ0.01、0.1、0.5および
1.0を添加すること以外は実施例1と同様にして行い
高性能炭素材料を得た。得られた高性能炭素材料の物性
および過酸化水素の分解率の結果を表−3に示す。
Example 7 A high performance carbon material was obtained in the same manner as in Example 1 except that 0.01, 0.1, 0.5 and 1.0 of silver nitrate were added. The results of the physical properties of the obtained high performance carbon material and the decomposition rate of hydrogen peroxide are shown in Table-3.

【0043】実施例 8 酢酸銀0.5gを添加する以外は実施例1と同様にして
行い高性能炭素材料を得た。得られた高性能炭素材料の
物性および過酸化水素の分解率の結果を表−3に示す。
Example 8 A high performance carbon material was obtained in the same manner as in Example 1 except that 0.5 g of silver acetate was added. The results of the physical properties of the obtained high performance carbon material and the decomposition rate of hydrogen peroxide are shown in Table-3.

【0044】[0044]

【表3】 [Table 3]

【0045】比較例 1 ヤシガラ木炭(比表面積84m2 /g)を炭素質材料と
して用い実施例1と同様に加熱処理を行い炭素材料を得
た。得られた炭素材料の物性および過酸化水素の分解率
の結果を次に示す。
Comparative Example 1 Using coconut husk charcoal (specific surface area 84 m 2 / g) as a carbonaceous material, a heat treatment was carried out in the same manner as in Example 1 to obtain a carbon material. The results of the physical properties of the obtained carbon material and the decomposition rate of hydrogen peroxide are shown below.

【0046】[0046]

【表4】 [Table 4]

【0047】比較例 2 金属化合物の無添加、および硝酸マグネシウム6水和物
を500ppm添加すること以外は実施例1と同様にし
て炭素材料を得た。得られた炭素材料の物性および過酸
化水素の分解率の結果を示す。
Comparative Example 2 A carbon material was obtained in the same manner as in Example 1 except that no metal compound was added and 500 ppm of magnesium nitrate hexahydrate was added. The results of the physical properties of the obtained carbon material and the decomposition rate of hydrogen peroxide are shown.

【0048】[0048]

【表5】 [Table 5]

【0049】比較例 3 塩化マグネシウムに代えて硝酸カリウム3g添加するこ
と以外は実施例1と同様にして行い炭素材料を得た。得
られた炭素材料の物性および過酸化水素の分解率の結果
を示す。
Comparative Example 3 A carbon material was obtained in the same manner as in Example 1 except that 3 g of potassium nitrate was added instead of magnesium chloride. The results of the physical properties of the obtained carbon material and the decomposition rate of hydrogen peroxide are shown.

【0050】[0050]

【表6】 [Table 6]

【0051】[0051]

【発明の効果】本発明方法によれば高比表面積を有し、
かつCOD源物質分解活性の高い高性能炭素材料が得ら
れる。そして、マグネシウム、銀化合物等の金属化合物
の使用量が極めて少量であり装置の腐食性および混合物
による閉塞等がなく製造操作が簡単で連続化が容易であ
り経済的で工業的に有利に製造できる。
The method of the present invention has a high specific surface area,
Moreover, a high-performance carbon material having a high activity of decomposing a COD source substance can be obtained. In addition, the amount of metal compounds such as magnesium and silver compounds used is extremely small, there is no corrosiveness of the equipment and there is no clogging due to the mixture, the manufacturing operation is simple, the continuation is easy, and the manufacturing is economical and industrially advantageous. .

─────────────────────────────────────────────────────
─────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成6年8月16日[Submission date] August 16, 1994

【手続補正1】[Procedure Amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0001[Correction target item name] 0001

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0001】[0001]

【産業上の利用分野】本発明は、COD源物質に対して
高い分解能を有し、高比表面積を有する高性能な炭素材
料の製造方法に関する。本発明の炭素材料は、COD源
物質に対して高い分解能を有し、例えば過酸化水素、
ドラジン等の無機物質および有機物質に対して極めて優
れた分解活性を有することからこれらCOD源物質の分
解触媒として有用なものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for producing a high-performance carbon material having a high resolving power for a COD source material and a high specific surface area. Carbon material of the present invention has a high resolution for COD source material, such as hydrogen peroxide, arsenic
Since it has extremely excellent decomposition activity against inorganic substances such as dorazine and organic substances, it is useful as a decomposition catalyst for these COD source substances.

【手続補正2】[Procedure Amendment 2]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0006[Correction target item name] 0006

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0006】例えば、過酸化水素、ヒドラジン等の無機
物質または有機物質を含有する廃液をそのまま排出した
場合CODを高めるばかりでなく、廃水処理時、生物活
性汚泥処理装置に混入した場合、過酸化水素含有排水の
場合は分解にともなって発生する酸素ガスが懸濁物を浮
上させ、処理水の水質悪化の原因となるなど種々のトラ
ブルの原因となる。そこで、これらの廃液は、予め分解
処理して排出する必要があり、その分解方法として活性
炭を利用する方法がある。
For example, when a waste liquid containing an inorganic substance such as hydrogen peroxide or hydrazine or an organic substance is discharged as it is, not only the COD is increased but also when the waste liquid is mixed with a biological activated sludge treatment device, hydrogen peroxide In the case of contained wastewater, oxygen gas generated by decomposition causes suspension to float, causing various troubles such as deterioration of water quality of treated water. Therefore, it is necessary to decompose and discharge these waste liquids in advance, and there is a method of utilizing activated carbon as the decomposition method.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 細孔を有し比表面積100m2 /g以上
の炭素質材料にマグネシウム化合物または銀化合物を添
加した後、酸化性ガス雰囲気下で加熱処理することを特
徴とする高性能炭素材料の製法。
1. A high-performance carbon material characterized by adding a magnesium compound or a silver compound to a carbonaceous material having pores and having a specific surface area of 100 m 2 / g or more and then heat-treating it in an oxidizing gas atmosphere. Manufacturing method.
【請求項2】 マグネシウム化合物を炭素質材料に対し
て重量比で1:0.001〜1:0.5添加する請求項
1記載の高性能炭素材料の製法。
2. The method for producing a high performance carbon material according to claim 1, wherein the magnesium compound is added to the carbonaceous material in a weight ratio of 1: 0.001 to 1: 0.5.
【請求項3】 銀化合物を炭素質材料に対して重量比で
1:0.001〜1:0.1添加する請求項1記載の高
性能炭素材料の製法。
3. The method for producing a high performance carbon material according to claim 1, wherein the silver compound is added to the carbonaceous material in a weight ratio of 1: 0.001 to 1: 0.1.
JP30938593A 1993-12-09 1993-12-09 Manufacturing method of high performance carbon material Expired - Fee Related JP3539435B2 (en)

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* Cited by examiner, † Cited by third party
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JP2008285348A (en) * 2007-05-16 2008-11-27 Kuraray Chem Corp Silver-impregnated activated carbon, its production method and water purifier
WO2011055604A1 (en) * 2009-11-05 2011-05-12 日清紡ホールディングス株式会社 Carbon catalyst and use thereof
JP2018048063A (en) * 2016-09-01 2018-03-29 ファラッドパワー,インコーポレイテッド Manufacturing method of chemical active carbon
JP2018086614A (en) * 2016-11-28 2018-06-07 三菱瓦斯化学株式会社 Method for treating oxidizing substance-containing waste water

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008285348A (en) * 2007-05-16 2008-11-27 Kuraray Chem Corp Silver-impregnated activated carbon, its production method and water purifier
WO2011055604A1 (en) * 2009-11-05 2011-05-12 日清紡ホールディングス株式会社 Carbon catalyst and use thereof
US8372781B2 (en) 2009-11-05 2013-02-12 Nisshinbo Holdings, Inc. Carbon catalyst and use thereof
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