JP4314097B2 - Chemical substance adsorbent using bamboo charcoal - Google Patents

Chemical substance adsorbent using bamboo charcoal Download PDF

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JP4314097B2
JP4314097B2 JP2003374948A JP2003374948A JP4314097B2 JP 4314097 B2 JP4314097 B2 JP 4314097B2 JP 2003374948 A JP2003374948 A JP 2003374948A JP 2003374948 A JP2003374948 A JP 2003374948A JP 4314097 B2 JP4314097 B2 JP 4314097B2
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清 西尾
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株式会社チクノライフ
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本発明は、有機溶剤等を吸着し、空気や水を清浄化することが可能な吸着材に関する。   The present invention relates to an adsorbent capable of adsorbing an organic solvent or the like and purifying air or water.

建築用資材として壁紙や床板の貼り付け等に使用される接着剤中には、トルエンやホルムアルデヒド、アンモニア等の有機溶剤が含まれている。その他の建築用資材にも、様々な化学物質が使用されている。このような化学物質は、建造物の完成後から長期にわたって室内に揮発し続け、やがて人体に悪影響を及ぼすシックハウス症候群を引き起こすようになる。   An adhesive used for building materials, such as wallpaper and floorboard, contains an organic solvent such as toluene, formaldehyde, or ammonia. Various chemical substances are also used in other building materials. Such chemicals continue to volatilize indoors for a long time after the building is completed, and eventually cause sick house syndrome, which adversely affects the human body.

シックハウス症候群は、現在、非常に大きな問題となっており、有機溶剤の量を低減した接着剤や、人体に有害な成分を含まない接着剤等、極力化学物質を使用しない建築用資材についての研究が進められている。しかし、このような化学物質を全く使用しない建造物を作り上げることはほとんど不可能である。   Sick house syndrome is a very big problem at present, and research on building materials that do not use chemical substances as much as possible, such as adhesives that reduce the amount of organic solvents and adhesives that do not contain ingredients harmful to the human body. Is underway. However, it is almost impossible to build a building that does not use such chemicals at all.

そこで、このような有害物質を吸着したり分解したりすることが可能な物質についての研究が行われてきている。
このような中で、近年、細孔構造を有し、高い吸着性を示す活性炭が注目されており、活性炭に触媒を担持させて一酸化炭素等のガスの吸着材として使用する方法等が報告されている(特許文献1参照)。
Therefore, research has been conducted on substances capable of adsorbing and decomposing such harmful substances.
Under such circumstances, activated carbon having a pore structure and high adsorptivity has been attracting attention in recent years, and a method of using a catalyst on activated carbon as an adsorbent for gas such as carbon monoxide has been reported. (See Patent Document 1).

特開2002-126516号公報JP 2002-126516 A

以上のように、触媒を担持させた活性炭等は、ガスの吸着材等に利用されている。また、触媒を担持しない活性炭や炭が、室内の様々なにおいを除去する脱臭の目的等で利用されている。しかし、シックハウス症候群の原因といわれている、トルエンやホルムアルデヒド、アンモニア等の酸性及び塩基性のいずれの有機溶剤に対しても高い吸着能を有する吸着材についてはほとんど報告例がない。   As described above, activated carbon or the like carrying a catalyst is used as a gas adsorbent or the like. Further, activated carbon or charcoal that does not carry a catalyst is used for the purpose of deodorizing to remove various odors in the room. However, there are almost no reports on adsorbents having high adsorbability in acidic and basic organic solvents such as toluene, formaldehyde, and ammonia, which are said to cause sick house syndrome.

本発明が解決しようとする課題は、触媒を担持させずとも酸性及び塩基性のいずれの有機溶剤に対しても高い吸着能を有する、炭を使用した化学物質吸着材を提供することにある。   The problem to be solved by the present invention is to provide a chemical substance adsorbing material using charcoal, which has a high adsorbing ability for both acidic and basic organic solvents without supporting a catalyst.

上記課題を解決するために成された本発明に係る吸着材は、竹を650〜900℃で焼成して炭化した後、平均粒子径が5〜10μmになるように粉砕した竹炭微粉末75〜90重量%と、粘土状無機物質5〜15重量%と、バインダー樹脂5〜10重量%とを混合し、これを約200cell/inch 2 のセル密度を有するハニカム構造体に押し出し成形した有機化合物及び酸性・塩基性いずれの化学物質をも吸着可能な吸着材であって、前記粘土状無機物質が、セピオライト、カオリン、モンモリロナイト、緑泥石、カオリナイト、セリサイトのいずれか又はこれらの二以上の組み合わせであることを特徴とする。 The adsorbent according to the present invention made to solve the above problems is bamboo charcoal fine powder 75 ~ that is pulverized so that the average particle diameter is 5 ~ 10μm after baking and carbonizing the bamboo at 650 ~ 900 ° C. 90% by weight, 5-15% by weight of a clay-like inorganic substance, and 5-10% by weight of a binder resin are mixed, and this is extruded into a honeycomb structure having a cell density of about 200 cells / inch 2 An adsorbent capable of adsorbing both acidic and basic chemical substances, wherein the clay-like inorganic substance is sepiolite, kaolin, montmorillonite, chlorite, kaolinite, sericite, or a combination of two or more thereof. It is characterized by being.

本発明者らは、炭のうち、特に大きな比表面積を有し、細孔が数nm〜数十μmと広い分布を有する竹炭は、様々な分子量の物質を大量に吸着可能であると考えた。   The present inventors considered that, among charcoal, bamboo charcoal having a particularly large specific surface area and pores having a wide distribution of several nanometers to several tens of micrometers can adsorb a large amount of substances having various molecular weights. .

従来、炭を製造する際は、500〜1000℃程度で木材の焼成が行われており、焼成温度の違いにより炭の細孔構造が変化し、これにより比表面積が変化する。   Conventionally, when producing charcoal, wood is fired at about 500 to 1000 ° C., and the pore structure of the charcoal changes depending on the calcining temperature, thereby changing the specific surface area.

竹炭の場合、650〜900℃程度の温度で焼成した場合は、図1(a)に示すように径が数十μmの孔の周りに数nmの孔が蝟集した細孔構造を形成し、数十μmの孔の内部には、径がナノメートルオーダーのチューブ状構造体(以下、「ナノチューブ構造体」とする)(図1(b))が観察される。ナノチューブ構造体中には非常に細かい細孔が多数存在し、ナノチューブ構造体の存在により、特に分子量の小さな化学物質の吸着能が向上すると考えられる。しかし、1000℃以上で焼成すると、図2に示すように、ナノチューブ構造体はほとんど見られなくなる。   In the case of bamboo charcoal, when fired at a temperature of about 650 to 900 ° C., as shown in FIG. 1 (a), a pore structure in which pores of several nm are collected around pores having a diameter of several tens of μm, Inside the pores of several tens of μm, a tubular structure (hereinafter referred to as “nanotube structure”) having a diameter of the order of nanometers (FIG. 1B) is observed. There are a large number of very fine pores in the nanotube structure, and the presence of the nanotube structure is considered to improve the adsorption ability of a chemical substance having a particularly low molecular weight. However, when firing at 1000 ° C. or higher, as shown in FIG. 2, the nanotube structure is hardly seen.

また、焼成温度の違いにより、炭の細孔表面の官能基が変化する。炭化温度が低ければ細孔表面には酸性の官能基が存在するようになり、温度が高ければ塩基性の官能基が存在するようになるため、炭化温度が低い場合は塩基性の物質が炭に吸着されやすくなり、炭化温度が高い場合には、酸性の物質が吸着されやすくなるといわれている。例えば、備長炭の場合は1000〜1100℃で焼成が行われており、このような炭は酸性の物質を吸着しやすい。   Moreover, the functional group of the pore surface of charcoal changes with the difference in calcination temperature. If the carbonization temperature is low, acidic functional groups will be present on the pore surface, and if the temperature is high, basic functional groups will be present. It is said that acidic substances are easily adsorbed when the carbonization temperature is high. For example, in the case of Bincho charcoal, calcination is performed at 1000 to 1100 ° C., and such charcoal tends to adsorb acidic substances.

本発明者らは、竹を650〜900℃で焼成して得られる竹炭が、酸性及び塩基性のいずれの化学物質に対しても高い吸着能を有することを見出した。この竹炭の有する化学物質の吸着能力を更に高めるために、竹炭を微粉末化し、これを粘土状無機物質と、バインダー樹脂と混練し、図3に示すようなハニカム構造体を形成して比表面積を増大させ、効率的に化学物質等が吸着されるようにした。   The present inventors have found that bamboo charcoal obtained by baking bamboo at 650 to 900 ° C. has a high adsorbing ability for both acidic and basic chemical substances. In order to further enhance the adsorption ability of the chemical substance possessed by this bamboo charcoal, the bamboo charcoal is pulverized and kneaded with a clay-like inorganic substance and a binder resin to form a honeycomb structure as shown in FIG. In order to efficiently adsorb chemical substances and the like.

ハニカム構造体は、平均粒子径が5〜10μmになるように粉砕した竹炭微粉末75〜90重量%と、粘土状無機物質5〜15重量%と、バインダー樹脂5〜10重量%と、場合によっては適量の水とを混合し、これを例えばプレスや押し出し成形することにより作製する。この構造体の成形には、竹炭の焼成温度と竹炭微粉末の粒子径が重要であって、焼成温度が650〜900℃の場合は、均一なハニカム構造体を形成することが可能である。しかし、焼成温度が1000℃以上の竹炭の微粉末を使用した場合、ハニカム構造を形成することが困難になる。また、平均粒子径が5〜10μmよりも大きい場合も、ハニカム構造を形成することが困難になる。なお、竹炭の粉砕方法は特に問うものではなく、例えばジェットミル等により行うことができる。   The honeycomb structure has 75 to 90% by weight of bamboo charcoal fine powder pulverized so as to have an average particle size of 5 to 10 μm, 5 to 15% by weight of clay-like inorganic material, and 5 to 10% by weight of binder resin, depending on circumstances. Is prepared by mixing an appropriate amount of water, and pressing or extruding the mixture. For the formation of this structure, the firing temperature of bamboo charcoal and the particle size of bamboo charcoal fine powder are important. When the firing temperature is 650 to 900 ° C., a uniform honeycomb structure can be formed. However, when a bamboo charcoal fine powder having a firing temperature of 1000 ° C. or higher is used, it becomes difficult to form a honeycomb structure. Also, when the average particle size is larger than 5 to 10 μm, it becomes difficult to form a honeycomb structure. In addition, the grinding | pulverization method of bamboo charcoal is not ask | required in particular, For example, it can carry out with a jet mill etc.

粘土状無機物質としては、セピオライトやカオリン、モンモリロナイト、緑泥石、カオリナイト、セリサイト、及びこれらを二以上組み合わせたもの等を使用することが可能である。バインダーとしては、メチルセルロースやカルボキシメチルセルロース等のセルロース、デキストリン等の多糖類系樹脂、エポキシ樹脂、フラン樹脂、フェノールフラン樹脂、フェノール樹脂等を使用することが可能であり、バインダー樹脂は、吸着材の用途によって適宜選択する。吸着材を特に水の浄化に用いるような場合は、水に溶出しない、しかも人体に無害のバインダーを選択する必要がある。   As the clay-like inorganic substance, sepiolite, kaolin, montmorillonite, chlorite, kaolinite, sericite, or a combination of two or more thereof can be used. As the binder, it is possible to use celluloses such as methyl cellulose and carboxymethyl cellulose, polysaccharide resins such as dextrin, epoxy resins, furan resins, phenol furan resins, phenol resins, and the like. Select as appropriate. When the adsorbent is used for purification of water in particular, it is necessary to select a binder that does not elute into water and is harmless to the human body.

本発明に係る吸着材は、酸性及び塩基性のいずれの化学物質に対しても高い吸着能を有し、シックハウス症候群等の化学物質過敏症を引き起こす原因となるトルエン、ホルムアルデヒド、アンモニア等の化学物質を吸着除去することが可能である。   The adsorbent according to the present invention has high adsorbability for both acidic and basic chemical substances, and causes chemical substances such as toluene, formaldehyde, and ammonia that cause chemical sensitivity such as sick house syndrome. Can be removed by adsorption.

平均粒子径が7μmになるように粉砕した孟宗竹の竹炭微粉末800gと、粘土状無機物質(セピオライト)100gと、バインダー(メチルセルロース)60gとの混合物に水を150g加えた後、十分混練し、これを押し出し成形することによりハニカム構造体とした。その後これを170℃で24時間乾燥し、セル密度が約200cell/inch2のハニカム構造の吸着材を得た。 After adding 150 g of water to a mixture of 800 g of bamboo bamboo charcoal fine powder pulverized to an average particle size of 7 μm, 100 g of clay-like inorganic substance (sepiolite), and 60 g of binder (methylcellulose), this is kneaded thoroughly. Was extruded to form a honeycomb structure. Thereafter, this was dried at 170 ° C. for 24 hours to obtain a honeycomb structure adsorbent having a cell density of about 200 cells / inch 2 .

次に、この吸着材の化学物質(トルエン、アンモニア、ホルムアルデヒド、酢酸)の吸着能力を調べた。トルエンを実験開始時に50ppm含有する窒素、アンモニアを実験開始時に60ppm含有する窒素、ホルムアルデヒドを実験開始時に50ppm含有する窒素、酢酸を実験開始時に55ppm含有する窒素をそれぞれ用意し、同量の吸着材の存在下におけるこれらの化学物質の量の変化についてガスクロマトグラフ又はアンモニア検出装置又はホルムアルデヒド検出装置を用いて調べた。   Next, the adsorption ability of chemical substances (toluene, ammonia, formaldehyde, acetic acid) of this adsorbent was examined. Prepare nitrogen containing 50 ppm of toluene at the start of the experiment, nitrogen containing 60 ppm of ammonia at the start of the experiment, nitrogen containing 50 ppm of formaldehyde at the start of the experiment, and nitrogen containing 55 ppm of acetic acid at the start of the experiment. Changes in the amounts of these chemical substances in the presence were examined using a gas chromatograph, an ammonia detector or a formaldehyde detector.

その結果を図4〜図7に示す。これらの図には、吸着材を使用していない場合(ブランク)と、1000℃で焼成して得た備長炭、1000℃で焼成して得た竹炭、活性炭の存在下の化学物質量の変化についても併せて示す。
図4〜図7からわかるように、本発明の吸着材を用いた場合は、窒素中の化学物質の量はいずれも1時間以内に5分の1以下に低減し、24時間後にはほとんど消失している。このように、本発明の吸着材は高い化学物質の吸着能を有し、特に、図5から、アンモニアの吸着能において他の吸着材よりも優れていることがわかる。
The results are shown in FIGS. These figures show changes in the amount of chemical substances in the presence of no adsorbent (blank), Bincho charcoal obtained by firing at 1000 ° C, bamboo charcoal obtained by firing at 1000 ° C, and activated carbon. Is also shown.
As can be seen from FIGS. 4 to 7, when the adsorbent of the present invention is used, the amount of chemical substances in nitrogen is reduced to 1/5 or less within 1 hour and almost disappears after 24 hours. is doing. Thus, the adsorbent of the present invention has a high chemical substance adsorbing ability, and in particular, it can be seen from FIG. 5 that the adsorbing ability of ammonia is superior to other adsorbents.

以上のことから、本発明に係る化学物質吸着材は、同量の活性炭等と比較すると、酸性、塩基性のいずれの化学物質も急速に低減させる、優れた吸着能力を有することが示された。   From the above, it was shown that the chemical substance adsorbing material according to the present invention has an excellent adsorption capacity that rapidly reduces both acidic and basic chemical substances when compared with the same amount of activated carbon and the like. .

なお、上記においては窒素中に存在する化学物質量の変化について示したが、本発明に係る吸着材は、水中に存在する化学物質に対しても同様に高い吸着能力を示す。このため、本発明に係る吸着材は、空気清浄材として使用することができるだけでなく、水の清浄材としても使用することが可能である。また、通常の木炭のように、調湿剤や脱臭剤等として使用することはもちろん可能である。
更には、図8に示すように吸着材をキューブ状にすれば、室内装飾や建築用資材として、容易に使用することが可能である。なお、このキューブの大きさは任意に設定することができるが、一例としては、キューブの各辺の長さを3.5cm、ハニカムの各辺の長さを1mm、ハニカムの隔壁の厚さを0.3mmとしたものを挙げることができる。
In addition, although it showed about the change of the amount of chemical substances which exists in nitrogen in the above, the adsorbent which concerns on this invention shows the high adsorption capability similarly with respect to the chemical substance which exists in water. For this reason, the adsorbent according to the present invention can be used not only as an air cleaning material but also as a water cleaning material. Of course, it is possible to use it as a humidity control agent, a deodorizing agent, etc. like normal charcoal.
Furthermore, if the adsorbent is made in a cube shape as shown in FIG. 8, it can be easily used as an interior decoration or a building material. Although the size of the cube can be set arbitrarily, as an example, the length of each side of the cube is 3.5 cm, the length of each side of the honeycomb is 1 mm, and the thickness of the honeycomb partition walls is 0.3 mm. Examples of mm are listed.

また、本発明に係る化学物質吸着材は、日光に数時間当てることにより容易に再生されるため、何度でも使用可能であり、環境に対する負荷も小さい、優れた材料といえる。   Moreover, since the chemical substance adsorbing material according to the present invention is easily regenerated by being exposed to sunlight for several hours, it can be used any number of times, and can be said to be an excellent material with a small environmental load.

(a)800℃で焼成した竹炭の細孔構造のSEM写真、(b)800℃で焼成した竹炭のナノチューブ構造体部分を拡大したSEM写真。(a) SEM photograph of the pore structure of bamboo charcoal fired at 800 ° C., (b) SEM photograph of an enlarged part of the nanotube structure of bamboo charcoal fired at 800 ° C. 1000℃で焼成した竹炭の細孔構造のSEM写真。SEM photograph of the pore structure of bamboo charcoal fired at 1000 ° C. 本発明に係るハニカム構造を有する吸着材の概略構造図。1 is a schematic structural diagram of an adsorbent having a honeycomb structure according to the present invention. 各種吸着材を用いた場合の、窒素中に含まれるトルエン量の経時変化を示したグラフ。The graph which showed the time-dependent change of the amount of toluene contained in nitrogen at the time of using various adsorbents. 各種吸着材を用いた場合の、窒素中に含まれるアンモニア量の経時変化を示したグラフ。The graph which showed the time-dependent change of the ammonia amount contained in nitrogen at the time of using various adsorbents. 各種吸着材を用いた場合の、窒素中に含まれるホルムアルデヒド量の経時変化を示したグラフ。The graph which showed the time-dependent change of the amount of formaldehyde contained in nitrogen at the time of using various adsorbents. 各種吸着材を用いた場合の、窒素中に含まれる酢酸量の経時変化を示したグラフ。The graph which showed the time-dependent change of the amount of acetic acid contained in nitrogen at the time of using various adsorbents. キューブ形状を有する本発明に係る吸着材。The adsorbent according to the present invention having a cube shape.

Claims (2)

竹を650〜900℃で焼成して炭化した後、平均粒子径が5〜10μmになるように粉砕した竹炭微粉末75〜90重量%と、粘土状無機物質5〜15重量%と、バインダー樹脂5〜10重量%とを触媒を担持させずに混合し、これを200cell/inch 2 (31cell/cm 2 のセル密度を有するハニカム構造体に押し出し成形した、トルエン、アンモニア、ホルムアルデヒド、及び酢酸を吸着可能な吸着材であって、前記粘土状無機物質が、セピオライト、カオリン、モンモリロナイト、緑泥石、カオリナイト、セリサイトのいずれか又はこれらの二以上の組み合わせであることを特徴とする室内置き用の吸着材。 Bamboo charcoal powder baked at 650-900 ° C and carbonized and then ground to an average particle size of 5-10μm 75-90% by weight, clay-like inorganic substance 5-15% by weight, binder resin 5-10 wt% was mixed without supporting the catalyst, and this was extruded into a honeycomb structure having a cell density of 200 cell / inch 2 (31 cell / cm 2 ) , and toluene, ammonia, formaldehyde, and acetic acid were mixed. An adsorbent adsorbent, wherein the clay-like inorganic substance is sepiolite, kaolin, montmorillonite, chlorite, kaolinite, sericite, or a combination of two or more thereof. Adsorbent. 上記バインダー樹脂が、セルロース、多糖類系樹脂、エポキシ樹脂、フラン樹脂、フェノールフラン樹脂、フェノール樹脂のいずれか又はこれらの二以上の組み合わせであることを特徴とする請求項1に記載の吸着材。   The adsorbent according to claim 1, wherein the binder resin is any one of cellulose, polysaccharide-based resin, epoxy resin, furan resin, phenol furan resin, phenol resin, or a combination of two or more thereof.
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KR101400249B1 (en) 2012-02-10 2014-05-28 한국에너지기술연구원 Method for preparing carbon dioxide absorbent based on natural biomass and carbon dioxide absorbent based on natural biomass prepared by the same
CN110841596A (en) * 2019-12-02 2020-02-28 万安县朝荣毛竹林场 Preparation process of bamboo charcoal
CN111484665A (en) * 2020-04-29 2020-08-04 陈坤 Composite porous carbon-plastic unsaturated purifying new material and preparation method thereof

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