JP2005205123A - Char of discarded tatami (rush mat), discarded bamboo or the like and usage thereof - Google Patents

Char of discarded tatami (rush mat), discarded bamboo or the like and usage thereof Download PDF

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JP2005205123A
JP2005205123A JP2004043624A JP2004043624A JP2005205123A JP 2005205123 A JP2005205123 A JP 2005205123A JP 2004043624 A JP2004043624 A JP 2004043624A JP 2004043624 A JP2004043624 A JP 2004043624A JP 2005205123 A JP2005205123 A JP 2005205123A
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tatami
waste
bamboo
discarded
charcoal
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Shinsaku Ito
新作 伊藤
Masayoshi Tanaka
正義 田中
Mitsuyoshi Sakuma
光好 佐久間
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ITO TATAMITEN KK
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Abstract

<P>PROBLEM TO BE SOLVED: To utilize a char of a discarded tatami (rush mat), a discarded bamboo or the like as an adsorbent for malodorous substances, nitrogen oxides and organic volatile harmful substances, and to improve a glass wool by utilizing humidity conditioning properties thereof. <P>SOLUTION: The adsorbent of the char of the discarded tatami alone or preferably containing a 12-23 wt.% of ground char of the discarded bamboo is put into a cartridge, whereto the room air is circulated and allowed passage, to demonstrate high efficiency particularly in adsorption and removal of formalin in a new-built room. Commingling of these chars with a glass wool insulator demonstrates effects for preventing decrease of insulation efficiency due to moisture bead and development of fungus, and is established as a useful technique. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

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

本発明は、廃畳(畳床の藁、畳表のい草)・廃竹(竹、笹)の資源のリサイクルに関するものであり、これらを炭化した物を利用する、住宅など室内環境の改良浄化に関するものである。  The present invention relates to the recycling of resources of waste tatami (tatami floor cocoons, tatami mats) and waste bamboo (bamboo, firewood), and relates to the improvement and purification of indoor environments such as houses using carbonized materials. Is.

近年、新築住宅やマンションなどホルムアルデヒドを含む揮発性有機化合物(VOC)の低減化、除去が必須の問題となっている。
2003年7月には建築基準法が改正され、シックハウス病の原因物質とされるホルムアルデヒドの放散量が住宅建材について規制された。さらにトルエンやキシレンなども数年後には規制の対象になる現況にある。
In recent years, the reduction and removal of volatile organic compounds (VOC) containing formaldehyde has become an indispensable problem in newly built houses and condominiums.
In July 2003, the Building Standards Law was amended to limit the amount of formaldehyde that is a causative agent of sick house disease for residential building materials. In addition, toluene and xylene are subject to regulation in the next few years.

1997年東京都保健所はマンションなど機密性の高い住宅に住む人の健康度調査結果概要を報告した。これは調査希望者約600世帯を一酸化炭素、二酸化炭素、建材用接着剤などの有害化学物質・ホルムアルデヒド濃度測定他の分析であり、その結果、機密性の高い家ほど健康被害が高かったことを報告している。  In 1997, the Tokyo Metropolitan Public Health Center reported a summary of the results of a health survey of people living in highly confidential houses such as apartments. This is the analysis of about 600 households who want to investigate, such as carbon monoxide, carbon dioxide, adhesives for building materials, and other harmful chemical substances and formaldehyde concentration analysis. As a result, the higher the confidentiality of the house, the higher the health hazard. Has been reported.

高機密・高断熱建築は今や一般化しており、比例して住宅価格は上昇の一途であり、需要と供給のバランスから建材資材の合理化、大量生産が始まり化学物質との組み合わせが工夫された。
しかし、高機密・高断熱空間は外気との接触が阻害され、低濃度でも長時間室内で生活する主婦や妊婦、小児に与える影響が大きいと言われている。
High-confidence and high-insulation buildings are now common, and house prices are rising proportionally. From the balance between supply and demand, rationalization of building materials and mass production began, and combinations with chemical substances were devised.
However, it is said that high-confidence and high-adiabatic spaces have a large impact on housewives, pregnant women, and children who live indoors for a long time even at low concentrations.

これらの有害化学物質の吸着による低減化については、従来木炭・活性炭または竹炭などを押入れや部屋の隅に置く等の簡単な方法がとられている。木炭では吸着材としての性能に限界があること、また活性炭粉末や竹炭では高価であることにより、より安価な材料が求められている。  To reduce these harmful chemical substances by adsorption, conventional methods such as putting charcoal, activated carbon, or bamboo charcoal into a corner of a room or placing them in a room are used. Charcoal has a limit in performance as an adsorbent, and activated carbon powder and bamboo charcoal are expensive, so a cheaper material is required.

一方、畳は和風住宅にはなくてはならない建築材料であるが、古くなると産業廃棄物処理となり、新規交換や建屋解体に伴う排出量がかなりあり、処理施設の能力の限度から一部野放し状態とする事態も発生し、また雨などを含むと腐敗が発生し新たな公害に発展する要素をはらみ関係各層の悩みの種になって来おり、これら廃棄畳の有効な利用が求められている。  On the other hand, tatami mats are an indispensable building material for Japanese-style houses, but when they become old, they become industrial waste disposal, and the amount of emissions associated with new replacements and building demolition is considerable. In addition, it has become a source of concern for various layers, including the elements that cause corruption and develop into new pollution when it includes rain, etc., and effective use of these waste tatami mats is required .

さらに、内壁や天井裏に敷きこむグラスウールなどの断熱材は、従来高温度になると水滴が付着し立てかけたとき重さでだれたり落下したりして、本来の断熱材としての機能が失われ、またこれらの湿気によりダニが発生したりカビが発生したり、衛生上問題を生じる要因にもなっており、これらの湿気対策も求められている。
本発明は、廃畳(藁、い草)・廃竹(竹、笹)を利用することにより、これら廃棄物から生じる公害の発生を無くし、さらには資源の再利用により、有害化学物質・悪臭物質などの安価な吸着材ならびに安価な調湿材を得るものである。
In addition, heat insulating materials such as glass wool laid on the inner wall and the back of the ceiling, when the water becomes hot, dripping or dropping by the weight when the water drops adhere to it, the function as the original heat insulating material is lost, In addition, these moisture causes mites, molds, and hygiene problems, and countermeasures against these moisture are also required.
By using waste tatami (bamboo grass, grass) and waste bamboo (bamboo, wood), the present invention eliminates the occurrence of pollution caused by these wastes, and further, by reusing resources, harmful chemical substances and odorous substances Thus, an inexpensive adsorbing material and an inexpensive humidity conditioning material are obtained.

解決しようとする課題は、住宅やマンションなどホルムアルデヒドを含む揮発性有機化合物および悪臭物質であるアンモニア・硫化水素や公害物質である窒素酸化物・硫黄酸化物を効果的に吸着できること、また低費用でできること、ならびに畳・竹などの廃材を利用してこれらを実現することである。
また、グラスウールなどの断熱材が水滴の付着による断熱効果の低下を防ぐこと、さらに湿気によるダニやカビの発生を防止することである。
The problem to be solved is that it can effectively adsorb volatile organic compounds such as formaldehyde in houses and condominiums, malodorous substances such as ammonia and hydrogen sulfide, and pollutants such as nitrogen oxides and sulfur oxides, and at low cost. It is possible to achieve this by using waste materials such as tatami mats and bamboo.
Further, a heat insulating material such as glass wool prevents a decrease in the heat insulating effect due to adhesion of water droplets, and further prevents generation of ticks and molds due to moisture.

まず、加熱炉中に独立密閉式の炭化炉を装着したバッチ式炭化炉中に、廃畳を畳表をはぎ取ることなくそのまま適当な大きさに切り取ったものを入れ、摂氏400度〜900度で炭化する。得られるい草混入の藁炭は、壊れやすく取り出しなどの作業中に粉体がかなり出来るが、簡単な破砕により容易に5ミリメートル以下にすることが出来る。これらは断熱材であるマット状のグラスウールに、エアーガンで容易にからみ着かせることが出来、断熱材として利用される。また、この藁炭を通気性の良い紙袋・布などに入れて使い捨てやカートリッジタイプの吸着材として、室内空気を循環する系の中に位置させて、悪臭物質やホルムアルデヒドを含む揮発性有機化学物質の吸着に有効に使用されることである  First, in a batch-type carbonization furnace equipped with an independent closed-type carbonization furnace in the heating furnace, put the waste tatami cut into an appropriate size without stripping the tatami surface, and carbonize at 400 to 900 degrees Celsius. To do. The obtained charcoal mixed with grass is fragile and can be made into powder during the operation such as taking out, but can be easily reduced to 5 mm or less by simple crushing. These can be easily entangled with matte glass wool, which is a heat insulating material, with an air gun and used as a heat insulating material. In addition, this charcoal is placed in a well-ventilated paper bag or cloth and placed in a system that circulates indoor air as a disposable or cartridge-type adsorbent, and volatile organic chemicals containing malodorous substances and formaldehyde It is to be used effectively for adsorption

畳表をはぎ取り、これを適当な長さに切りこれを巻いてそのまま炭化すると、巻き物状のい草炭が出来る。これは藁炭より固く原形が保たれているが、通気性の良い紙袋・布などに入れて使い捨てやカートリッジタイプの吸着材として使用される。  If you cut off the tatami table, cut it into an appropriate length, roll it and carbonize it as it is, you will be able to make scroll-like grassy charcoal. It is harder than charcoal and retains its original shape, but is used as a disposable or cartridge type adsorbent in a paper bag or cloth with good ventilation.

竹炭や笹炭の場合は、廃竹・廃笹を適当な長さに切りさらに必要なら縦方向に割って前記した炭化炉により炭化する。竹炭・笹炭はかなり固く、前記マット状のグラスウールにからみ着かせる場合はなど、粉砕を要する。また、使い捨てやカートリッジタイプの吸着材として原形のまま使用出来るが、効率を高めるには粉砕された粉体の方が単位重量当たりの表面積が大きくなり、効率が良い。  In the case of bamboo charcoal or wood charcoal, the waste bamboo / waste wood is cut into an appropriate length, and if necessary, divided in the vertical direction and carbonized by the carbonization furnace described above. Bamboo charcoal / coal charcoal is quite hard and requires pulverization, for example, when it is entangled with the mat-like glass wool. Moreover, although it can be used as it is as a disposable or cartridge type adsorbent, in order to increase the efficiency, the pulverized powder has a higher surface area per unit weight and is more efficient.

畳炭単独での使用も出来るが、畳炭に竹・笹炭の粉砕物を10〜25重量%混合した物を使用すると、ホルムアルデヒドなどの吸着に好適であり、1ppm以下となし得る他吸着材としての使用時間が延長されるため好ましい。  Tatami charcoal can be used alone, but it is suitable for adsorption of formaldehyde and other adsorbents that can be used at 1 ppm or less if a mixture of 10-25% by weight of crushed bamboo and straw charcoal is mixed with tatami charcoal. Since the use time as is extended, it is preferable.

悪臭物質としてアンモニアのようなアルカリ物質の場合、低温(400度〜500度)での炭化物が弱酸性を示し吸着材として好適である。
また硫化水素などの悪臭物質、窒素酸化物、ホルムアルデヒド、トルエン、キシレンなどの有機揮発性有害物質は、さらに高温度で炭化したものが吸着材として優れている。
In the case of an alkaline substance such as ammonia as a malodorous substance, a carbide at a low temperature (400 ° C. to 500 ° C.) exhibits weak acidity and is suitable as an adsorbent.
In addition, malodorous substances such as hydrogen sulfide, and organic volatile harmful substances such as nitrogen oxides, formaldehyde, toluene, and xylene are excellent adsorbents that are carbonized at higher temperatures.

これらの畳炭は、形状が複雑であり多量の空気を抱え軽いので、グラスウールに容易にからみ着き、自重で落下することが少ない。またこれら炭の顕微鏡写真を撮ったところ、断面構造がハニカム状で内部も繊維状であり、悪臭物質、窒素酸化物、揮発性有害有機化合物の吸着および湿気の吸着が速やかであり、吸着容量も多い理由が明らかとなった。
湿気については、水分の吸着および脱着があるため、余分な水分を蓄えることなく、自重でずり落ちたり、落下することがなく、断熱効果も低下しない。かくして畳炭をからませたグラスウールは、湿気が調整されて水滴として存在せず、断熱材としての機能を低下させず、またダニやカビの発生が避けられる利点がある。
These tatami coals are complex in shape, have a large amount of air and are light, so they easily entangle with glass wool and do not fall under their own weight. Also, when micrographs of these charcoal were taken, the cross-sectional structure was honeycomb and the inside was fibrous, the adsorption of malodorous substances, nitrogen oxides and volatile harmful organic compounds and the adsorption of moisture were rapid, and the adsorption capacity was also high. Many reasons became clear.
As for moisture, since moisture is adsorbed and desorbed, excess moisture is not accumulated, and it does not slide or fall under its own weight, and the heat insulation effect does not deteriorate. Thus, glass wool entangled with tatami charcoal has the advantage that moisture is adjusted and does not exist as water droplets, does not deteriorate the function as a heat insulating material, and avoids the occurrence of mites and molds.

これらの吸着材料は、廃畳や竹などの廃材で充分な性能があり、新しい藁・竹である必要が無く、とくに廃畳の処分法として一石二鳥の資源リサイクルとして有用である。
さらに、有機揮発性有害物質の吸着に使用済の炭は、土壌に還元することで公害を発生させることは無い。
These adsorbent materials have sufficient performance with waste materials such as waste tatami and bamboo, and do not need to be new firewood or bamboo, and are particularly useful as resource recycling for two birds with one stone as a disposal method for waste tatami.
Furthermore, spent charcoal for adsorption of organic volatile harmful substances does not cause pollution by being reduced to the soil.

畳炭単独での使用も出来るが、畳炭に竹炭の粉砕物を12〜23重量%混合した物を使用すると、ホルムアルデヒドなどの吸着にも好適であり、容易に1ppm以下となし得る他吸着材としての使用時間が持続されるため好ましい。とくに新築の住宅の場合に、入居に先立って畳炭と竹炭の混合物を入れたものを装填した大型のカートリッジ内に、室内空気を終夜循環させ、ホルムアルデヒドなどの有害物質の吸着をさせることにより、健康に良い環境とすることが出来る。
また、築1〜3年でなおホルムアルデヒドなどの有害物質が出る部屋では、上記の小型のカートリッジで、風量の少ないファンで常時室内空気を循環運転し、良い環境を作ることが出来る。カートリッジ内の混合炭は2〜3ケ月に一度の交換で充分であり、さらにこれを他のシステム、例えば空調機や空気清浄機などとシステム化するなどして、吸着システムの低価格化のメリットを実現し長期の浄化を期待することが出来る。
Tatami charcoal can be used alone, but using admixture of 12-23 wt% of crushed bamboo charcoal with tatami charcoal is also suitable for adsorption of formaldehyde and other adsorbents that can easily be reduced to 1 ppm or less Since the use time as is sustained, it is preferable. Especially in the case of a newly built house, the indoor air is circulated overnight in a large cartridge loaded with a mixture of tatami and bamboo charcoal prior to moving in to adsorb harmful substances such as formaldehyde, It can be a healthy environment.
Also, in a room where formaldehyde and other harmful substances are still present after 1 to 3 years of construction, it is possible to create a good environment by constantly circulating indoor air with a fan with a small air volume, using the above-mentioned small cartridge. It is sufficient to replace the coal mixture in the cartridge once every two to three months, and further, this can be systematized with other systems such as air conditioners and air purifiers, etc. Can be expected and long-term purification can be expected.

まず廃畳や廃竹をそれぞれ単独で炭化する。炭化物を揮発性有害有機化合物の吸着および調湿に使用する場合は、それぞれ約5ミリメートル以下に破砕または粉砕されたものを使用するのが良い。畳表を巻物状に炭化したものは粉砕しても良いが、見た目が綺麗でありそのまま見える形で使用する方が、部屋に置いて使用する場合違和感が少ない。
なお、廃畳と廃竹を共存下で炭化すると、竹炭の表面が銀色になる。これを粉砕して吸着物としての機能があることも明らかである。
First, each of the waste tatami and waste bamboo is carbonized independently. When the carbide is used for adsorption and humidity control of volatile harmful organic compounds, it is preferable to use those that are crushed or ground to about 5 millimeters or less. The carbonized tatami surface may be crushed, but it is less uncomfortable to use it in a room when it is used in a clean and visible form.
When carbonized in the presence of waste tatami and bamboo, the surface of bamboo charcoal becomes silver. It is also clear that this can be crushed to function as an adsorbate.

揮発性有害有機化合物の吸着に関しては、とくにホルムアルデヒドの吸着には、廃畳炭単独よりも廃畳炭に廃竹炭を12〜23重量%入れた混合粉体が優れている。
廃畳炭の破砕は容易であるが、廃竹炭は硬いので粉砕機が必要となり、経済的に23重量%以上混合するメリットは無いと考えられる。
Regarding the adsorption of volatile harmful organic compounds, mixed powders containing 12-23 wt% of waste bamboo charcoal in waste tatami coal are superior to adsorption of formaldehyde, especially for adsorption of formaldehyde.
Although it is easy to crush waste tatami coal, it is considered that there is no merit of mixing 23% by weight or more economically because waste bamboo charcoal is hard and requires a pulverizer.

用途としての第一は、冷蔵庫・トイレの悪臭除去、揮発性有害有機化合物の吸着にあり、粉砕していない竹炭や活性炭・ヤシガラ活性炭などが市販にあるが、上記で記載の廃畳炭や廃畳炭に廃竹炭を12〜23重量%入れた混合粉体は見あたらない。
この廃畳炭や廃畳炭に廃竹炭を12〜23重量%入れた混合粉体は、通気性の和紙や布に包んで、冷蔵庫内・トイレ内・部屋内に置いて使用される。
また、自動車の排気管に組み入れて窒素酸化物や硫黄酸化物の吸着に有効である可能性がある。
The first application is removal of foul odors in refrigerators and toilets and adsorption of volatile toxic organic compounds. Unburned bamboo charcoal, activated carbon and coconut shell activated carbon are commercially available. There is no mixed powder with 12-23 wt% of waste bamboo charcoal in tatami coal.
This waste tatami coal or mixed powder containing 12-23 wt% of waste bamboo charcoal in waste tatami coal is wrapped in breathable Japanese paper or cloth and used in a refrigerator, toilet, or room.
In addition, it may be incorporated in an automobile exhaust pipe and effective for adsorption of nitrogen oxides and sulfur oxides.

用途としての第二は、マット状のグラスウール断熱材に廃畳炭や廃畳炭に廃竹炭を12〜23重量%入れた混合粉体をエァーガンにより絡ませたものである。グラスウール断熱材に15〜25容量%絡み着かせた物が容易に作れるが、これは揮発性有害有機化合物の吸着に寄与するだけでなく、断熱材が結露してその自量によりだれたりして断熱効果が低下することを防止する。さらに結露によりカビやダニが発生することをも防止し、一石三鳥の効果を発揮する。  The second use is a mixture of matt glass wool heat insulating material with waste tatami coal or 12-23 wt% of waste bamboo charcoal in waste tatami coal with an air gun. It is easy to make a glass wool insulation entangled with 15-25% by volume. This not only contributes to the adsorption of volatile harmful organic compounds, but the insulation is condensed and drooled by its own amount. Prevents the heat insulation effect from decreasing. Furthermore, it prevents mold and mites from being generated by condensation, and demonstrates the effect of three birds with one stone.

用途としての第三は、畳炭単独での使用も出来るが、畳炭に竹炭の粉砕物を10〜25容量%混合した物を使用すると、ホルムアルデヒドなどの吸着に好適であり、新築の住宅や新築の集合住宅の場合に、入居に先立って畳炭と竹炭の混合物を入れたものを装填した大型の金属製または樹脂製のカートリッジ内に、室内空気を終夜循環させ、ホルムアルデヒドなどの有害物質の吸着をさせることにより、健康に良い環境としてから入居することが出来る。この場合は壁材その他からホルムアルデヒドなどの揮発性有害有機化合物の蒸散を促すために、備え付けの暖房機器を稼働させ、室内空気温度を上げることが好ましい。必要ならカートリッジ内の畳炭などを新規なものと交換して続行できる。
この入居前ホルムアルデヒドなどの除去の後、なおホルムアルデヒドなどが蒸散する場合または築1〜3年でなお有機有害物質が出る部屋では、上記の小型のカートリッジで、風量の少ないファンで常時室内空気を循環運転し、良い環境を作ることが出来る。カートリッジ内の混合炭は2〜3ケ月に一度の交換で充分であり、さらにこれを他のシステ厶、例えば空調機や空気清浄機などとシステム化するなどして、吸着システムの低価格化のメリットが実現出来る。
Thirdly, the use of tatami charcoal alone is possible, but the use of tatami charcoal mixed with 10-25% by volume of crushed bamboo charcoal is suitable for adsorption of formaldehyde, etc. In the case of a newly built apartment house, indoor air is circulated overnight in a large metal or resin cartridge loaded with a mixture of tatami and bamboo charcoal prior to moving in, so that harmful substances such as formaldehyde can be circulated. By adsorbing, you can move into a healthy environment. In this case, in order to promote the evaporation of volatile harmful organic compounds such as formaldehyde from wall materials and the like, it is preferable to operate the installed heating equipment and raise the indoor air temperature. If necessary, you can continue by replacing the tatami charcoal in the cartridge with a new one.
After removal of formaldehyde before moving into the room, if formaldehyde evaporates, or in a room where organic harmful substances still appear in 1 to 3 years, the above-mentioned small cartridge circulates indoor air constantly with a fan with low airflow. You can drive and create a good environment. It is sufficient to replace the coal mixture in the cartridge once every two to three months. Furthermore, this can be systematized with other systems such as air conditioners and air purifiers to reduce the price of the adsorption system. Benefits can be realized.

株式会社シー・ワイ・シー社製CYT型炭化装置を用い、廃畳を約30センチ角に切断した物40個を乾留ボックスに入れ、ボックス内温度400度から〜最高温度が約800度で約10時間の炭化を実施し、畳炭(藁と少量のい草炭の混合物)を得た。  Using a CYT type carbonization device manufactured by Sea Y Sea Co., Ltd., 40 pieces of waste tatami cut into about 30 cm square are placed in a dry distillation box, and the temperature inside the box is from 400 degrees to the maximum temperature is about 800 degrees Carbonization was carried out for 10 hours to obtain tatami coal (a mixture of firewood and a small amount of charcoal).

実施例1と同様に、ただし廃畳の代わりに約4センチ径の廃竹を、長さ約30センチで4つに割った物を用いて炭化し廃竹炭を得、これを約5ミリメートル以下に粉砕した。  As in Example 1, but instead of waste tatami, waste bamboo charcoal having a diameter of about 4 centimeters is carbonized using a material divided into four with a length of about 30 centimeters to obtain waste bamboo charcoal, which is about 5 millimeters or less. To grind.

実施例1で得られた畳炭を5ミリメートル以下のもの2グラムを単独で、および該畳炭1.67グラムに実施例2で得られた竹炭粉0.33グラムの混合物計2グラムを用い、空気3リットル中に所定の濃度の有機有害ガスをにおい袋に入れて放置した。有害有機ガスの除去試験結果は、表1、表2、表3の通りであった。

Figure 2005205123
Figure 2005205123
Using 2 grams of tatami coal obtained in Example 1 of 5 mm or less alone, and 2 grams of the mixture of 0.33 grams of bamboo charcoal powder obtained in Example 2 for 1.67 grams of tatami coal. Then, an organic harmful gas having a predetermined concentration in 3 liters of air was placed in an odor bag and left standing. Tables 1, 2 and 3 show the results of the test for removing harmful organic gases.
Figure 2005205123
Figure 2005205123

廃畳より畳表をはがして、これを長さ約160センチ×幅約27センチに切ったものを、直径約6〜7センチに巻き実施例1と同様に炭化した。得られた炭化物は幅約27センチに多少収縮しているが、巻き物そのままに近い形状で得られた。
この1本を通気性の良いい草の和紙(株式会社水の子社製)に包み冷蔵庫に入れて置くと、1〜2時間後には冷蔵庫に特有の臭気が除去されていることが確認された。
The tatami surface was peeled off from the abandoned tatami and cut into a length of about 160 centimeters and a width of about 27 centimeters. The obtained carbide was somewhat contracted to a width of about 27 centimeters, but was obtained in a shape close to that of the roll.
It was confirmed that the odor peculiar to the refrigerator was removed after 1-2 hours when this one was wrapped in Japanese paper with good air permeability (manufactured by Mizuko Co., Ltd.) and placed in the refrigerator. .

実施例3で得られた畳炭単独および畳炭と竹炭の混合物を、厚み約2センチのマット状グラスウール断熱材に、エアーガンを用いて、グラスウール容量の約20%を吹きつけからみ着かせた。これら炭化物は良くからみ、自然落下する量は極く少なかった。
この炭をからませたグラスウールともとのグラスウールそのものを、湿熱試験器に入れ、相対湿度80%/温度40度で7日間行ったところ、対照のグラスウールそのものは水滴が発生しだれたりグラスウール繊維がからまったりしていたが、炭をからませたグラスウールには、水滴の発生は見られなかった。
About 20% of the glass wool capacity was blown out by spraying the tatami charcoal alone and the mixture of tatami charcoal and bamboo charcoal obtained in Example 3 onto a mat-shaped glass wool heat insulating material having a thickness of about 2 cm using an air gun. These carbides entangled well and the amount of spontaneous fall was very small.
When the glass wool itself entangled with this charcoal is placed in a wet heat tester and subjected to a relative humidity of 80% / temperature of 40 ° C. for 7 days, the control glass wool itself has water droplets or glass wool fibers entangled. However, no water droplets were seen on glass wool entangled with charcoal.

実施例1と同様に、ただし、乾留ボックス内最高温度480度で畳炭を得た。これの約50グラムをい草の和紙袋に入れ、トイレ内に置いておくと1〜2時間後には特異のアンモニア臭が消えることを確認した。  As in Example 1, however, tatami coal was obtained at a maximum temperature of 480 degrees in the dry distillation box. About 50 grams of this was put in a Japanese paper bag of grass and placed in the toilet, and it was confirmed that the unique ammonia odor disappeared after 1-2 hours.

新築和住宅の6畳の2部屋を、1つはそのままにして対照区とし、他の1つにはファンの送風口に、内径60センチメートル・高さ70センチメートルの円筒状金属製のカートリッジ内に、実施例3で得た畳炭と竹炭の混合物をカートリッジ高さ約50センチメートルに装填した。風量約2.5立方メートル/分のファンで室内空気を終夜循環させ、ホルムアルデヒドの有害物質の吸着をテストした。テスト期間を通して両部屋の温調機の温度設定は26度とした。
2時間後にホルムアルデヒド検知管で室内空気を測定した結果は以下の通りであった。
対照区のホルムアルデヒド濃度 6ppm
実験区のホルムアルデヒド濃度 検知せず
Two 6-tatami rooms in a newly built Japanese house are left as they are for reference, and the other one is a cylindrical metal cartridge with an inner diameter of 60 centimeters and a height of 70 centimeters at the fan vent. Inside, the mixture of tatami coal and bamboo charcoal obtained in Example 3 was loaded to a cartridge height of about 50 centimeters. Indoor air was circulated overnight with a fan with an air volume of about 2.5 cubic meters / minute to test the adsorption of formaldehyde harmful substances. The temperature setting of the temperature controllers in both rooms was 26 degrees throughout the test period.
The results of measuring the indoor air with a formaldehyde detector tube after 2 hours were as follows.
Control formaldehyde concentration 6ppm
No formaldehyde concentration detected in the experimental area

実施例7で対照区とした部屋に、実施例4で作った長さ約24センチメートル・直径約6〜7センチメートルの巻物状廃畳表炭(い草炭)30本を部屋の一隅に、新聞紙の上に三段に並べて置き、これに実施例7で用いたファンで空気を当てる様にして室内空気を終夜循環さた。部屋の温調機の温度設定は26度とした。
1日後にホルムアルデヒド検知管で室内空気を測定した結果は、ホルムアルデヒド濃度1ppm以下であった。
In the room designated as the control zone in Example 7, 30 roll-shaped scraped surface coals (ie, charcoal) having a length of about 24 centimeters and a diameter of about 6 to 7 centimeters made in Example 4 were placed in the corner of the newspaper. The room air was circulated all night so that the air was applied to it with the fan used in Example 7. The temperature setting of the room temperature controller was 26 degrees.
One day later, the result of measuring indoor air with a formaldehyde detector tube was a formaldehyde concentration of 1 ppm or less.

Claims (4)

摂氏400度から900度の温度範囲で炭化した廃畳(藁・い草)の畳炭の単独、または該廃畳炭に同温度範囲で炭化した廃竹・廃笹の炭化物を5ミリメートル以下に粉砕した粉体を、12〜23重量%配合したことを特徴とする、アンモニアなどの悪臭物質、窒素酸化物および有機揮発性有害物質を吸着させる炭化物ならびに炭化組成物。Abandoned tatami coal (carp / grass) carbonized in the temperature range of 400 to 900 degrees Celsius, or waste bamboo / waste charcoal carbonized in the same temperature range to less than 5 millimeters. A carbide and a carbonized composition for adsorbing malodorous substances such as ammonia, nitrogen oxides and organic volatile harmful substances, characterized by blending 12 to 23% by weight of the obtained powder. 廃畳の畳表を剥ぎ取りこれを長さの方向に巻き、直径5〜10センチメートルの巻き物状としたものを、摂氏400度から900度の温度範囲で炭化して得られる巻き物状の悪臭物質、窒素酸化物および有機揮発性有害物質を吸着させる炭化物。A scroll-like malodorous substance obtained by stripping the tatami surface of an abandoned tatami and winding it in the length direction to form a scroll having a diameter of 5 to 10 centimeters in a temperature range of 400 to 900 degrees Celsius. , Carbides that adsorb nitrogen oxides and organic volatile harmful substances. 請求項1記載の廃畳炭または該畳炭に廃竹・廃笹の炭化物粉体12〜23重量%配合物を、マット状グラスウール断熱材にエアーガンにより該グラスウール断熱材の15〜25容量%にあたる量をからみ着かせることを特徴とする、調湿性、耐カビ性の断熱材。The waste tatami coal according to claim 1 or a mixture of 12-23 wt% of waste bamboo / waste carbide powder to the tatami charcoal, and 15-25% by volume of the glass wool insulation by air gun on a matte glass wool insulation. Humidity-controlling and mold-resistant insulation, characterized by entanglement. 請求項1記載の廃畳炭または該畳炭に廃竹・廃笹の炭化物粉体12〜23重量%配合物を、カートリッジ内に入れ、室内空気を循環するファンの送風側に導入管を取り付け、その先に該カートリッジをつなぎ、室内空気を該カートリッジ内に循環通過させることを特徴とする、有機揮発性有害物質を吸着除去する効率的方法。The waste tatami coal according to claim 1 or a mixture of 12-23 wt% of waste bamboo and waste carbide powder in the tatami coal and placed in a cartridge, and an introduction pipe is attached to the blower side of a fan that circulates indoor air An efficient method for adsorbing and removing organic volatile harmful substances, characterized in that the cartridge is connected to the tip of the cartridge and room air is circulated through the cartridge.
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JP6028186B1 (en) * 2015-10-23 2016-11-16 村上産業株式会社 Rush charcoal, rush charcoal
JP6136040B1 (en) * 2016-07-28 2017-05-31 村上産業株式会社 Manufacturing method of carbide
JP2018016783A (en) * 2017-03-10 2018-02-01 村上産業株式会社 Manufacturing method of carbide

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JP2003080061A (en) * 2001-09-12 2003-03-18 Toshiba Corp Functional carbonizing material and method for manufacturing the same
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JPH09248550A (en) * 1996-03-14 1997-09-22 Toa Neichiyaa Planning:Kk Treatment of waste
JP2001064653A (en) * 1999-08-31 2001-03-13 Noriaki Nakamura Production of rush charcoal and gas adsorbent using the same
JP2002249922A (en) * 2000-08-01 2002-09-06 Takashima:Kk Single fiber containing carbon powder in interior of fiber, processed material and loose fiber mass composed of the same single fiber, processed material and loose fiber mass comprising carbon powder on fiber surface or among fibers and method producing the same
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JP6028186B1 (en) * 2015-10-23 2016-11-16 村上産業株式会社 Rush charcoal, rush charcoal
JP6136040B1 (en) * 2016-07-28 2017-05-31 村上産業株式会社 Manufacturing method of carbide
JP2018016737A (en) * 2016-07-28 2018-02-01 村上産業株式会社 Manufacturing method of carbide
JP2018016783A (en) * 2017-03-10 2018-02-01 村上産業株式会社 Manufacturing method of carbide

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