JP2007015907A - Adsorbent charcoal, water-purifying agent, water-purifying sachet, water-purifying substrate and method for removing oil film - Google Patents

Adsorbent charcoal, water-purifying agent, water-purifying sachet, water-purifying substrate and method for removing oil film Download PDF

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JP2007015907A
JP2007015907A JP2005210000A JP2005210000A JP2007015907A JP 2007015907 A JP2007015907 A JP 2007015907A JP 2005210000 A JP2005210000 A JP 2005210000A JP 2005210000 A JP2005210000 A JP 2005210000A JP 2007015907 A JP2007015907 A JP 2007015907A
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adsorbed charcoal
charcoal
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water purification
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Toshiya Ueda
俊也 上田
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UEDA HOLDINGS KK
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
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    • Y02A20/20Controlling water pollution; Waste water treatment
    • Y02A20/204Keeping clear the surface of open water from oil spills

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Abstract

<P>PROBLEM TO BE SOLVED: To provide a novel adsorbent charcoal capable of efficiently removing oily components (oil film) when sprinkled on water surface, by floating on the water surface over a long period of time and staying in contact with the oily components (oil film) that are contained in and floating on the surface of natural water area such as rivers, lakes and seas, waste water such as industrial waste water, sewage, rainwater pools, etc., a water-purifying agent, a water-purifying sachet, a water-purifying substrate, and a method for removing the oil film. <P>SOLUTION: The adsorbent charcoal is obtained by using a coconut mesocarp as a raw material and subjecting it to heating and a carbonization treatment. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、特に、河川、湖沼、海などの自然水域や、工場廃水等の廃水、下水、雨水の溜池などに含まれ、その水面上に浮遊した状態で存在する油分(油膜)を効率よく除去するための吸着炭、水質浄化剤、水質浄化袋、水質浄化基材及び油膜の除去方法に関する。   In particular, the present invention efficiently includes oil (oil film) that is contained in natural water areas such as rivers, lakes, and seas, waste water such as factory waste water, sewage, and rainwater ponds and that floats on the surface of the water. The present invention relates to a method for removing adsorbed charcoal, a water purification agent, a water purification bag, a water purification substrate, and an oil film for removal.

ガソリン、軽油、灯油、ジェット燃料などの燃料を取り扱うガソリンスタンドや飛行場、更に軍用基地などにおいて、誤ってこぼしてしまった油や、各種工場などにおいて発生する有機溶剤を含んだ工場廃水等の廃水などは、相当注意深く取り扱っても雨水の溜池や下水、廃水に混入してしまい、その水面上に拡散・浮遊した状態で薄い油膜を形成して流出し、その後、河川、湖沼、海などの自然水域に流れ込み、自然環境を悪化させるといった問題が生じる。   Oil that has been accidentally spilled at gasoline stations, airfields, and military bases that handle fuel such as gasoline, light oil, kerosene, and jet fuel, and wastewater such as factory wastewater that contains organic solvents generated at various factories Are mixed into rainwater ponds, sewage, and wastewater even when handled with great care, and form a thin oil film that scatters and floats on the surface of the water, then flows out and then flows into natural waters such as rivers, lakes, and seas. The problem arises that the natural environment deteriorates.

そのため、このような水面上の油膜を除去するための手段が研究・開発されている(例えば、特許文献1〜5。)。   For this reason, means for removing such an oil film on the water surface have been researched and developed (for example, Patent Documents 1 to 5).

特開平8−182929号公報JP-A-8-182929 実開平6−85035号公報Japanese Utility Model Publication No. 6-85035 特開平6−170359号公報JP-A-6-170359 特開2004−131855号公報JP 2004-131855 A 特開2002−346380号公報JP 2002-346380 A

これら特許文献1〜5に記載された油膜の除去手段は、油分を吸着するマットやシートを用いるものであるが、このマットやシートによる油の吸着には時間がかかり、又、水面上の広範囲に広がった油膜を除去するためには、相当な数のマットやシートを敷設する必要があり、多大なコストと労力更に手間を要するといった問題がある。   The oil film removing means described in these Patent Documents 1 to 5 uses a mat or sheet that adsorbs oil, but it takes time to adsorb oil by the mat or sheet, and a wide range on the water surface. In order to remove the oil film spread over a large area, it is necessary to lay a considerable number of mats and sheets, and there is a problem that a great deal of cost and labor are required.

ところで、水中の不純物を吸着除去することができる材料としては、活性炭が最も簡単且つ効率が良いということで一般的に多用されている。   By the way, as a material capable of adsorbing and removing impurities in water, activated carbon is generally used because it is the simplest and most efficient.

活性炭は、木材、おがくず、木材乾留物、木炭、椰子殻及びリグニン等を原料(活性炭原料)として、これに加熱、炭化処理を施すことによって、気体や色素等に対する吸着能力を高めたものであり、生活臭等の臭いの成分やホルマリン、エチルベンゼン又はキシレン等のシックハウスの原因となるVOCガス等の吸着成分に対する吸着能力が比較的高く、且つ安価であることから、現在、水の浄化、冷蔵庫や下駄箱の消臭剤或いは空気清浄機のフィルターその他の消臭・吸着製品の分野において、最も広く使用されている。   Activated carbon uses wood, sawdust, wood distillate, charcoal, coconut shell, lignin, etc. as raw materials (activated carbon raw material), and is heated and carbonized to increase its adsorption capacity for gases and pigments. Because of its relatively high and low-cost adsorption capacity for odorous components such as life odors and adsorbed components such as formalin, ethylbenzene or xylene such as VOC gas that cause sick house, water purification, refrigerators, etc. It is most widely used in the field of deodorizers for clogs or air purifier filters and other deodorant / adsorption products.

そして、加熱、炭化処理直後の活性炭は比較的比重が小さいことから水に浮くことができるのであり、そのため、このような活性炭を油膜が生じた水面上に相当量散布すれば、油分を吸着して水質を浄化することが可能になる。   Since activated carbon immediately after heating and carbonization treatment has a relatively low specific gravity, it can float on water. Therefore, if a large amount of such activated carbon is sprayed on the water surface on which an oil film is formed, the oil is adsorbed. It becomes possible to purify the water quality.

しかしながら、このような活性炭による吸着特性は、油分に対する吸着より、水分に対する吸着の方が優先するので、活性炭を水面上に散布すると、短期間で水分を吸収し、その結果、比重が増大して当該活性炭が水面下に沈むため、油分の吸着効率が非常に悪く、又、油を吸着したまま水面下に沈んだ活性炭を回収する作業も必要となり、大変な煩わしさが生じる。   However, since the adsorption characteristics by activated carbon have priority over adsorption by moisture over adsorption by oil, when activated carbon is sprayed on the water surface, moisture is absorbed in a short period of time, resulting in an increase in specific gravity. Since the activated carbon sinks below the surface of the water, the oil adsorption efficiency is very poor, and it is also necessary to collect the activated carbon that has submerged under the surface of the water while adsorbing the oil, resulting in great inconvenience.

そこで、本発明者は、前記課題を解決するために鋭意検討を重ねた結果、ココヤシの中果皮を原料として用い、これに加熱、炭化処理を施してなる吸着炭を開発するに至ったのである。   Therefore, as a result of intensive studies to solve the above problems, the present inventor has developed an adsorbed charcoal using coconut mesocarp as a raw material, which is heated and carbonized. .

即ち、本発明者は、ココヤシの中果皮(原料)を電子顕微鏡で観察すると、この中果皮(原料)にはその表面ないし内部において、独立孔同士や独立孔と連続孔が一体形となった複雑な網目構造を形成して無数に存する細孔同士が隣接したハニカム構造を形成している点に着目し、ココヤシの中果皮に加熱、炭化処理を施せば、無数に存する細孔同士が隣接したハニカム構造の吸着炭となるので、木材、おがくず、木材乾留物、木炭、椰子殻或いはリグニン等を原料とする従来の活性炭よりも比重が小さい炭化物質(吸着炭)となり、このようなココヤシの中果皮を原料とする吸着炭を水面上に散布すれば、多少の水分を吸収しても水面上に浮遊し続け、長期間にわたって水面上の油膜と接触させることが可能になるとの知見を得たのである。   That is, when the inventor observed the coconut mesocarp (raw material) with an electron microscope, the mesocarp (raw material) had independent holes or independent holes and continuous holes integrated on the surface or inside thereof. Paying attention to the fact that a honeycomb structure in which countless pores are adjacent to each other by forming a complex network structure, heating and carbonization treatment is applied to the coconut mesocarp, and countless pores are adjacent to each other Since the adsorbed charcoal has a honeycomb structure, it becomes a carbonized material (adsorbed charcoal) having a specific gravity smaller than that of conventional activated carbon made from wood, sawdust, wood dry matter, charcoal, coconut shell or lignin. Obtained knowledge that if adsorbed charcoal made from mesocarp is sprayed on the surface of the water, even if some moisture is absorbed, it will remain floating on the surface of the water and can be in contact with the oil film on the surface for a long period of time. Is

又、上述のように、ココヤシの中果皮を原料として得られた吸着炭は、独立孔同士や独立孔と連続孔が一体形となった複雑なハニカム構造をしているため、各細孔のサイズが非常に広範な構造となっているので、あらゆる種類の油分に対する吸着性に優れるとの知見も得たのである。   In addition, as described above, the adsorbed charcoal obtained using coconut mesocarp as a raw material has a complicated honeycomb structure in which independent holes and independent holes and continuous holes are integrated. Since the structure has a very wide range of sizes, we have also learned that it has excellent adsorbability for all kinds of oils.

ところで、従来、ココヤシの中果皮は、繊維成分以外利用価値が殆んどなく、殆んど利用されることなく廃棄されているのが現状であり、至極低コストで原材料の調達が可能であり、又、廃棄物利用の観点からも大きな利点があるとの知見も得たのである。   By the way, conventionally, coconut mesocarp has almost no utility value other than fiber components, and it has been discarded without being used at all, and raw materials can be procured at extremely low cost. In addition, they also learned that there are significant advantages from the viewpoint of waste utilization.

本発明は、前記知見に基づき完成されたものであって、散布すると水面上に長期間にわたって浮遊し、その結果、河川、湖沼、海などの自然水域や、工場廃水等の廃水、下水、雨水の溜池などに含まれ、その水面上に浮遊した状態で存在する油分(油膜)と長期間にわたって接触するので、当該油分(油膜)を効率よく除去し得る、新規な吸着炭、水質浄化剤、水質浄化袋、水質浄化基材及び油膜の除去方法を提供することを目的とするものである。   The present invention has been completed based on the above knowledge, and when dispersed, floats on the water surface for a long period of time. As a result, natural water areas such as rivers, lakes, and seas, waste water such as factory waste water, sewage, and rainwater New adsorbed charcoal, water purification agent, which can efficiently remove the oil (oil film) because it is in contact with the oil (oil film) that is contained in the pond of the water and floats on the water surface for a long period of time. An object of the present invention is to provide a water purification bag, a water purification substrate, and a method for removing an oil film.

前記目的を達成するため、本発明に係る吸着炭は、ココヤシの中果皮を原料として用い、この原料に加熱、炭化処理を施したことを特徴とするものである。   In order to achieve the object, the adsorbed charcoal according to the present invention is characterized in that coconut mesocarp is used as a raw material, and the raw material is heated and carbonized.

ここで、ココヤシは、その最も中央に配される「胚乳」、その外側を包む硬い殻からなる「内果皮(ヤシガラ)」、及び内果皮を包むように取り巻く「中果皮」の三層構造となっており、前記胚乳は主として食用に供され、又、前記内果皮(ヤシガラ)はヤシガラ活性炭の原料などに供されている。   Here, the coconut palm has a three-layer structure of “endosperm” arranged at the center, “endocarp (palm gall)” consisting of a hard shell that wraps the outside, and “mesocarp” surrounding the inner pericarp. The endosperm is mainly used for food, and the inner pericarp (coconut shell) is used as a raw material for coconut shell activated carbon.

その一方で、中果皮については、繊維成分以外、殆んど利用されることなく廃棄されているのが現状である。   On the other hand, as for the mesocarp, it is the present condition that it is discarded almost without being used except the fiber component.

しかしながら、本発明者が、このココヤシの中果皮の利用について鋭意検討したところ、ココヤシの中果皮は、独立孔同士や独立孔と連続孔が一体形となった複雑なハニカム構造をしており、このココヤシの中果皮に加熱、炭化処理を施せば、複雑なハニカム構造の吸着炭が得られるのであり、この吸着炭は、木材、おがくず、木材乾留物、木炭、椰子殻或いはリグニン等を原料とする従来の活性炭よりも、比重が小さい炭化物質(吸着炭)となることが判明したのである。   However, when the present inventors diligently studied the use of this coconut mesocarp, the coconut mesocarp has a complex honeycomb structure in which independent holes and independent holes and continuous holes are integrated, By heating and carbonizing the coconut skin of this coconut, an adsorbed charcoal with a complex honeycomb structure can be obtained. This adsorbed charcoal is made from wood, sawdust, wood dry distillate, charcoal, coconut shell or lignin. It became clear that it becomes a carbonized substance (adsorbed charcoal) with a smaller specific gravity than the conventional activated carbon.

そして、このようなココヤシの中果皮を原料とする吸着炭を水面上に散布すれば、多少の水分を吸収しても水面上に浮遊し続け、長期間にわたって水面上の油分(油膜)と接触し続けることが可能になるのである。その結果、この吸着炭は、前述の油分(油膜)を効率良く、吸着、除去し得るのである。   And if the adsorbed charcoal using coconut mesocarp as a raw material is sprayed on the surface of the water, it will float on the surface of the water even if it absorbs some water, and it will contact the oil (oil film) on the surface for a long time. It will be possible to continue. As a result, this adsorbed charcoal can adsorb and remove the aforementioned oil (oil film) efficiently.

又、上述のように、ココヤシの中果皮を原料として得られた吸着炭は、独立孔同士や独立孔と連続孔が一体形となった複雑なハニカム構造をしているため、各細孔のサイズが非常に広範な構造となっており、このため、あらゆる種類の油分に対する吸着性に優れるのである。   In addition, as described above, the adsorbed charcoal obtained using coconut mesocarp as a raw material has a complicated honeycomb structure in which independent holes and independent holes and continuous holes are integrated. The structure has a very wide range of sizes, so that it has excellent adsorptivity for all kinds of oils.

しかも、前述のように、ココヤシの中果皮は、繊維成分以外利用価値が殆んどなく、殆んど利用されることなく廃棄されているのが現状であり、至極低コストでの原料の調達が可能であり、又、廃棄物利用の観点からも大きな利点があるのである。
以下、本発明の吸着炭について更に詳細に説明する。
Moreover, as described above, coconut mesocarp has almost no utility value other than fiber components, and it is currently discarded without being used, and procurement of raw materials at extremely low cost. In addition, there is a great advantage from the viewpoint of waste utilization.
Hereinafter, the adsorbed coal of the present invention will be described in more detail.

本発明の吸着炭は、ココヤシの中果皮を原料として用い、この原料に加熱、炭化処理を施してなるものである。   The adsorbed charcoal of the present invention is obtained by using coconut mesocarp as a raw material and heating and carbonizing the raw material.

ところで、ココヤシの中果皮は、繊維成分を含むものであり、本発明の吸着炭においては、係る繊維成分を含んだ状態のままの中果皮に対して加熱、炭化処理を施しても良いのであるが、吸着炭において繊維成分が多く含まれると、吸着炭全体としての比重が大きくなることから、本発明においては、特に、ココヤシの中果皮から、更に繊維成分を除いたもの原料として用いることが好ましい。   By the way, coconut mesocarp contains a fiber component, and in the adsorbed charcoal of the present invention, the mesocarp that contains the fiber component may be heated and carbonized. However, if the adsorbed charcoal contains a large amount of fiber components, the specific gravity of the adsorbed charcoal as a whole will increase. preferable.

本発明において、「加熱、炭化処理を施す」とは、原料(ココヤシの中果皮)に対して熱を加えて炭化する処理のことをいい、この加熱、炭化処理における処理温度としては、前記原料を炭化できる温度であれば特に限定されるものではないが、本発明の場合、350〜850℃の範囲とすることが好ましく、この加熱、炭化処理温度が350℃未満では炭化が不十分となって油(油膜)の吸着性が悪いのであり、一方、850℃を超えると、前述のハニカム構造が破壊される恐れが生じる上、省エネルギーの観点からも好ましくないのである。   In the present invention, “heating and carbonizing” refers to a process of heating and carbonizing the raw material (coconut mesocarp). Is not particularly limited as long as the temperature can be carbonized, but in the case of the present invention, it is preferably in the range of 350 to 850 ° C., and if this heating and carbonization temperature is less than 350 ° C., the carbonization becomes insufficient. Oil (oil film) adsorbability is poor, while if it exceeds 850 ° C., the honeycomb structure described above may be destroyed, and it is not preferable from the viewpoint of energy saving.

又、本発明においては、更に、吸着能力を高めることを目的として、原料(ココヤシの中果皮)を加熱、炭化処理と共に、賦活処理を施したり、或いは原料(ココヤシの中果皮)を加熱、炭化処理後、賦活処理を施すことが好ましい。   Further, in the present invention, for the purpose of further increasing the adsorption capacity, the raw material (coconut mesocarp) is heated, carbonized, and activated, or the raw material (coconut mesocarp) is heated and carbonized. It is preferable to carry out an activation treatment after the treatment.

この賦活処理は、通常の活性炭の製造の際に施される吸着能力を高めるための処理と同様のものであり、大きく分けて「ガス賦活法」と「薬品賦活法」の二種類がある。   This activation treatment is the same as the treatment for increasing the adsorption capacity performed during the production of ordinary activated carbon, and is roughly divided into two types, a “gas activation method” and a “chemical activation method”.

前者のガス賦活法は、工業的によく用いられる一般的な方法であり、本発明の場合、前述の吸着炭を、更に水蒸気、二酸化炭素等の雰囲気中において、特に、温度650〜850度程度で処理する方法である。   The former gas activation method is a general method often used industrially, and in the case of the present invention, the adsorbed charcoal described above is further in an atmosphere of water vapor, carbon dioxide, etc., particularly at a temperature of about 650 to 850 degrees. It is the method of processing with.

一方、後者の薬品賦活法は、本発明の場合、前述の吸着炭に塩化亜鉛水溶液等の処理液を染み込ませ、特に、350〜700℃程度の温度条件下で炭化と賦活を一挙に行う方法である。   On the other hand, in the case of the present invention, the latter chemical activation method is a method of impregnating the above-mentioned adsorbed charcoal with a treatment solution such as an aqueous zinc chloride solution, and in particular, performing carbonization and activation all at once under a temperature condition of about 350 to 700 ° C. It is.

即ち、本発明において、いずれの賦活処理を用いるかについては、特に限定されるものではないが、賦活処理温度を通常より若干低めに設定することにより、油分に対する吸着力が増すことが判明しており、従って、本発明においては、350〜850℃程度、更に好ましくは、400〜850℃程度の通常より比較的低温にて賦活処理することが好ましい。   That is, in the present invention, which activation treatment is used is not particularly limited, but it has been found that by setting the activation treatment temperature slightly lower than usual, the adsorptive power to oil increases. Therefore, in the present invention, the activation treatment is preferably performed at a relatively low temperature of about 350 to 850 ° C, more preferably about 400 to 850 ° C.

このように、吸着炭を比較的低温で処理を行うと吸着能力が上昇する理由は、吸着炭を比較的低温で処理を行うと、前述した原料(ココヤシの中果皮)のハニカム構造がそのまま残存するのに対し、高温処理を行うと、前述のハニカム構造が破壊される恐れが生じるためと解される。   As described above, when the adsorbed charcoal is processed at a relatively low temperature, the adsorption capacity increases. When the adsorbed charcoal is processed at a relatively low temperature, the honeycomb structure of the raw material (coconut peel) remains as it is. On the other hand, it is understood that the above-described honeycomb structure may be destroyed when the high temperature treatment is performed.

なお、本発明の吸着炭は、そのままの状態、即ち、粉末状態で使用してもよいが、その後の回収・再生作業を容易にするために、通常は、粒状、板状、円盤状などのペレット状、タブレット状又は錠剤形等の任意の形状に形成し、使用しても良いのである。   The adsorbed charcoal of the present invention may be used as it is, that is, in a powder state. However, in order to facilitate the subsequent recovery / regeneration work, it is usually in the form of particles, plates, disks, etc. It may be formed into an arbitrary shape such as a pellet, tablet or tablet and used.

ここで、本発明の吸着炭を任意の形状に加工するにあたり、例えば、バインダーを介して吸着炭を接着・固定する手段などを用いても良いが、特に、本発明においては、目的とする形状の型に吸着炭と粉状ないし粒状のホットメルト系樹脂とを充填し、その充填物の一方から他方に水蒸気を通過させることにより、前記ホットメルト系樹脂を水蒸気の熱で溶融、接着性を発現させて、当該吸着炭を所定形状に加工する手段を用いることが好ましい。   Here, in processing the adsorbed charcoal of the present invention into an arbitrary shape, for example, a means for adhering and fixing the adsorbed charcoal via a binder may be used. The mold is filled with adsorbed charcoal and powdered or granular hot-melt resin, and water vapor is passed from one of the fillers to the other, so that the hot-melt resin is melted by the heat of water vapor and adhesion is improved. It is preferable to use a means for expressing and processing the adsorbed charcoal into a predetermined shape.

この理由は、単に、バインダーを介して吸着炭を接着する手段などを用いると、バインダーの乾燥に比較的長期間を要する上、吸着炭の大部分がバインダーに埋もれてしまい、その吸着特性を損なう場合があるからであり、この点につき、目的とする形状の型に吸着炭とホットメルト系樹脂とを充填し、その充填物の一方から他方に水蒸気を通過させることにより、前記ホットメルト系樹脂を水蒸気の熱で溶融、接着性を発現させて、当該吸着炭を所定形状に形成、固定する上述の手段を用いると、短時間で吸着炭を所定形状に形成、固定できる上、水蒸気を通過させることにより吸着炭が樹脂に埋もれることを極力制限することができる結果、これより吸着炭の活性を維持することができるからである。   The reason for this is that if a means for adsorbing adsorbed charcoal via a binder is used, it takes a relatively long time to dry the binder, and most of the adsorbed charcoal is buried in the binder, impairing its adsorption characteristics. This is because there is a case where the hot melt resin is filled by adsorbing charcoal and hot melt resin into a mold having a desired shape and passing water vapor from one of the fillers to the other. By using the above-mentioned means for forming and fixing the adsorbed charcoal in a predetermined shape by causing the heat of the steam to melt and exhibit adhesiveness, the adsorbed charcoal can be formed and fixed in a predetermined shape in a short time and also passes through the water vapor. This is because it is possible to limit as much as possible that the adsorbed charcoal is buried in the resin, so that the activity of the adsorbed charcoal can be maintained.

なお、ホットメルト系樹脂としては、水蒸気の熱で処理されることにより接着性を発現するものであれば特に限定されるものではないが、具体的には例えば、ポリエチレンやポリプロピレン等のポリオレフィン系樹脂、エチレン−酢酸ビニル共重合体、ポリスチレン、ポリイソブチレン、ポリアミド樹脂又はポリエステル樹脂から選ばれた少なくとも1種以上を挙げることができるが、特に、ポリエチレンやエチレン−酢酸ビニル共重合体が比較的低温で溶融して接着性が発現するうえ、安価であるので望ましい。   The hot melt resin is not particularly limited as long as it exhibits adhesiveness by being treated with the heat of water vapor. Specifically, for example, a polyolefin resin such as polyethylene or polypropylene is used. , Ethylene-vinyl acetate copolymer, polystyrene, polyisobutylene, polyamide resin or polyester resin, at least one selected from the group consisting of polyethylene and ethylene-vinyl acetate copolymers at relatively low temperatures. It is desirable because it melts to exhibit adhesiveness and is inexpensive.

本発明の水質浄化剤においては、前記本発明の吸着炭を主成分とすることを特徴とするものであり、河川、湖沼、海などの自然水域や、工場廃水等の廃水、下水、雨水の溜池などに散布すると、長期間にわたって、水面上に浮遊する結果、水面上に浮遊している油分(油膜)と水質浄化剤とが長期間にわたって接触し続けるので、当該油分(油膜)を効率よく除去することができるのである。   The water purification agent of the present invention is characterized by comprising the adsorbed charcoal of the present invention as a main component, natural water areas such as rivers, lakes and seas, waste water such as factory waste water, sewage, rainwater When sprayed in a pond, etc., it floats on the water surface for a long period of time. As a result, the oil component (oil film) floating on the water surface and the water purification agent remain in contact with each other for a long period of time. It can be removed.

ここにおいて、「主成分とする」とは、吸着炭を水質浄化剤として使用する際に、水質浄化剤が吸着炭のみで形成されている場合の他、吸着炭の有する油分吸着作用が損なわれない程度の割合で他の機能性材料を配合しても良いという意味である。この他の機能性材料としては、一般に使用されている通常の活性炭やゼオライトなどの吸着剤や、吸油性能を向上させるための綿織物などの繊維製品、或いは発泡剤などを挙げることができるのであり、この場合、一般的には、水質浄化剤全体に対する吸着炭の配合割合が60重量%程度以上とするのが好ましい。そして、特に、吸着炭のみで水質浄化剤を製造するのが最も望ましい。   Here, “main component” means that when adsorbed charcoal is used as a water purification agent, the oil adsorbing action of adsorbed charcoal is impaired in addition to the case where the water purification agent is formed only of adsorbed charcoal. It means that other functional materials may be blended in a proportion not present. Examples of other functional materials include commonly used adsorbents such as ordinary activated carbon and zeolite, fiber products such as cotton fabric for improving oil absorption performance, and foaming agents. In this case, generally, it is preferable that the mixing ratio of the adsorbed charcoal with respect to the whole water purification agent is about 60% by weight or more. In particular, it is most desirable to produce a water purification agent using only adsorbed charcoal.

本発明の水質浄化袋は、前記本発明の吸着炭を袋材に封入したことを特徴とするものであり、吸着炭の運搬性や携帯性更に回収性などの取扱性を向上したものである。   The water purification bag of the present invention is characterized in that the adsorbed charcoal of the present invention is enclosed in a bag material, which improves the handling properties such as the transportability and portability of the adsorbed charcoal and the recoverability. .

前記袋材としては、通液性を有し、封入した吸着炭が簡単に漏れないものであれば特に限定されるものではなく、例えば、不織布や職布、織物、紙製の製品、高分子材料製のフィルムないしシートなどに穿孔処理などを施した、通液性のフィルムないしシートを袋状に形成したものなどを挙げることができる。   The bag material is not particularly limited as long as it has liquid permeability and does not easily leak the enclosed adsorbed charcoal. For example, non-woven fabric, work cloth, woven fabric, paper product, polymer Examples thereof include a film or sheet made of a material, which has been subjected to perforation treatment or the like, and a liquid-permeable film or sheet formed into a bag shape.

一方、本発明の水質浄化基材は、前記本発明の吸着炭を、担持体に担持したことを特徴とするものであり、これも吸着炭の運搬性や携帯性更に回収性などの取扱性を向上したものである。   On the other hand, the water purification substrate of the present invention is characterized in that the adsorbed charcoal of the present invention is supported on a carrier, and this also handles the adsorbed charcoal in terms of transportability, portability and recoverability. Is an improvement.

ここで、本発明の吸着炭を担持体に担持する方法としては、まず、吸着炭をバインダーと混合し、この混合物を任意に選択した担持体に塗布することにより、担持体表面に吸着炭を担持する手段を挙げることができる。   Here, as a method for supporting the adsorbed charcoal of the present invention on a carrier, first, adsorbed charcoal is mixed with a binder, and the adsorbed charcoal is adsorbed on the surface of the carrier by applying this mixture to an arbitrarily selected carrier. A means for carrying can be mentioned.

しかしながら、バインダーを介して吸着炭を担持体に接着する手段は、担持体の素材や形状、性質などを問わず、簡単に吸着炭を担持体に担持することができる点において利点があるが、この手段を用いると、バインダーの乾燥に比較的長期間を要する上、吸着炭の大部分がバインダーに埋もれてしまい、その吸着特性を損なう場合がある。   However, the means for adsorbing the adsorbed charcoal to the carrier via the binder is advantageous in that the adsorbed charcoal can be easily carried on the carrier regardless of the material, shape, properties, etc. of the carrier, When this means is used, it takes a relatively long time to dry the binder, and most of the adsorbed charcoal is buried in the binder, which may impair the adsorption characteristics.

そこで、本発明の水質浄化基材においては、吸着炭を担持体に担持させるにあたり、以下に例示する手段を講じることが好ましい。   Therefore, in the water purification substrate of the present invention, it is preferable to take the following means for supporting the adsorbed charcoal on the support.

まず、本発明の水質浄化基材において、吸着炭の吸着特性を極力損なわずに、吸着炭を担持体に担持させる好ましい方法の一つとしては、繊維製品を担持体として用い、該繊維製品の繊維網中に吸着炭を担持する手段を挙げることができる。   First, in the water purification substrate of the present invention, as one of preferable methods for supporting the adsorbed charcoal on the support without damaging the adsorption characteristics of the adsorbed charcoal as much as possible, using a fiber product as the support, A means for supporting adsorbed charcoal in the fiber network can be mentioned.

即ち、本発明の水質浄化基材においては、吸着炭を担持体に担持させるにあたり、バインダーなどの接着手段を用いずに、繊維製品や担持体として、該繊維製品の繊維網中に吸着炭を担持すれば、担持された吸着炭は、常に活性な状態を維持することができるのである。   That is, in the water purification substrate of the present invention, when adsorbing charcoal is supported on the carrier, the adsorbed charcoal is adsorbed in the fiber network of the fiber product as a fiber product or carrier without using an adhesive means such as a binder. If supported, the supported adsorbed charcoal can always maintain an active state.

なお、前記繊維製品としては、その繊維網中に吸着炭を担持し得るものであれば特に限定されるものではなく、例えば、天然繊維及び/又は人造繊維からなる布地、タオル地、毛布、切ると、編み物、不織布及び不織などの布基材や、パルプ繊維からなる紙、パルプモールドなどを挙げることができる。   The fiber product is not particularly limited as long as it can support the adsorbed charcoal in the fiber net. For example, when the fabric is made of natural fiber and / or artificial fiber, towel fabric, blanket, Examples thereof include cloth base materials such as knitted fabrics, non-woven fabrics and non-woven fabrics, paper made of pulp fibers, and pulp molds.

しかしながら、繊維製品の繊維網中に吸着炭を担持する手段にあっては、吸着炭の漏れや脱落が生じたり、担持する吸着炭の量が少なくなったりするといった問題が生じる場合がある。   However, in the means for supporting the adsorbed charcoal in the fiber net of the textile product, there may be a problem that the adsorbed charcoal leaks or falls off or the amount of adsorbed charcoal to be carried decreases.

この点につき、本発明の水質浄化基材において、吸着炭を担持体に担持させる他の好ましい方法の一つとしては、通液性を有するフィルム状ないしシート状の基材及び被覆材を担持体として選択し、前記基材上に吸着炭を積層し、更にその上から前記被覆材で覆うことにより当該基材と被覆材を部分的に接着して前記基材と前記被覆材との間に吸着炭を担持する手段を挙げることができる。   With respect to this point, in the water purification substrate of the present invention, as one of other preferable methods for supporting the adsorbed charcoal on the carrier, a film or sheet substrate having a liquid permeability and a covering material are supported on the carrier. The adsorbed charcoal is laminated on the base material, and the base material and the covering material are partially adhered by covering with the covering material from above, and the base material and the covering material are interposed between them. A means for supporting adsorbed charcoal can be mentioned.

又、吸着炭を担持体に担持させるにあたり、通液性を有するフィルム状ないしシート状の基材上に、吸着炭と粉状ないし粒状のホットメルト系樹脂とを積層し、更にその上から前記被覆材で覆うことにより積層体を形成し、次いでこの積層体の厚さ方向に水蒸気を通過させることにより、前記ホットメルト系樹脂を水蒸気の熱で溶融、接着性を発現させて、前記基材と前記被覆材との間に吸着炭を担持する手段を挙げることができるのであり、このように構成することにより、吸着炭の漏れや脱落を防止し、しかも挟み込む吸着炭の量を適宜調節することができるのである。   Further, when the adsorbed charcoal is supported on the carrier, the adsorbed charcoal and the powdery or granular hot-melt resin are laminated on the film-like or sheet-like substrate having liquid permeability, and further from above, the above-mentioned A laminate is formed by covering with a covering material, and then water vapor is passed in the thickness direction of the laminate, whereby the hot melt resin is melted by the heat of water vapor to exhibit adhesiveness, and the base material And a means for supporting the adsorbed charcoal between the coating material and the covering material, and by configuring in this way, the adsorbed charcoal is prevented from leaking or falling off, and the amount of adsorbed charcoal to be sandwiched is appropriately adjusted. It can be done.

又、この方法においては、特に、前記積層体の厚さ方向に水蒸気を通過させることにより、前記ホットメルト系樹脂を水蒸気の熱で溶融、接着性を発現させて、前記基材と前記被覆材との間に吸着炭を担持することにより、通気性や柔軟性を損なうことなく、短時間で吸着炭を固定することができる上、樹脂中への吸着炭の埋没が極力制限され、吸着炭の活性を維持することができるのである。   Further, in this method, in particular, by passing water vapor in the thickness direction of the laminate, the hot melt resin is melted by the heat of water vapor to develop adhesiveness, and the base material and the coating material are obtained. By adsorbing the adsorbed charcoal between the adsorbent charcoal, the adsorbed charcoal can be fixed in a short time without impairing the air permeability and flexibility, and the adsorption of the adsorbed charcoal in the resin is limited as much as possible. The activity of can be maintained.

なお、前記基材及び被覆材としては、例えば、天然繊維及び/又は人造繊維からなる布体を挙げることができ、前記天然繊維及び/又は人造繊維から成る布体としては、一般的には、布地、タオル地、毛布、キルト、編み物、紙、不織布又は織布等を挙げることができる。   In addition, as the base material and the covering material, for example, a cloth body made of natural fibers and / or artificial fibers can be mentioned, and as the cloth body made of natural fibers and / or artificial fibers, in general, Examples thereof include cloth, towel cloth, blanket, quilt, knitting, paper, non-woven cloth, and woven cloth.

その他に、本発明の水質浄化基材において、吸着炭を担持体に担持させる好ましい方法の一つとしては、発泡プラスチックを担持体として、当該発泡プラスチック内に吸着炭を担持する手段を挙げることができる。   In addition, in the water purification substrate of the present invention, one preferred method for supporting the adsorbed charcoal on the support is to use a foamed plastic as the support and a means for supporting the adsorbed charcoal in the foamed plastic. it can.

ここで、「発泡プラスチック」とは、ポリスチレン、ポリウレタン、ABS樹脂、ポリ塩化ビニル、ポリエチレン、ポリプロピレン、フェノール樹脂、尿素樹脂、エポキシ樹脂、ケイ素樹脂などをベースポリマーとしてこれに、種々の発泡手段[例えば、(1)揮発性液体又は分解性発泡剤の添加、(2)空気や、窒素などの吹き込み、(3)スプレーによる造泡、(4)反応生成ガスの利用など]を講じて1.1〜10倍程度の低発泡品から、100倍を越える高発泡品として成形したもののことをいい、結果的に、当該発泡プラスチックには無数の細孔のネットワークが形成されている。   Here, “foamed plastic” refers to polystyrene, polyurethane, ABS resin, polyvinyl chloride, polyethylene, polypropylene, phenol resin, urea resin, epoxy resin, silicon resin, etc. as a base polymer, and various foaming means [for example, (1) Addition of volatile liquid or decomposable foaming agent, (2) Blowing in air or nitrogen, (3) Foaming by spraying, (4) Utilization of reaction product gas, etc.] It refers to a product formed as a highly foamed product exceeding 100 times from a low foamed product of about 10 times, and as a result, an infinite number of pore networks are formed in the foamed plastic.

即ち、吸着炭を担持体に担持させるにあたり、発泡プラスチックを担持体として、該発泡プラスチック内に吸着炭を担持することにより、前記無数の細孔のネットワーク中に吸着炭が保持されることから、樹脂中への吸着炭の埋没が極力制限され、吸着炭の活性を維持することができるのである。   That is, when the adsorbed charcoal is supported on the carrier, the adsorbed charcoal is retained in the network of innumerable pores by supporting the adsorbed charcoal in the foamed plastic with the foamed plastic as a carrier. The burying of the adsorbed charcoal in the resin is limited as much as possible and the activity of the adsorbed charcoal can be maintained.

ここで、発泡プラスチック内に吸着炭を担持する手段としては、特に限定されるものではないが、具体的に例えば、前述のベースポリマーからなるプラスチックビーズにペンタンやフレオンなどを浸透させた発泡性ビーズと吸着炭とを混合し、この混合物を所定の型に充填した後に加熱し、発泡させるなどの手段を挙げることができる。   Here, the means for supporting the adsorbed charcoal in the foamed plastic is not particularly limited, but specifically, for example, a foamable bead in which pentane or freon is infiltrated into the plastic bead made of the aforementioned base polymer. And adsorbed charcoal, and after filling the mixture into a predetermined mold, heating and foaming can be used.

なお、前述のように、本発明の水質浄化基材においては、吸着炭の運搬性や携帯性更に回収性などの取扱性が向上する利点があるが、担持体に吸着炭を担持させることにより、使用の際に、水面上への吸着炭の広範な拡散が妨げられる場合がある。   As described above, in the water purification substrate of the present invention, there is an advantage that the handling property such as the transportability and portability of the adsorbed charcoal and the recoverability are improved, but by supporting the adsorbed charcoal on the carrier. In use, widespread diffusion of adsorbed charcoal on the water surface may be hindered.

そこで、本発明の水質浄化基材に対して、水面上への吸着炭の広範な拡散が要される場合にあっては、本発明の水質浄化基材における担持体につき、例えば、ティッシュペーパーやトイレットペーパーのような、水に触れた際に、簡単に溶けたり破けたりする水溶性ないし水分解性の素材を用い、担持した吸着炭を速やかに離散させることが好ましい。   Therefore, in the case where a wide diffusion of adsorbed charcoal on the water surface is required for the water purification substrate of the present invention, the carrier in the water purification substrate of the present invention may be, for example, tissue paper or It is preferable to disperse the adsorbed charcoal quickly using a water-soluble or water-decomposable material that easily melts or tears when touching water, such as toilet paper.

本発明の油膜の除去方法は、前記本発明の水質浄化剤、水質浄化袋、水質浄化基材を用いて、水面上に浮遊する油膜を除去することを特徴とするものであり、本発明の水質浄化剤を、河川、湖沼、海などの自然水域や、工場廃水等の廃水、下水、雨水の溜池などに散布することにより、その水面上に浮遊した状態で存在する油分(油膜)を効率よく除去することができるのである。   The oil film removal method of the present invention is characterized in that the oil film floating on the water surface is removed using the water purification agent, water purification bag, and water purification substrate of the present invention. Efficiency of oil (oil film) that floats on the surface of water by spraying water purification agents on natural waters such as rivers, lakes, and seas, wastewater such as factory wastewater, sewage, and rainwater reservoirs It can be removed well.

本発明は、前記構成を有し、河川、湖沼、海などの自然水域や、工場廃水等の廃水、下水、雨水の溜池などに含まれ、その水面上に浮遊した状態で存在する油分(油膜)を効率よく除去するための吸着炭である。   The present invention has the above-described configuration, and is contained in natural water areas such as rivers, lakes, and seas, waste water such as factory waste water, sewage, and rainwater reservoirs, and the like (oil film) that exists in a floating state on the water surface. ) Is an adsorptive charcoal for efficient removal.

即ち、本発明の吸着炭は、独立孔同士や独立孔と連続孔が一体形となった複雑な網目構造を形成して無数に存在する細孔同士が隣接したハニカム構造をしているココヤシの中果皮を原料とし、このココヤシの中果皮に加熱、炭化処理を施して得たものであり、この吸着炭は、従来の活性炭よりも比重が小さい炭化物質であり、このため、本発明の水質浄化剤を水面上に散布すれば、多少の水分を吸収しても水面上に浮遊し続け、長期間にわたって当該水面上の油分(油膜)と接触させることができるので、当該油分(油膜)を効率よく除去することができるなどの効果を奏するのである。   That is, the adsorbed charcoal of the present invention forms a complex network structure in which independent holes or independent holes and continuous holes are integrated, and has a honeycomb structure in which countless number of pores are adjacent to each other. It is obtained by heating and carbonizing this coconut mesocarp, using mesocarp as a raw material, and this adsorbed charcoal is a carbonized material having a specific gravity smaller than that of conventional activated carbon. Therefore, the water quality of the present invention If the purifier is sprayed on the water surface, it will continue to float on the water surface even if it absorbs some moisture, and can be kept in contact with the oil (oil film) on the water surface for a long period of time. The effect of being able to remove efficiently is produced.

又、上述のように、ココヤシの中果皮を原料として得られた吸着炭は、独立孔同士や独立孔と連続孔が一体形となった複雑なハニカム構造をしているので、各細孔のサイズが非常に広範な構造となっており、このため、あらゆる種類の油分に対する吸着性に優れるなどの効果を奏するのである。   In addition, as described above, the adsorbed charcoal obtained using coconut mesocarp as a raw material has a complicated honeycomb structure in which independent pores or independent pores and continuous pores are integrated. The structure has a very wide range of sizes, and as a result, there are effects such as excellent adsorptivity to all kinds of oils.

しかも、ココヤシの中果皮は、繊維成分以外利用価値が殆んどなく、殆んど利用されることなく廃棄されているのが現状であり、至極低コストで安定した原料の調達が可能であり、又、廃棄物利用の観点からも大きな利点があるのである。   Moreover, coconut mesocarp has almost no utility value other than fiber components, and it is currently being discarded without being used almost at all, making it possible to procure stable raw materials at extremely low cost. There is also a great advantage from the viewpoint of waste utilization.

そして、本発明の水質浄化剤は、本発明の吸着炭を主成分とすることを特徴とするものであり、河川、湖沼、海などの自然水域や、工場廃水等の廃水、下水、雨水の溜池などに散布することにより、その水面上に長期間にわたって浮遊する結果、浮遊した状態で存在する油分(油膜)と長期間にわたって接触するので、当該油分(油膜)を効率よく除去することができるなどの効果を奏するのである。   The water purification agent of the present invention is characterized by comprising the adsorbed charcoal of the present invention as a main component, natural water areas such as rivers, lakes, and seas, waste water such as factory waste water, sewage, and rainwater. By spraying in a reservoir, etc., as a result of floating on the surface of water for a long time, the oil (oil film) existing in a floating state is contacted for a long time, so that the oil (oil film) can be efficiently removed. There are effects such as.

又、本発明の水質浄化袋においては、本発明の吸着炭を袋材に封入させたことを特徴とするものであり、吸着炭の運搬性や携帯性更に回収性などの取扱性が著しく向上するなどの効果を奏するのである。   Further, the water purification bag of the present invention is characterized in that the adsorbed charcoal of the present invention is sealed in a bag material, and the handleability of the adsorbed charcoal, such as transportability, portability and recoverability, is remarkably improved. It has the effect of doing.

更に、本発明の水質浄化基材においては、本発明の吸着炭を担持体に担持させたことを特徴とするものであり、吸着炭の運搬性や携帯性更に回収性などの取扱性が著しく向上するなどの効果を奏するのである。   Furthermore, the water purification substrate of the present invention is characterized in that the adsorbed charcoal of the present invention is supported on a carrier, and the handling properties such as the transportability and portability of the adsorbed charcoal and the recoverability are remarkably high. There are effects such as improvement.

本発明の油膜の除去方法においては、本発明の水質浄化剤、水質浄化袋又は水質浄化基材を用いて、水面上に浮遊する油分(油膜)を除去することを特徴とするものであり、本発明の水質浄化剤、水質浄化袋又は水質浄化基材を、海、湖沼、河川などの自然水域や、工場廃水等の廃水、下水、雨水の溜池などに散布することにより、その水面上に長期間にわたって浮遊する結果、浮遊した状態で存在する油分(油膜)と長期間にわたって接触するので、当該油分(油膜)を効率よく除去することができるなどの効果を奏するのである。   The method for removing an oil film of the present invention is characterized by removing oil (oil film) floating on the water surface using the water purification agent, water purification bag or water purification substrate of the present invention, By spraying the water purification agent, water purification bag or water purification substrate of the present invention on natural water areas such as the sea, lakes and rivers, waste water such as factory waste water, sewage, rainwater reservoirs, etc., on the surface of the water As a result of floating for a long period of time, the oil (oil film) existing in a floating state is brought into contact for a long period of time, so that the oil (oil film) can be efficiently removed.

発明を実施する最良の形態Best Mode for Carrying Out the Invention

以下、本発明を実施するための最良の形態を具体的に説明するが、本発明は以下の実施例によって限定されるものではない。   BEST MODE FOR CARRYING OUT THE INVENTION The best mode for carrying out the present invention will be specifically described below, but the present invention is not limited to the following examples.

ココヤシの中果皮を水流で洗い、繊維成分をある程度除去したものを乾燥し、これを温度約550℃で加熱し、赤熱した状態で水蒸気、炭酸ガス(燃焼ガス中のCO2)及び酸素(燃焼空気中のO2)の混合雰囲気中、温度約600℃で加熱、炭化処理を施すことにより、本発明の吸着炭粉末を得た。   Wash the coconut skin with water, dry the fiber component to a certain extent, heat it at a temperature of about 550 ° C, and in a reddish state, steam, carbon dioxide (CO2 in the combustion gas) and oxygen (combustion air) The adsorbed carbon powder of the present invention was obtained by heating and carbonizing at a temperature of about 600 ° C. in a mixed atmosphere of O2).

比較例1Comparative Example 1

椰子殻(ココヤシの内果皮)を乾燥して微粉を除いた活性炭原料を温度約800℃で加熱し、赤熱した状態で水蒸気、炭酸ガス(燃焼ガス中のCO2)及び酸素(燃焼空気中のO2)の混合雰囲気中、温度約900℃で賦活処理することにより、活性炭粉末を得た。   The activated carbon raw material from which the coconut shell (coconut skin) is dried and fine powder is removed is heated at a temperature of about 800 ° C, and in a red-hot state, water vapor, carbon dioxide (CO2 in the combustion gas) and oxygen (O2 in the combustion air) ) Was activated at a temperature of about 900 ° C. to obtain activated carbon powder.

<比較試験>
縦20cm、横15cm、高さ15cmの角形ステンレス製パレットを3個用意し、この3個の角形ステンレス製パレットにそれぞれ水道水3000mlを入れ、この各角形ステンレス製パレットの水面上にビュレットで1.5mlの軽油を滴下して当該軽油を水面上に拡散させた後、実施例1で得た吸着炭粉末15gをそれぞれ水面上に散布、拡散させて、一昼夜静置した。
<Comparison test>
Three rectangular stainless steel pallets of 20 cm in length, 15 cm in width, and 15 cm in height are prepared, and 3000 ml of tap water is placed in each of these three rectangular stainless steel pallets, and a burette is placed on the water surface of each of these rectangular stainless steel pallets. After dripping 5 ml of light oil and diffusing the light oil on the water surface, 15 g of the adsorbed charcoal powder obtained in Example 1 was sprayed and diffused on the water surface, respectively, and allowed to stand overnight.

又、同様に、縦20cm、横15cm、高さ15cmの角形ステンレス製パレットを3個用意し、この3個の角形ステンレス製パレットにそれぞれ水道水3000mlを入れ、この各角形ステンレス製パレットの水面上にビュレットで1.5mlの軽油を滴下して当該軽油を水面上に拡散させた後、比較例1で得た活性炭粉末15gをそれぞれ水面上に散布、拡散させて、一昼夜静置した。   Similarly, prepare 3 square stainless steel pallets 20cm long, 15cm wide and 15cm high, put 3000ml of tap water in each of these 3 square stainless steel pallets, and put on the water surface of each square stainless steel pallet. After 1.5 ml of light oil was dropped onto the water surface using a burette, 15 g of the activated carbon powder obtained in Comparative Example 1 was sprayed and diffused on the water surface, and allowed to stand overnight.

更に、参考例として、実施例1及び比較例1で用いたものと同様の角形ステンレス製パレットを1個用意し、これに、実施例1及び比較例1と同様に、水道水3000mlを入れ、この各角形ステンレス製パレットの水面上にビュレットで1.5mlの軽油を滴下して当該軽油を水面上に拡散させた後、そのままの状態で一昼夜静置した。
即ち、この参考例においては、油の吸着剤を何も散布しなかった。
Furthermore, as a reference example, one rectangular stainless steel pallet similar to that used in Example 1 and Comparative Example 1 was prepared, and into this, as in Example 1 and Comparative Example 1, 3000 ml of tap water was added. After 1.5 ml of light oil was dropped on the water surface of each square stainless steel pallet with a burette to diffuse the light oil on the water surface, the pallet was allowed to stand for 24 hours.
That is, in this reference example, no oil adsorbent was sprayed.

一昼夜経過後、各角形ステンレス製パレットの状態を確認したところ、実施例1に係る吸着炭粉末を散布したものは、その3個すべてにおいて、依然、吸着炭粉末が水面上に浮遊していたが、比較例1に係る活性炭粉末を散布したものは、その3個すべてにおいて、殆んど全ての活性炭が水面下に沈んでおり、しかも水面上に軽油膜が残存していることが確認された。   After a day and night, the state of each square stainless steel pallet was confirmed. As a result, the adsorbed charcoal powder dispersed in Example 3 was still floating on the water surface. It was confirmed that almost all of the activated carbon was submerged below the surface of the water in which the activated carbon powder according to Comparative Example 1 was dispersed, and that the light oil film remained on the surface of the water. .

又、実施例1及び比較例1のものについて、各角形ステンレス製パレットからそれぞれ吸着炭及び活性炭を取り出し、当該各角形ステンレス製パレット内の軽油膜の状態を目視で確認した。   Moreover, about the thing of Example 1 and the comparative example 1, adsorption charcoal and activated carbon were each taken out from each square stainless steel pallet, and the state of the light oil film in each said square stainless steel pallet was confirmed visually.

その結果、実施例1に係る吸着炭粉末を散布したものについては、軽油膜が消滅し、油(軽油)分を確認することができないことが認められた。   As a result, it was recognized that the oil oil film disappeared and the oil (light oil) content could not be confirmed for the sprayed adsorbed charcoal powder according to Example 1.

一方、比較例に係る活性炭を散布したものについては、前述のように、水面上に軽油膜が残存していることが確認された。   On the other hand, about what sprinkled the activated carbon which concerns on a comparative example, as mentioned above, it was confirmed that the light oil film remains on the water surface.

更に、参考例のものについては、軽油膜がそのままの状態で生存しており、全く変化が認められなかった。   Furthermore, in the case of the reference example, the light oil film survived as it was, and no change was observed.

<円柱状の吸着炭の作成>
図1〜図4は、本発明の吸着炭(粉末)1を、円柱状の吸着炭へ加工する工程を示す模式図である。
<Creation of columnar adsorbed charcoal>
FIGS. 1-4 is a schematic diagram which shows the process of processing the adsorption charcoal (powder) 1 of this invention into a columnar adsorption charcoal.

図1及び図2に示すように、本実施例においては、まず、特定形状の型5に、吸着炭1と粉状ないし粒状のホットメルト系樹脂(エチレン−酢酸ビニル共重合体)2とを充填して、充填物Mを形成する。   As shown in FIGS. 1 and 2, in this embodiment, first, adsorbed charcoal 1 and powdery or granular hot-melt resin (ethylene-vinyl acetate copolymer) 2 are placed in a specific-shaped mold 5. Fill to form fill M.

ここで、特定形状の型5に、吸着炭1と粉状ないし粒状のエチレン−酢酸ビニル共重合体2とを充填するにあたり、吸着炭1とエチレン−酢酸ビニル共重合体2とを個別に積層・充填してもよいが、本実施例では、吸着炭1とエチレン−酢酸ビニル共重合体2との混合物(容積比で吸着炭8:エチレン−酢酸ビニル共重合体2)を充填している。   Here, when the adsorbed charcoal 1 and the powdery or granular ethylene-vinyl acetate copolymer 2 are filled in the mold 5 having a specific shape, the adsorbed charcoal 1 and the ethylene-vinyl acetate copolymer 2 are individually laminated. In this embodiment, the mixture is filled with adsorbed charcoal 1 and ethylene-vinyl acetate copolymer 2 (adsorbed charcoal 8: ethylene-vinyl acetate copolymer 2 by volume). .

なお、本実施例における特定形状の型5としては、本実施例では円筒状のものを用いているが、その形状は特に限定されるものではなく、任意の形状の型が挙げられる。   In addition, as the mold 5 having a specific shape in the present embodiment, a cylindrical shape is used in the present embodiment, but the shape is not particularly limited, and a mold having an arbitrary shape can be mentioned.

又、この特定形状の型5を構成する素材としては、水蒸気Sで処理する際に簡単に溶けたり、壊れたりするものでなければ特に限定されるものではなく、一般的には、木や竹等の天然素材、ステンレス等の金属材料、耐熱性高分子材料又は陶器やセラミック材料等を好適に用いることができる。   The material constituting the mold 5 of the specific shape is not particularly limited as long as it is not easily melted or broken when treated with the water vapor S. Generally, wood or bamboo is used. A natural material such as stainless steel, a metal material such as stainless steel, a heat-resistant polymer material, or a pottery or ceramic material can be suitably used.

なお、更に詳しくは、図4に示すように、本実施例においては、円筒状のステンレス製型(直径2cm、高さ3cm)5には、その上面全面に水蒸気Sを送り込むための水蒸気流入部6と円筒状の型の底面全面に水蒸気Sが流出するための水蒸気流出部7が設けられており、この水蒸気流出部7から水蒸気Sを吸引できるように構成されている。   In more detail, as shown in FIG. 4, in this embodiment, the cylindrical stainless steel mold (diameter 2 cm, height 3 cm) 5 has a water vapor inflow portion for feeding water vapor S to the entire upper surface. 6 and the bottom surface of the cylindrical mold are provided with a water vapor outflow portion 7 through which the water vapor S flows out, and the water vapor S can be sucked from the water vapor outflow portion 7.

又、本実施例においては、吸着炭1と粉状ないし粒状のエチレン−酢酸ビニル共重合体2とを充填する前に、これらの成分がこぼれ出ないように円筒状のステンレス製型5の底面全体が布体8で覆われている。   In this embodiment, before filling the adsorbed charcoal 1 and the powdery or granular ethylene-vinyl acetate copolymer 2, the bottom surface of the cylindrical stainless steel mold 5 is used to prevent these components from spilling out. The whole is covered with the cloth body 8.

そして、本実施例においては、図3及び図4に示すように、前記ステンレス製型5に充填した充填物Mに水蒸気流入部6から水蒸気流出部7に向かって水蒸気Sを通過させることにより、当該水蒸気Sの熱で前記エチレン−酢酸ビニル共重合体2を溶融、接着性を発現させて、前記吸着炭12を円柱状に形成し得るのである。   In this embodiment, as shown in FIGS. 3 and 4, by passing the steam S through the filler M filled in the stainless steel mold 5 from the steam inlet 6 to the steam outlet 7, The ethylene-vinyl acetate copolymer 2 is melted by the heat of the water vapor S to develop adhesiveness, so that the adsorbed charcoal 12 can be formed in a cylindrical shape.

この場合、処理室内に、水蒸気発生装置(図示せず)から発生させた水蒸気Sを流入するパイプ状の水蒸気流入部6とこの流入した水蒸気Sを流出するパイプ状の水蒸気流出部7が、それぞれ処理室の側面に設けられ、この水蒸気流出部7から水蒸気Sを吸引できるように構成されている。   In this case, a pipe-shaped water vapor inflow portion 6 into which the water vapor S generated from a water vapor generator (not shown) flows into the processing chamber and a pipe-shaped water vapor outflow portion 7 through which the water vapor S flows out are respectively provided. It is provided on the side surface of the processing chamber and is configured such that the water vapor S can be sucked from the water vapor outflow portion 7.

得られた円柱体を用い、前記実施例1と同様の試験を行ったところ、この円柱体は多孔質で水面に浮かび水面上の軽油膜を効率良く吸着することが認められたのであり、又、使用後、この円柱体の回収性が著しく優れることが認められた。   When the same test as in Example 1 was performed using the obtained cylindrical body, it was found that this cylindrical body was porous and floated on the water surface and efficiently adsorbed the light oil film on the water surface. After use, it was confirmed that the recoverability of this cylindrical body was remarkably excellent.

<水質浄化基材の作成>
図5及び図6は、本発明の吸着炭(粉末)1を、シート状の水質浄化基材へ加工する工程を示す模式図である。
<Creation of water purification substrate>
FIG.5 and FIG.6 is a schematic diagram which shows the process of processing the adsorbed charcoal (powder) 1 of this invention into a sheet-like water purification substrate.

図5に示すように、本実施例においては、まず、布製の基材3上に、吸着炭1と粉状ないし粒状のエチレン−酢酸ビニル共重合体2とを散布、積層し、更に、その上から布製の被覆材4で覆うことにより積層体を形成する。   As shown in FIG. 5, in this example, first, the adsorbed charcoal 1 and the powdery or granular ethylene-vinyl acetate copolymer 2 are sprayed and laminated on the cloth base material 3. A laminated body is formed by covering with a cloth covering material 4 from above.

ここで、基材3上に、吸着炭1とエチレン−酢酸ビニル共重合体2との混合物を散布、積層するにあたり、吸着炭1とエチレン−酢酸ビニル共重合体2とを個別に散布、積層してもよく、又、吸着炭1とエチレン−酢酸ビニル共重合体2との混合物を散布、積層してもよいが、この実施例では吸着炭1とエチレン−酢酸ビニル共重合体2との混合物(容積比で吸着炭8:エチレン−酢酸ビニル共重合体2)を散布、積層している。   Here, on the base material 3, the adsorbed charcoal 1 and the ethylene-vinyl acetate copolymer 2 are separately sprayed and laminated in order to spread and laminate the mixture of the adsorbed charcoal 1 and the ethylene-vinyl acetate copolymer 2. Alternatively, a mixture of adsorbed charcoal 1 and ethylene-vinyl acetate copolymer 2 may be sprayed and laminated. In this embodiment, adsorbed charcoal 1 and ethylene-vinyl acetate copolymer 2 The mixture (adsorbed charcoal 8: ethylene-vinyl acetate copolymer 2 by volume ratio) is sprayed and laminated.

そして、本実施例においては、図6のように、前記積層体の厚さ方向、例えば、被覆材4から基材3方向に向かって水蒸気Sを通過させることにより、当該水蒸気Sの熱で前記エチレン−酢酸ビニル共重合体3を溶融、接着性を発現させて、前記基材3と前記被覆材4との間に前記吸着炭1を固定して積層体(縦90cm、横35cm)を得た。
得られた積層体を縦15cm、横15cmに裁断して積層体片を得た。
And in a present Example, as shown in FIG. 6, by making the water vapor | steam S pass through the thickness direction of the said laminated body, for example, toward the base material 3 direction from the coating | covering material 4, it is the said heat | fever with the heat | fever of the said water vapor | steam S. The ethylene-vinyl acetate copolymer 3 is melted to exhibit adhesiveness, and the adsorbed charcoal 1 is fixed between the base material 3 and the covering material 4 to obtain a laminate (vertical 90 cm, horizontal 35 cm). It was.
The obtained laminate was cut into a length of 15 cm and a width of 15 cm to obtain a laminate piece.

得られた積層体片を用い、前記実施例1と同様の試験を行ったところ、この積層体片は多孔質で水面に浮かび水面上の軽油膜を効率良く吸着することが認められたのであり、又、使用後、この積層体片の回収性が著しく優れることが認められた。   When the same test as in Example 1 was performed using the obtained laminate piece, it was found that this laminate piece was porous and floated on the water surface and efficiently adsorbed the light oil film on the water surface. Also, after use, it was recognized that the recoverability of this laminate piece was remarkably excellent.

<水質浄化基材の作成>
図7〜8図は、本発明の吸着炭(粉末)1を発泡プラスチックの担持体に担持した水質浄化基材に加工する工程を示す模式図である。
<Creation of water purification substrate>
FIGS. 7 to 8 are schematic views showing a process of processing the adsorbed charcoal (powder) 1 of the present invention into a water purification substrate supported on a foamed plastic carrier.

図7に示すように、本実施例においては、まず、特定形状の型5に、ポリスチレンビーズにペンタンを5%程度浸透させた発泡性ビーズ9と本発明の吸着炭1とを充填して、充填物を形成する。   As shown in FIG. 7, in this example, first, the mold 5 having a specific shape is filled with expandable beads 9 in which about 5% of pentane is infiltrated into polystyrene beads and the adsorbed charcoal 1 of the present invention. A filling is formed.

なお、本実施例における特定形状の型5としては、直方体状のものを用いているが、その形状は特に限定されるものではなく、任意の形状の型を用いることができる。   In addition, although the rectangular parallelepiped type | mold is used as the type | mold 5 of the specific shape in a present Example, the shape is not specifically limited, The type | mold of arbitrary shapes can be used.

又、この特定形状の型5を構成する素材としては、後述する加熱処理(発泡処理)の際に簡単に溶けたり、壊れたりするものでなければ特に限定されるものではなく、本実施例においては、アルミニウム製のものを用い、縦2.5cm、横5cm、高さ2.5cmの直方体状のものであって、その周囲に多数の小孔51を設けたものである。   Further, the material constituting the mold 5 of the specific shape is not particularly limited as long as it does not easily melt or break during the heat treatment (foaming treatment) described later. Is made of aluminum and has a rectangular parallelepiped shape having a length of 2.5 cm, a width of 5 cm, and a height of 2.5 cm, and is provided with a large number of small holes 51 around it.

次いで、発泡性ビーズ9と本発明の吸着炭1の混合物を充填した充填物に対して、予備発泡を行った後、110〜120℃程度の処理温度で加熱することにより、図8に示す本発明の水質浄化基材を得た。   Next, after pre-foaming the filler filled with the mixture of the expandable beads 9 and the adsorbed charcoal 1 of the present invention, the mixture shown in FIG. 8 is heated at a processing temperature of about 110 to 120 ° C. The water purification substrate of the invention was obtained.

得られた水質浄化基材を用い、前記実施例1と同様の試験を行ったところ、この水質浄化基材は多孔質で水面に浮かび水面上の軽油膜を効率良く吸着することが認められたのであり、又、使用後、この水質浄化基材の回収性が著しく優れることが認められた。   When the same test as in Example 1 was carried out using the obtained water purification substrate, it was found that this water purification substrate was porous and floated on the water surface, and efficiently adsorbed the light oil film on the water surface. Moreover, after use, it was recognized that the recoverability of this water purification substrate is remarkably excellent.

図1は、実施例2の水質浄化剤の製造工程において、吸着炭とエチレン−酢酸ビニル共重合体との混合物を特定形状の型に投入する工程を示す模式図である。FIG. 1 is a schematic view showing a step of introducing a mixture of adsorbed charcoal and ethylene-vinyl acetate copolymer into a mold having a specific shape in the production process of the water purification agent of Example 2. 図2は、実施例2の水質浄化剤の製造工程において、吸着炭とエチレン−酢酸ビニル共重合体との混合物を特定形状の型に充填した状態を示す模式図である。FIG. 2 is a schematic diagram showing a state in which a mixture of adsorbed charcoal and ethylene-vinyl acetate copolymer is filled in a mold having a specific shape in the production process of the water purification agent of Example 2. 図3は、実施例2の水質浄化剤の製造工程において、型の充填物に水蒸気を通過させる状態を示す模式図である。FIG. 3 is a schematic view showing a state in which water vapor passes through the mold filling in the production process of the water purification agent of Example 2. 図4は、実施例2の水質浄化剤の製造工程において好適に用いられる水蒸気通過装置を示す模式図である。FIG. 4 is a schematic view showing a water vapor passage device suitably used in the production process of the water purification agent of Example 2. 図5は、実施例3の水質浄化基材の製造工程において、吸着炭とエチレン−酢酸ビニル共重合体との混合物を基材と被覆材との間に積層する工程を示す模式図である。FIG. 5 is a schematic view showing a step of laminating a mixture of adsorbed charcoal and ethylene-vinyl acetate copolymer between the base material and the covering material in the manufacturing process of the water purification base material of Example 3. 図6は、実施例3の水質浄化基材の製造工程において、積層体に水蒸気を通過させる状態を示す模式図である。FIG. 6 is a schematic diagram illustrating a state in which water vapor is passed through the laminate in the manufacturing process of the water purification substrate of Example 3. 図7は、実施例4の水質浄化基材の製造工程において、吸着炭と発泡ビーズとの混合物を特定形状の型に投入する工程を示す模式図である。FIG. 7 is a schematic diagram showing a step of feeding a mixture of adsorbed charcoal and foamed beads into a mold having a specific shape in the water purification substrate manufacturing process of Example 4. 図8は、実施例4の水質浄化基材を示す斜視図である。FIG. 8 is a perspective view showing a water purification substrate of Example 4.

符号の説明Explanation of symbols

1 吸着炭
2 ホットメルト系樹脂(エチレン−酢酸ビニル共重合体)
3 基材
4 被覆材
5 特定形状の型
6 水蒸気流入部
7 水蒸気流出部
8 布体
9 発泡性ビーズ
1 Adsorbed charcoal 2 Hot melt resin (ethylene-vinyl acetate copolymer)
DESCRIPTION OF SYMBOLS 3 Base material 4 Coating | covering material 5 Mold of specific shape 6 Water vapor | steam inflow part 7 Water vapor | steam outflow part 8 Cloth body 9 Expandable bead

Claims (17)

ココヤシの中果皮を原料として用い、この原料に加熱、炭化処理を施して形成したことを特徴とする吸着炭。   Adsorbed charcoal, which is formed by using coconut mesocarp as a raw material and heating and carbonizing the raw material. ココヤシの中果皮から、更に繊維成分を除いたものを原料として用いた請求項1に記載の吸着炭。   The adsorbed charcoal according to claim 1, wherein a raw material obtained by removing a fiber component from coconut mesocarp is used. 加熱、炭化処理における処理温度が350〜850℃の範囲である請求項1又は2に記載の吸着炭。   The adsorption charcoal according to claim 1 or 2 whose processing temperature in heating and carbonization processing is the range of 350-850 ° C. 加熱、炭化処理と共に、賦活処理を施してなる請求項1ないし3のいずれか1項に記載の吸着炭。   The adsorbed charcoal according to any one of claims 1 to 3, wherein an activation treatment is performed together with the heating and carbonization treatment. 加熱、炭化処理後、賦活処理を施してなる請求項1ないし3のいずれか1項に記載の吸着炭。   The adsorbed charcoal according to any one of claims 1 to 3, wherein an activation treatment is performed after the heating and carbonization treatment. 賦活処理における処理温度が350〜850℃の範囲である請求項4又は5に記載の吸着炭。   The adsorption charcoal according to claim 4 or 5 whose processing temperature in activation processing is the range of 350-850 ° C. 請求項1ないし6のいずれか1項に記載の吸着炭が、粒状、ペレット状、タブレット状又は錠剤形などの任意の形状に成形されている吸着炭。   The adsorbed charcoal in which the adsorbed charcoal according to any one of claims 1 to 6 is formed into an arbitrary shape such as a granular shape, a pellet shape, a tablet shape, or a tablet shape. 吸着炭を任意の形状に加工するにあたり、目的とする形状の型に吸着炭と粉状ないし粒状のホットメルト系樹脂とを充填し、その充填物の一方から他方に水蒸気を通過させることにより、前記ホットメルト系樹脂を水蒸気の熱で溶融、接着性を発現させて、当該吸着炭を所定形状に加工する請求項7に記載の吸着炭。   In processing the adsorbed charcoal into an arbitrary shape, by filling the mold of the target shape with adsorbed charcoal and powdered or granular hot melt resin, by passing water vapor from one of the packing to the other, The adsorptive charcoal according to claim 7, wherein the hot-melt resin is melted by heat of water vapor to develop adhesiveness, and the adsorbed charcoal is processed into a predetermined shape. 請求項1ないし8のいずれか1項に記載の吸着炭を主成分とすることを特徴とする水質浄化剤。   A water purification agent comprising the adsorbed charcoal according to any one of claims 1 to 8 as a main component. 請求項1ないし8のいずれか1項に記載の吸着炭を、袋材に封入してなることを特徴とする水質浄化袋。   A water purification bag comprising the adsorbed charcoal according to any one of claims 1 to 8 enclosed in a bag material. 請求項1ないし8のいずれか1項に記載の吸着炭を、担持体に担持してなることを特徴とする水質浄化基材。   A water quality purification substrate comprising the adsorbed charcoal according to any one of claims 1 to 8 supported on a carrier. 吸着炭をバインダーと混合し、この混合物を担持体に塗布することにより、担持体表面に吸着炭を担持してなる請求項11に記載の水質浄化基材。   The water purification substrate according to claim 11, wherein the adsorbed charcoal is mixed with a binder and the adsorbed charcoal is supported on the surface of the support by applying the mixture to the support. 担時体が繊維製品であり、該繊維製品の繊維網中に吸着炭を担持してなる請求項11に記載の水質浄化基材。   The water purification substrate according to claim 11, wherein the carrier is a fiber product, and adsorbed charcoal is supported in a fiber net of the fiber product. 担持体が、通液性を有するフィルム状ないしシート状の基材及び被覆材からなり、前記基材上に吸着炭と粉状ないし粒状のホットメルト系樹脂とを積層し、更にその上から前記被覆材で覆うことにより積層体を形成し、次いでこの積層体の厚さ方向に水蒸気を通過させることにより、前記ホットメルト系樹脂を水蒸気の熱で溶融、接着性を発現させて、前記基材と前記被覆材との間に吸着炭を担持してなる請求項11に記載の水質浄化基材。   The carrier is composed of a film-like or sheet-like base material having a liquid permeability and a coating material, and adsorbed charcoal and a powdery or granular hot-melt resin are laminated on the base material, and further from above, the above-mentioned A laminate is formed by covering with a covering material, and then water vapor is passed in the thickness direction of the laminate, whereby the hot melt resin is melted by the heat of water vapor to exhibit adhesiveness, and the base material The water purification substrate according to claim 11, wherein adsorbed charcoal is supported between the water and the covering material. 担持体が発泡プラスチックであり、該発泡プラスチック内に吸着炭を担持してなる請求項11に記載の水質浄化基材。   The water purification substrate according to claim 11, wherein the support is foamed plastic, and adsorbed charcoal is supported in the foamed plastic. 担持体が、水溶性ないし水分解性を有する請求項11ないし15のいずれか1項に記載の水質浄化基材。   The water purification substrate according to any one of claims 11 to 15, wherein the carrier has water solubility or water decomposability. 請求項9に記載の水質浄化剤、請求項10に記載の水質浄化袋、又は請求項11ないし16のいずれか1項に記載の水質浄化基材を用いて、水面上に浮遊する油膜を除去することを特徴とする油膜の除去方法。   An oil film floating on the water surface is removed using the water purification agent according to claim 9, the water purification bag according to claim 10, or the water purification substrate according to any one of claims 11 to 16. A method for removing an oil film.
JP2005210000A 2005-06-06 2005-07-20 Adsorbent charcoal, water-purifying agent, water-purifying sachet, water-purifying substrate and method for removing oil film Pending JP2007015907A (en)

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JP2005210000A JP2007015907A (en) 2005-06-06 2005-07-20 Adsorbent charcoal, water-purifying agent, water-purifying sachet, water-purifying substrate and method for removing oil film
US11/366,932 US20070029246A1 (en) 2005-07-20 2006-03-01 Adsorbent carbon, water quality purifier, water quality purifying bag, water quality purifying substrate and method of removing oil film
DE102006033810A DE102006033810A1 (en) 2005-07-20 2006-07-19 Adsorbent carbon, useful for removing oil (oil film) from natural water and waste water, prepared by heating and carbonizing a coconut mesocarp as its raw material

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JP2005210000A JP2007015907A (en) 2005-06-06 2005-07-20 Adsorbent charcoal, water-purifying agent, water-purifying sachet, water-purifying substrate and method for removing oil film

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013034950A (en) * 2011-08-09 2013-02-21 Mitsunori Ueda Method for producing charcoal ph buffering adjusting mixing particulate material having air permeability, water retaining property, adsorbability, ph adjusting function and method for using the same
KR101236818B1 (en) * 2011-01-07 2013-02-25 윤환헌 A manufacturing method of oil adsorbing materials using coco-peat and oil adsorbing materials using coco-peat manufactured by the same
WO2017022449A1 (en) * 2015-08-04 2017-02-09 株式会社クラレ Carbon precursor derived from plant material
JP2017178697A (en) * 2016-03-30 2017-10-05 株式会社Lixil Granulated active carbon
JP7459365B1 (en) 2023-11-29 2024-04-01 大阪ガスケミカル株式会社 Carbonaceous material and its manufacturing method, and palladium complex adsorption method

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101236818B1 (en) * 2011-01-07 2013-02-25 윤환헌 A manufacturing method of oil adsorbing materials using coco-peat and oil adsorbing materials using coco-peat manufactured by the same
JP2013034950A (en) * 2011-08-09 2013-02-21 Mitsunori Ueda Method for producing charcoal ph buffering adjusting mixing particulate material having air permeability, water retaining property, adsorbability, ph adjusting function and method for using the same
WO2017022449A1 (en) * 2015-08-04 2017-02-09 株式会社クラレ Carbon precursor derived from plant material
JP2017178697A (en) * 2016-03-30 2017-10-05 株式会社Lixil Granulated active carbon
WO2017170754A1 (en) * 2016-03-30 2017-10-05 株式会社Lixil Granulated activated charcoal
JP7459365B1 (en) 2023-11-29 2024-04-01 大阪ガスケミカル株式会社 Carbonaceous material and its manufacturing method, and palladium complex adsorption method

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