JP4856610B2 - Method for producing molded article for water purification - Google Patents

Method for producing molded article for water purification Download PDF

Info

Publication number
JP4856610B2
JP4856610B2 JP2007268768A JP2007268768A JP4856610B2 JP 4856610 B2 JP4856610 B2 JP 4856610B2 JP 2007268768 A JP2007268768 A JP 2007268768A JP 2007268768 A JP2007268768 A JP 2007268768A JP 4856610 B2 JP4856610 B2 JP 4856610B2
Authority
JP
Japan
Prior art keywords
water
purification
bacteria
weight
parts
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP2007268768A
Other languages
Japanese (ja)
Other versions
JP2009095738A (en
Inventor
章 青山
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Aoyamaecosystem corporation
Original Assignee
Aoyamaecosystem corporation
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Aoyamaecosystem corporation filed Critical Aoyamaecosystem corporation
Priority to JP2007268768A priority Critical patent/JP4856610B2/en
Publication of JP2009095738A publication Critical patent/JP2009095738A/en
Application granted granted Critical
Publication of JP4856610B2 publication Critical patent/JP4856610B2/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Water Treatment By Sorption (AREA)

Description

本発明は、水に接触させてその水を浄化する水浄化用成形体及びその製造方法に関する。   The present invention relates to a water purification molded article for purifying water by contacting with water and a method for producing the same.

水に接触させることによりその水を浄化することについては活性炭や炭などの炭素材を他素材と複合的に使用した方法やそのための部材が幾多知られている。(例えば、特許文献1、2参照)これらは汚水中の不純物を活性炭や炭に吸着させることにより水の浄化を行うものであり、活性炭や炭の吸着サイトが不純物等の被吸着物で飽和してしまうと浄化能力が失われるので、頻繁な交換を要する場合が多い。   For purifying the water by bringing it into contact with water, a number of methods using carbon materials such as activated carbon and charcoal in combination with other materials and members therefor are known. (For example, refer to Patent Documents 1 and 2) These purify water by adsorbing impurities in sewage to activated carbon or charcoal, and the adsorption sites of activated carbon and charcoal are saturated with adsorbed substances such as impurities. If this happens, the ability to purify is lost, and frequent replacement is often required.

一方、活性炭や炭を有機物を消費する好気性菌などの菌の担体として利用することにより水処理を行う方法が開示されている。(例えば、特許文献3参照)この方法は汚水中に自然生息している菌が担体に自然に付着することを利用するものであり、その菌が汚水中の有機物を栄養素として増殖して汚泥となり、浄化能力が低下する問題がある。
特開2000−233189号公報 特開2007−831号公報 特開2000−176489号公報
On the other hand, a method is disclosed in which activated carbon or charcoal is used as a carrier for bacteria such as aerobic bacteria that consume organic matter. (For example, refer to Patent Document 3) This method uses the fact that bacteria naturally inhabiting in sewage adhere to the carrier naturally, and the bacteria grow as organic nutrients in the sewage and become sludge. There is a problem that the purification ability is lowered.
JP 2000-233189 A JP 2007-831 A Japanese Patent Application Laid-Open No. 2000-176489

本発明の目的は、水との接触により長期にわたり優れた水浄化能力を発揮する水浄化用成形体及びその製造方法を提供しようとすることである。   An object of the present invention is to provide a molded body for water purification that exhibits excellent water purification performance over a long period of time by contact with water, and a method for producing the same.

本発明の要旨とするところは、炭粉と、水中の有害物質を消費する菌と、接着剤とを含む複合物であり、前記炭粉の粒子が前記接着剤を介して連結されて多孔質体が形成されてなる、水浄化用成形体であることにある。   The gist of the present invention is a composite containing carbon powder, bacteria that consume harmful substances in water, and an adhesive, wherein the particles of the carbon powder are connected via the adhesive and are porous. The object is to be a water purification molded body formed with a body.

前記菌は、乾燥により休眠状態にある菌であり得る。   The bacterium may be a bacterium that is in a dormant state due to drying.

前記菌は、Empedobactr属細菌のSIID2926−1b株(FERM AP−10360)であり得る。 The bacteria may be a Empedobact e r bacterium SIID2926-1b strain (FERM AP- 10360).

前記接着剤は、セメント系の接着剤であり得る。   The adhesive may be a cement-based adhesive.

前記炭粉は、南洋材を炭化焼成してなる炭由来の炭粉を含み得る。   The charcoal powder may include charcoal-derived charcoal powder obtained by carbonizing and firing a southern ocean material.

前記炭粉は、気乾比重0.5以下の木材を炭化焼成してなる炭由来の炭粉を含み得る。   The charcoal powder may include charcoal-derived charcoal powder obtained by carbonizing and firing wood having an air-dry specific gravity of 0.5 or less.

前記炭粉は、木材を450℃以上800℃未満で炭化焼成してなる炭由来の炭粉を含み得る。   The charcoal powder may include charcoal-derived charcoal powder obtained by carbonizing and firing wood at 450 ° C. or higher and lower than 800 ° C.

また、本発明の要旨とするところは、
炭粉と、水中の有害物質を消費する菌と、接着剤とを含む混合物を準備する工程、
前記接着剤を硬化させることにより前記混合物を固化させて成形体を得る工程
を含む水浄化用成形体の製造方法であることにある。
In addition, the gist of the present invention is that
Preparing a mixture containing charcoal powder, bacteria that consumes harmful substances in water, and an adhesive;
It is a method for producing a water purification molded article including a step of solidifying the mixture to obtain a molded article by curing the adhesive.

さらに、本発明の要旨とするところは、前記接着剤がセメントとセメント用凝固剤を含み、
前記混合物を静置することにより前記セメントを凝固させて成形体を得る前記水浄化用成形体の製造方法であることにある。
Further, the gist of the present invention is that the adhesive contains cement and a coagulant for cement,
It is in the manufacturing method of the said molded object for water purification which solidifies the said cement by standing the said mixture and obtains a molded object.

前記水浄化用成形体の製造方法においては、前記セメント用凝固剤が金属イオンの水溶液を含み得る。   In the method for producing a molded body for water purification, the cement coagulant may include an aqueous solution of metal ions.

前記水浄化用成形体の製造方法においては、前記セメント用凝固剤が、塩化カルシウム、塩化カリウム、塩化第二、酸化マグネシウム、塩化マグネシウム、塩化アンモニウムを含み得る。 In the production method of the water purifying moldings, the cement solidification agent, calcium chloride, potassium chloride, ferric chloride, magnesium oxide, magnesium chloride, may include ammonium chloride.

前記水浄化用成形体の製造方法においては、前記菌が乾燥により休眠状態にある菌であり得る。   In the method for producing the molded body for water purification, the bacterium may be a bacterium that is in a dormant state due to drying.

前記水浄化用成形体の製造方法においては、前記菌がEmpedobactr属細菌のSIID2926−1b株(FERM AP−10360)であり得る。 In the production method of the water purifying moldings, the bacteria may be Empedobact e r bacterium SIID2926-1b strain (FERM AP- 10360).

本発明によると、水との接触により長期にわたり優れた水浄化能力を発揮する水浄化用成形体及びその製造方法が提供される。   ADVANTAGE OF THE INVENTION According to this invention, the molded object for water purification which exhibits the water purification capability excellent over the long term by the contact with water, and its manufacturing method are provided.

本発明の水浄化用成形体は、炭粉と水中の有害物質を消費して分解または変化させる機能を有する菌(以下浄化用菌と称する)と接着剤とを含んでなる複合物であり、その炭粉の粒子がその接着剤を介して連結されて多孔質体が形成されてなる水浄化用成形体である。浄化用菌は炭粉の粒子に担持された状態で水浄化用成形体の表面や内部に存在している。   The molded article for water purification of the present invention is a composite comprising a fungus having a function of consuming and decomposing or changing charcoal powder and harmful substances in water (hereinafter referred to as a purification fungus) and an adhesive, This is a water purification molded body in which the carbon powder particles are connected via the adhesive to form a porous body. The purification bacteria are present on the surface and inside of the water purification molded article in a state of being supported on the carbon powder particles.

浄化用菌としては、Bacillus属細菌、Clostriduim属細菌、Thermus属細菌、Pseudomonas属細菌、Empedobactr属細菌から選択される1または複数種の菌が挙げられる。なかでも、本発明の水浄化用成形体に用いられる菌としては、Empedobactr属細菌が好ましい。Empedobactr属細菌のなかでも、SIID2926−1b株(FERM AP−10360)が本発明の水浄化用成形体の水浄化性能のうえで最も好ましい。 The purifying bacteria, Bacillus bacteria, Clostriduim bacteria, Thermus bacteria, Pseudomonas bacteria, include one or more bacteria selected from Empedobact e r bacterium. Among them, as the bacteria used for water purification molded article of the present invention, Empedobact e r bacteria are preferred. Among Empedobact e r bacteria, SIID2926-1b strain (FERM AP- 10360) is most preferable in the water purification performance of the water purifying molded article of the present invention.

本発明の水浄化用成形体に含まれる浄化用菌は、乾燥により休眠状態にある菌であることが好ましい。この場合、水浄化用成形体が水中に投入されるなどして水と接触することにより、浄化用菌が吸湿して活性化し、炭粉の粒子の吸着作用と相俟って優れた水浄化能力を発揮する。   It is preferable that the purification | cleaning microbe contained in the molded object for water purification of this invention is a microbe which is in a dormant state by drying. In this case, when the water purification molded article is brought into contact with water, for example, the purification bacteria absorbs and activates the water, and the water purification is excellent in combination with the adsorption action of the carbon powder particles. Demonstrate ability.

水浄化用成形体の未使用時に、この水浄化用成形体に含まれる浄化用菌が湿潤状態にあり活性化していると、水浄化用成形体の未使用時に、この菌が異常増殖して腐敗し、水浄化能力が充分発揮されない場合がある。   If the purification bacteria contained in the water purification molded body are wet and activated when the water purification molded body is not used, the bacteria will grow abnormally when the water purification molded body is unused. It may rot and water purification ability may not be fully demonstrated.

浄化用菌は比較的強いアルカリ性の水の中では増殖が制限されるので、水浄化用成形体が水に接触している状態では、炭の近傍の水がアルカリ性となることにより、浄化用菌の過度の増殖が抑制される。これにより、浄化用菌の過度の増殖による汚泥の発生が抑制され、過度に増殖した菌により汚水と炭粉粒子との接触が妨げられて炭の吸着能力が低下するという現象も抑制され、浄化能力が長期にわたり維持される。   Since the bacteria for purification are restricted in growth in relatively strong alkaline water, the water in the vicinity of the charcoal becomes alkaline when the water purification molded product is in contact with water, so that the bacteria for purification Excessive growth is suppressed. As a result, the generation of sludge due to excessive growth of the purification bacteria is suppressed, and the phenomenon that the excessive growth of bacteria prevents the contact between the sewage and the charcoal powder particles and the charcoal adsorption capacity is reduced is also suppressed. Ability is maintained for a long time.

接着剤としてはエポキシ系樹脂、アクリル系樹脂で例示されるような樹脂系の接着剤の使用が可能であるが、セメントが好ましい。接着剤がセメントであることにより、水浄化用成形体が水中に置かれた状態で接着剤の近傍がよりアルカリ性となるので、浄化用菌の過度の増殖がさらに抑制され、浄化能力がさらに長期にわたり維持される。   As the adhesive, resin-based adhesives such as those exemplified by epoxy resins and acrylic resins can be used, but cement is preferable. Since the adhesive is cement, the vicinity of the adhesive becomes more alkaline in the state where the molded product for water purification is placed in water, so that excessive proliferation of the bacteria for purification is further suppressed, and the purification ability is further prolonged. Maintained over time.

炭粉としては木、竹、籐、籾殻、等の植物由来のセルロース系物質の炭化物が粒状物してなるものが用いられる。炭粉の粒子の粒径は0.001〜1mmであることが好ましい。炭粉としては南洋材を原料とする炭が粉砕されてなる炭粉が好適に用いられる。南洋材は国産材に比べて成長が速く細胞組織が粗くて大きいので、多孔質の炭化物の細孔のサイズが大きく、この細孔に浄化用菌がはまりやすく、安定した浄化用菌の担持がなされ、浄化用菌の浄化活動が円滑に行なわれ、なら、かしなどの細胞組織の密な国産材の炭粉を使用した場合に比べると、優れた水浄化効果が得られる。また、炭粉に代えて粉状の活性炭を用いた場合は細孔のサイズが炭に比べさらに小さいので、浄化用菌がさらに安定して担持されにくく、長期にわたる優れた水浄化効果を得ることができない。   As the charcoal powder, a granular material of a carbonaceous material derived from a plant such as wood, bamboo, rattan or rice husk is used. The particle size of the carbon powder particles is preferably 0.001 to 1 mm. As the charcoal powder, charcoal powder obtained by pulverizing charcoal made from South Sea wood is preferably used. South Seawood grows faster and has a coarser and larger cell structure than domestic timber, so the pore size of the porous carbide is large. As a result, the purification activity of the bacteria for purification is carried out smoothly, and an excellent water purification effect can be obtained as compared with the case of using charcoal powder of domestic material with dense cellular tissue such as scarecrow. In addition, when powdered activated carbon is used instead of charcoal powder, the size of the pores is even smaller than charcoal, so that the bacteria for purification are less likely to be stably supported, and an excellent water purification effect over a long period of time can be obtained. I can't.

このような南洋材としては、ラミン、ゴム、ラワン、カポール、テレンタン、メランティ、ゲロンガン、ピサンピサン、ファルカータ、プナ、ケンパス、バラン、ビンタングル、ニャトー、アガチス、が例示されるが成長が速く細胞組織が粗くて大きいものであればこれらに限定されない。   Examples of such South Sea materials include lamin, rubber, lawan, capol, terentan, meranti, gelongan, pisanpisan, falcata, puna, kempas, balun, bintangle, nyato, and agathis, but the growth is fast and the tissue is rough. If it is large, it is not limited to these.

南洋材に限らず、本発明において使用する木材の気乾比重が0.5以下であることが細孔のサイズが大きい炭化物を使用できて好ましい。例えば、気乾比重0.5以下の桐、杉類、松類のような木材であることが好ましい。   It is preferable that the air-drying specific gravity of the wood used in the present invention is not more than 0.5, not limited to the South Sea lumber, because carbides having a large pore size can be used. For example, wood such as paulownia, cedar and pine having an air-drying specific gravity of 0.5 or less is preferable.

また、炭粉に用いる炭としては上記セルロース系物質が450℃以上、800℃未満で炭化焼成されたものであることが好ましい。炭化焼成温度が、例えばいわゆる白炭や備長炭におけるように、800℃以上であると、炭が過度にアルカリ性となり、担持された浄化用菌の増殖や活動が妨げられて浄化能力が最大限には発揮されない傾向にある。炭化焼成温度が450℃を下回ると炭が酸性となり、担持された浄化用菌の増殖や活動が妨げられて浄化能力が最大限には発揮されない傾向にある。   Further, as the charcoal used for the charcoal powder, it is preferable that the cellulosic material is carbonized and fired at 450 ° C. or higher and lower than 800 ° C. When the carbonization firing temperature is 800 ° C. or higher, as in, for example, so-called white coal or Bincho charcoal, the charcoal becomes excessively alkaline, and the growth and activity of the carried purification bacteria are hindered to maximize the purification capacity. There is a tendency not to be demonstrated. When the carbonization firing temperature is lower than 450 ° C., the charcoal becomes acidic, and the growth and activity of the carried purification bacteria are hindered, and the purification ability tends not to be exhibited to the maximum.

炭粉は、炭を公知の粉砕手段により粉砕して得てもよい。おがくずや木材の粉砕物などの、木材の粒状物を焼成して得てもよい。   The charcoal powder may be obtained by crushing charcoal with a known crushing means. You may obtain by baking the granular material of wood, such as sawdust and the ground material of wood.

本発明の水浄化用成形体は、炭粉と、浄化用菌と、硬化あるいは凝固前の接着剤と、必要ならば接着剤の硬化剤あるいは凝固剤と、を含む混合物を含む成形体前駆体を、接着剤の硬化あるいは凝固により固化させることにより得ることができるが、接着剤がセメントである場合、水のみを凝固剤として使用すると成形体の必要な強度を得るためには、大量の水を必要とし、成形体前駆体が大量の水を含有するものとなる。このため、成形体前駆体中の浄化用菌がその水に浸かることとなり、水に浸かった浄化用菌が活性化し、浄化用菌が活性化した状態で成形体前駆体の固化が行なわれ、固化により浄化用菌が損傷されてしまう傾向にある。またセメントの固化により炭粉の細孔の大部分が閉塞され、細孔中の浄化用菌の活動が阻害される。セメントの量を減らして閉塞を防ぎ、多孔質の成形体を得ようとすれば、成形体の強度が低いものとなってハンドリングに支障をきたすことがあり、取り扱い方や用途が限定される。   The molded article for water purification according to the present invention is a molded article precursor comprising a mixture containing charcoal powder, purification bacteria, an adhesive before curing or coagulation, and, if necessary, an adhesive curing agent or coagulant. However, when the adhesive is cement, if only water is used as the coagulant, a large amount of water is required to obtain the required strength of the molded product. Therefore, the molded body precursor contains a large amount of water. For this reason, the purification bacteria in the molded body precursor are immersed in the water, the purification bacteria immersed in water are activated, and the molded body precursor is solidified in the activated state. There exists a tendency for the bacteria for purification to be damaged by solidification. In addition, the solidification of the cement blocks most of the pores of the carbon powder, thereby inhibiting the activity of the purification bacteria in the pores. If an attempt is made to reduce the amount of cement to prevent clogging and obtain a porous molded body, the strength of the molded body may be low, which may hinder handling, and the handling method and application are limited.

本発明においては、セメントの凝固剤として金属イオンを含む水溶液を用いることにより、セメントを接着剤とする成形体前駆体の固化に必要な水分を少なくし、かつ充分な強度の成形体が得られることがわかった。これにより、成形体前駆体中の浄化用菌を乾燥による休眠状態で成形体前駆体の固化を行なうことができる。またセメントの固化により炭粉の細孔が閉塞されることが少なく、成形体を水に投じて浄化作用を行うときに浄化用菌が活性を回復し細孔中の浄化用菌の活動が充分に行なわれる。   In the present invention, by using an aqueous solution containing metal ions as a coagulant for cement, it is possible to reduce the water necessary for solidification of the molded body precursor using cement as an adhesive and to obtain a molded body having sufficient strength. I understood it. Thereby, solidification of a molded object precursor can be performed in the dormant state by drying the microbe for purification | cleaning in a molded object precursor. Also, the pores of the carbon powder are less likely to be clogged by solidification of the cement, and when the molded product is poured into water for purification, the purification bacteria recover their activity and the purification bacteria in the pores are sufficiently active To be done.

このように、成形体前駆体の段階では、浄化用菌は乾燥により休眠状態にあることが好ましい。このような成形体前駆体を固化してなる本発明の水浄化用成形体においても、この成形体に担持されている浄化用菌は乾燥により安定した休眠状態にあり、このような本発明の水浄化用成形体は性能を低下させることなく未使用状態での長期の保存が可能である。   Thus, at the stage of the molded body precursor, the purification bacteria are preferably in a dormant state by drying. Also in the water purification molded body of the present invention obtained by solidifying such a molded body precursor, the purification bacteria carried on the molded body are in a stable dormant state due to drying, and The molded body for water purification can be stored for a long time in an unused state without degrading performance.

セメントの凝固剤として用いられる水溶液に含有される好適な金属イオンとしては、カルシウムイオン、カリウムイオン、第二鉄イオン、マグネシウムイオン、が例示される。   Examples of suitable metal ions contained in the aqueous solution used as a coagulant for cement include calcium ions, potassium ions, ferric ions, and magnesium ions.

さらに、凝固剤として用いられる水溶液が、塩化カルシウム、塩化カリウム、塩化第二鉄、酸化マグネシウム、塩化マグネシウム、塩化アンモニウムを含む場合は、少量の水の使用により高強度の成形体が得られ、成形体を水に投じて浄化作用を行うときに細孔中の浄化用菌の最も充分な活動が得られる。   Furthermore, when the aqueous solution used as a coagulant contains calcium chloride, potassium chloride, ferric chloride, magnesium oxide, magnesium chloride, or ammonium chloride, a high-strength molded product can be obtained by using a small amount of water, and molding When the body is poured into water for purification, the most sufficient activity of the purification bacteria in the pores is obtained.

また、本発明においては、通常は、浄化用菌を用いるときにはその培養物と混合状態のものが用いられる。また、浄化用菌のかわりに浄化用菌の培養物を用いることができる。培養物とは浄化用菌の培養に用いた培地と浄化用菌の育成に伴ってその培地に放出された化合物や酵素を含むものをいう。浄化用菌自体が水中の化合物を消費して分解できるが、浄化用菌が産生する酵素等も同様の機能を有すると考えられる。   In the present invention, usually, when the purification bacteria are used, those in a mixed state with the culture are used. In addition, a culture of purification bacteria can be used instead of the purification bacteria. The culture refers to a culture medium used for culturing the bacteria for purification and a compound or enzyme released into the culture medium as the bacteria for purification are grown. Although the purification bacteria themselves can be decomposed by consuming the compounds in the water, the enzymes produced by the purification bacteria are considered to have the same function.

本発明の水浄化用成形体は、上述のように、炭粉と、浄化用菌および/またはその培養物と、凝固あるいは硬化前の接着剤と、必要に応じて添加される硬化剤あるいは凝固剤を攪拌混合して成形体前駆体となし、所定の型にいれて接着剤を硬化あるいは凝固などによりかたまらせて得ることができるが、この成形体前駆体は、炭粉100重量部に対して、浄化用菌および/またはその培養物5〜20重量部、凝固あるいは硬化前の接着剤15〜60重量部が配合されてなることが好ましい。   As described above, the water purification molded article of the present invention comprises charcoal powder, purification bacteria and / or cultures thereof, an adhesive before coagulation or curing, and a curing agent or coagulation added as necessary. It can be obtained by stirring and mixing the agent to form a molded body precursor, and putting it in a predetermined mold to stiffen the adhesive by curing or coagulation. This molded body precursor is added to 100 parts by weight of carbon powder. On the other hand, it is preferable that 5 to 20 parts by weight of the purifying bacteria and / or culture thereof and 15 to 60 parts by weight of the adhesive before solidification or curing are blended.

接着剤がセメントである場合、金属イオンを含む水溶液からなる凝固剤が成形体前駆体全体に対して0.5〜3重量部配合されることが好ましい。   When the adhesive is cement, 0.5 to 3 parts by weight of a coagulant made of an aqueous solution containing metal ions is preferably added to the entire molded body precursor.

接着剤がセメントである場合、成形体前駆体に含まれる水の割合は成形体前駆体全体に対して5〜30重量%であることが好ましい。この水の割合がこの範囲を下回ると成形体の強度が不足する。この範囲を上回ると浄化用菌および/またはその培養物が膨潤してセメントの凝固が妨げられて成形体がもろくなり、ハンドリングに支障をきたす。   When the adhesive is cement, the ratio of water contained in the molded body precursor is preferably 5 to 30% by weight with respect to the entire molded body precursor. If the proportion of this water is below this range, the strength of the molded product will be insufficient. If it exceeds this range, the bacteria for purification and / or the culture thereof swell, the solidification of the cement is hindered, the molded product becomes brittle, and handling is hindered.

接着剤がセメントである場合、成形体前駆体に含まれる浄化用菌および/またはその培養物の乾燥物の配合割合が炭粉100重量部に対して5〜20重量部の範囲を下回ると、水浄化用成形体としての水浄化能力が充分でない。この範囲を上回ると、浄化用菌および/またはその培養物が膨潤して成形体がもろくなり、ハンドリングに支障をきたす。 When the adhesive is cement, when the mixing ratio of the purification bacteria contained in the molded body precursor and / or the dried product thereof is less than 5 to 20 parts by weight with respect to 100 parts by weight of the carbon powder, Water purification ability as a water purification molded product is not sufficient. Above this range, the germs for purification and / or their cultures swell and the molded body becomes brittle, which hinders handling.

本発明においては、成形体前駆体中の浄化用菌および/またはその培養物の乾燥物とは、その浄化用菌および/またはその培養物の水分率が50重量%以下であるものをいう。そのためには、浄化用菌および/またはその培養物を、水分率50重量%以下の乾燥状態で硬化前の接着剤と混合することが好ましい。   In the present invention, the purification bacteria and / or the dried product of the culture in the molded body precursor means that the moisture content of the purification bacteria and / or the culture is 50% by weight or less. For that purpose, it is preferable to mix the bacteria for purification and / or the culture thereof with an adhesive before curing in a dry state with a moisture content of 50% by weight or less.

また、本発明においては、浄化用菌を含む液に炭粉を混合し、浄化用菌を炭粉に吸着させたのち硬化前の接着剤等と混合して成形体前駆体を得てもよい。この場合、接着剤に混合する前に浄化用菌を吸着させた炭粉を乾燥しておくことが好ましい。あるいは本発明においては、浄化用菌を含む液と炭粉と接着剤等とを混合して成形体前駆体を得てもよい。この場合はこの成形体前駆体は固化前に乾燥しておくことが好ましい。   Further, in the present invention, a molded product precursor may be obtained by mixing charcoal powder with a liquid containing purification bacteria, adsorbing the purification bacteria to the carbon powder, and then mixing with an adhesive before curing. . In this case, it is preferable to dry the charcoal powder on which the purification bacteria are adsorbed before mixing with the adhesive. Or in this invention, you may obtain the molded object precursor by mixing the liquid containing the microbe for purification | cleaning, carbon powder, an adhesive agent, etc. In this case, the molded body precursor is preferably dried before solidification.

本発明の水浄化用成形体は、汚水に浸漬して静置しておく態様で浄化を行う他に、流水の経路の一部分に配置してその流水と接触させる態様で浄化を行うこともできる。   The molded product for water purification according to the present invention can be purified in a mode in which it is placed in a part of a flow path of water and brought into contact with the flowing water, in addition to performing purification in a mode in which it is immersed in sewage and left standing. .

実施例1
浄化用菌の培養
水400重量部に浄化用菌(Empedobactr属細菌のSIID2926−1b株(FERM AP−10360))0.5重量部、グルコース10重量部、ペプトン5重量部、酵母エキス2.5重量部を添加し、30℃で5日間培養し培養液を得た。この配合比率によるこの培養液4000重量部に米糠10000重量部、コーヒー粕1000重量部、蜂蜜2重量部を加え、発酵熱による温度上昇に注意しつつ55℃を超えないように適宜攪拌して5日間静置培養し培養物を得た。この培養物を自然乾燥して乾燥培養物を得た。この乾燥培養物の水分率は15%であった。
Example 1
(SIID2926-1b strain (FERM AP- 10360) of Empedobact e r bacteria) 0.5 parts by weight purifying bacteria culture water 400 parts by weight of purifying bacteria, glucose 10 parts by weight, peptone 5 parts, yeast extract 2 .5 parts by weight was added and cultured at 30 ° C. for 5 days to obtain a culture solution. Add 10000 parts by weight of rice bran, 1000 parts by weight of coffee bran, and 2 parts by weight of honey to 4000 parts by weight of this culture solution according to this blending ratio, and stir appropriately so as not to exceed 55 ° C. while paying attention to temperature rise due to fermentation heat. The culture was obtained by stationary culture for days. This culture was naturally dried to obtain a dry culture. The moisture content of this dry culture was 15%.

炭粉
南洋材であるファルカータを約600℃で乾留して得た炭を粉砕し、平均粒径約0.5mmの炭粉としたものを用いた。
成形体前駆体
Charcoal powder Charcoal powder obtained by dry-distilling Falcarta, which is a South Sea material, at about 600 ° C. was pulverized to obtain charcoal powder having an average particle size of about 0.5 mm.
Molded body precursor

上記炭粉100重量部、水20重量部、普通ポルトランドセメント50重量部、セメント用凝固剤1重量部を攪拌混合して混合物を得た。この混合物に上記乾燥培養物10重量部を加えて攪拌混合して成形体前駆体を得た。セメント用凝固剤は、塩化カルシウム2量部、塩化カリウム2重量部、塩化第二鉄2重量部、酸化マグネシウム2重量部、塩化マグネシウム2量部、塩化アンモニウム2重量部、水2500重量部からなる水溶液である。   100 parts by weight of the above carbon powder, 20 parts by weight of water, 50 parts by weight of ordinary Portland cement, and 1 part by weight of a coagulant for cement were stirred and mixed to obtain a mixture. To this mixture, 10 parts by weight of the dried culture was added and stirred to obtain a molded body precursor. The cement coagulant comprises 2 parts by weight of calcium chloride, 2 parts by weight of potassium chloride, 2 parts by weight of ferric chloride, 2 parts by weight of magnesium oxide, 2 parts by weight of magnesium chloride, 2 parts by weight of ammonium chloride, and 2500 parts by weight of water. It is an aqueous solution.

水浄化用成形体
上記成形体前駆体を型枠に入れて約5000Paで加圧後24時間静置してサイズ2cm×5cm×5cmのブロック状の水浄化用成形体を得た。
Water Purified Molded Body The molded body precursor was placed in a mold, pressed at about 5000 Pa, and allowed to stand for 24 hours to obtain a block-shaped water purification molded body having a size of 2 cm × 5 cm × 5 cm.

浄化テスト1
汚水として市街を流れる川から採取した水を用いた。この水(原水)のCODは15ppmであった。
Purification test 1
Water collected from a river flowing through the city was used as sewage. The COD of this water (raw water) was 15 ppm.

A槽、B槽の2個の槽(容量200リットル)それぞれに原水各100リットルを入れた。A槽に、ブロック状の水浄化用成形体50個を投入した。B槽に、市販の樹脂(PP)製接触濾材(径約5cmの円盤状)を100枚投入した。   100 liters of raw water was added to each of the two tanks (capacity 200 liters) of tank A and tank B. In the tank A, 50 block-shaped water purification molded bodies were charged. 100 pieces of commercially available resin (PP) contact filter media (a disk shape having a diameter of about 5 cm) were put into the B tank.

次いで各槽の水を曝気状態で48時間経過させた後のCODは、A槽約8ppm、B槽約13ppmであり、上記水浄化用成形体のすぐれた浄化能力を確認した。   Next, COD after allowing water in each tank to pass for 48 hours in an aerated state was about 8 ppm for tank A and about 13 ppm for tank B, and the excellent purification capability of the water purification molded product was confirmed.

浄化テスト2
a槽、b槽の2個のガラス水槽(容量50リットル)それぞれに井戸水20リットルを入れて太町約5cmの金魚各5匹を飼育した。a槽に上記水浄化用成形体3個を投入し水槽の底に静置した。各槽とも通常の曝気のもとに飼育を行い、6日経過後の水質を測定した結果を表1に示す。
Purification test 2
20 liters of well water was placed in each of two aquarium tanks (a tank and b tank) (capacity: 50 liters), and 5 goldfishes of approximately 5 cm in Taimachi were raised. The three water purification molded bodies were put into the tank a and allowed to stand at the bottom of the tank. Table 1 shows the results of measuring the water quality after 6 days of breeding under normal aeration for each tank.

Figure 0004856610
Figure 0004856610

また、a槽はb槽にくらべてアオコの発生が少なく、水の透明性が高く、b槽がアオコにより水槽壁が曇ったのに対して、a槽はアオコによる水槽壁の曇りがほとんどなかった。   In addition, tank a has less water-blooming than tank b and water transparency is high, and tank a has a water tank wall clouded by water, whereas tank a has almost no clouding of the water tank wall by water. It was.

浄化テスト3
図1に示すように、長さ5m、内径20cmの塩ビ管を2つに縦割りした樋状物2の底部4に、上記成形体前駆体を樋状物2の長手方向に沿って断面かまぼこ形状に敷き詰めて、12日間静置して固化させ、樋状物2とかまぼこ型水浄化用成形体6との複合体である長尺複合体8を得た。かまぼこ型水浄化用成形体6の上面10と樋状物2の露出内壁12とで、樋状物2の長手方向に延びる溝14が形成されている。図2に示すように、複合体8を長手方向に関して水平から傾けて、かつ溝14が上方に開口するように配置させ、循環ポンプ16と導水パイプ18により水を複合体8の上方片端部20に導いて、上面10上を流下させた。上面10上を流下した水を複合体8の下端部21から受け槽22(容量100リットル)に受け、再び循環ポンプ16と導水パイプ18により水を複合体8の上方片端部20に導いて流量5リットル/mimで循環させた。
Purification test 3
As shown in FIG. 1, the molded body precursor is cross-sectioned along the longitudinal direction of the rod-like material 2 at the bottom 4 of the rod-like material 2 obtained by vertically dividing a PVC pipe having a length of 5 m and an inner diameter of 20 cm into two. The product was spread in a shape and allowed to stand for 12 days to solidify to obtain a long composite 8 that is a composite of the bowl 2 and the kamaboko-type water purification molded product 6. A groove 14 extending in the longitudinal direction of the bowl-shaped object 2 is formed by the upper surface 10 of the kamaboko-type water purification molded body 6 and the exposed inner wall 12 of the bowl-shaped object 2. As shown in FIG. 2, the composite 8 is inclined from the horizontal with respect to the longitudinal direction and the groove 14 is opened upward, and water is supplied to the upper end 20 of the composite 8 by the circulation pump 16 and the water guide pipe 18. To flow down on the upper surface 10. The water flowing down on the upper surface 10 is received in the receiving tank 22 (capacity: 100 liters) from the lower end 21 of the composite 8, and the water is again guided to the upper one end 20 of the composite 8 by the circulation pump 16 and the water guide pipe 18. Circulation was performed at 5 liter / mim.

始めの24時間は水のみを循環させた。
次に、循環を続けながら受け槽22に市販の粒状肥料(8−8−8)を100g投入し溶解させた。この直後の受け槽22内の水を採取しサンプル1とした。その後17時間経過後に上面10上を流下する水を水質測定用に採取し、サンプル2とした。
そのまま水を循環させ、循環開始時から48時間後に循環を停止し、同時に複合体8の上面10を水道水によりその圧を利用して洗浄した。洗浄に用いた水を採取し、サンプル3とした。
この洗浄とともに循環水を清水に交換し、水の循環を再開した。この再開時から24時間経過の時点で上面10上を流下する水を水質測定用に採取し、サンプル4とした。
Only water was circulated for the first 24 hours.
Next, 100 g of commercially available granular fertilizer (8-8-8) was added to the receiving tank 22 and dissolved while the circulation was continued. The water in the receiving tank 22 immediately after this was sampled and used as sample 1. Thereafter, water flowing down on the upper surface 10 after 17 hours was collected for water quality measurement and used as sample 2.
Water was circulated as it was, and the circulation was stopped 48 hours after the start of circulation, and at the same time, the upper surface 10 of the composite 8 was washed with tap water using the pressure. The water used for washing was collected and used as sample 3.
Along with this washing, the circulating water was replaced with fresh water, and the water circulation was resumed. The water flowing down on the upper surface 10 after 24 hours from the restart was collected for water quality measurement and used as sample 4.

各サンプルの水質測定結果を表2に示す。水浄化用成形体との接触流下により流水中の肥料成分(窒素成分、リン成分)が浄化されたことを確認した。   Table 2 shows the water quality measurement results of each sample. It was confirmed that the fertilizer components (nitrogen component, phosphorus component) in the flowing water were purified by the flow of contact with the molded body for water purification.

Figure 0004856610
Figure 0004856610

実施例2
実施例1で得たと同様の成形体前駆体を型に入れて実施例1と同様にして固化させ、径3cm、高さ3cmの円柱形の水浄化用成形体を得た。この成形体をサンプル(1)とする。
Example 2
A molded body precursor similar to that obtained in Example 1 was placed in a mold and solidified in the same manner as in Example 1 to obtain a cylindrical water purification molded body having a diameter of 3 cm and a height of 3 cm. This molded product is designated as sample (1).

ビーカー(容量1リットル)に培地(溶液)を600ccを入れ、さらにサンプル(1)をビーカーに6個投入した。その後、養魚用曝気装置による培地の曝気を継続しつつ、サンプル投入後の培地のpH、成分(イオン、グルコース)、COD、を測定し、表4、5に示す結果を得た。   600 cc of the medium (solution) was put into a beaker (capacity: 1 liter), and six samples (1) were put into the beaker. Then, while continuing the aeration of the culture medium with the aeration apparatus for fish culture, the pH, components (ions, glucose), COD of the culture medium after the sample was added were measured, and the results shown in Tables 4 and 5 were obtained.

表3に培地1リットル中の成分を示す。残余は蒸留水である。この培地のpHは7.0であった。   Table 3 shows the components in 1 liter of medium. The balance is distilled water. The pH of this medium was 7.0.

Figure 0004856610
Figure 0004856610

Figure 0004856610
Figure 0004856610

Figure 0004856610
Figure 0004856610

表4、5における変化率はサンプル投入直後(経過時間0)の各項目の測定値を100としたときの対応する項目の測定値の比率を示す。   The rate of change in Tables 4 and 5 indicates the ratio of the measured value of the corresponding item when the measured value of each item immediately after sample introduction (elapsed time 0) is 100.

表4、5で示されるように、硝酸イオンは2日目に、リン酸イオン、亜硝酸イオンは2〜3日目にほぼ消失した。アンモニウムイオンは3日でほぼ半減した。   As shown in Tables 4 and 5, nitrate ions almost disappeared on the second day, and phosphate ions and nitrite ions almost disappeared on the second to third days. Ammonium ions were almost halved in 3 days.

pHの上昇はサンプルからセメント成分由来のアルカリイオンの溶出によるものと思われる。   The increase in pH seems to be due to elution of alkali ions derived from cement components from the sample.

グルコースは菌の生育にともない減少した。CODは途中減少し、後に菌の代謝物及び菌体分解物等により再び上昇した。なお、液中の菌のDNAを調べたが、主として単悍菌であり、サンプル(1)に含まれている菌とは一致しなかった。培地(溶液)中の、アンモニウムイオン、硝酸イオン、亜硝酸イオン及びリン酸イオンの減少は、水浄化用成形体への吸着によるものではなく、水浄化用成形体中の菌の増殖により消費されたことによるものと思われる。   The glucose decreased with the growth of the fungus. COD decreased on the way, and later rose again due to fungal metabolites and cell degradation products. In addition, although the DNA of the bacterium in the liquid was examined, it was mainly a gonococcus and did not match the bacterium contained in the sample (1). The decrease of ammonium ion, nitrate ion, nitrite ion and phosphate ion in the medium (solution) is not due to adsorption to the water purification molded product, but is consumed by the growth of bacteria in the water purification molded product. This is probably due to this.

実施例3
睡蓮鉢(径80cm、高さ60cm)に水を張り、睡蓮苗を10株定着させた。1ヶ月放置したところ水が濁って睡蓮の成長が停滞した。この鉢の水底に実施例1で得たと同様の水浄化用成形体10個を投入した。その後20日経過させたところ、水が澄んできて睡蓮の生育が進行しはじめた。さらにその後1ヶ月で睡蓮鉢の水面を満たすぼどに睡蓮が生育した。この間、水はきわめて清澄な状態を維持した。
Example 3
Water was added to a water lily bowl (diameter 80 cm, height 60 cm) to fix 10 water lily seedlings. After standing for one month, the water became cloudy and the growth of water lilies stagnated. Ten water purification molded bodies similar to those obtained in Example 1 were put into the bottom of the bowl. After 20 days, the water became clear and the water lily began to grow. One month later, water lilies grew in the pot that filled the water surface of the water lilies. During this time, the water remained very clear.

比較例1
実施例3と同様な睡蓮鉢に水を張り、実施例3と同時期に睡蓮苗を10株定着させた。1ヶ月放置したところ水が濁って睡蓮の成長が停滞した。その後50日放置を続けたが、水は濁ったままであり、雑草類が繁茂し睡蓮の生育は停滞したままであった。
Comparative Example 1
Water was applied to a water lily pot similar to Example 3, and 10 water lily seedlings were fixed at the same time as Example 3. After standing for one month, the water became cloudy and the growth of water lilies stagnated. After 50 days, the water remained cloudy, the weeds grew and the water lily grew stagnant.

実施例4
実施例1で得たと同様の成形体前駆体を用いて、この成形体前駆体を型枠に入れて静置してサイズ5cm×10cm×20cmのブロック状の水浄化用成形体を得た。この水浄化用成形体20個を、あおこの発生で濁り底が見えない状態の池(20m、深さ50cm)に投入し池底に静置した。1ヶ月経過後、池は清澄になり、底まで透き通って見えるようになっていた。
Example 4
Using the same molded body precursors obtained in Example 1, to obtain a block-shaped water-purifying compact of size 5 cm × 10 cm × 20 cm to stand put the molded body precursor into a mold. Twenty of these water purification molded bodies were put into a pond (20 m 2 , depth 50 cm) in a state where the turbid bottom could not be seen due to the occurrence of the cocoons, and was allowed to stand on the pond bottom. After a month, the pond became clear and transparent to the bottom.

比較例2
炭粉に代えて平均粒径約0.5mmの活性炭を用いたほかは実施例4と同様にして水浄化用成形体を得た。この水浄化用成形体20個を、あおこの発生で濁り底が見えない状態の池(20m、深さ50cm)に投入し池底に静置した。投入当初は池がやや清澄になったが、1ヶ月経過後、池は濁りが目立つようになった。
Comparative Example 2
A water purification molded article was obtained in the same manner as in Example 4 except that activated carbon having an average particle size of about 0.5 mm was used in place of the carbon powder. Twenty of these water purification molded bodies were put into a pond (20 m 2 , depth 50 cm) in a state where the turbid bottom could not be seen due to the occurrence of the cocoons, and was allowed to stand on the pond bottom. At the beginning of the pond, the pond became slightly clear, but after a month, the pond became cloudy.

実施例5
実施例1で用いたと同様の炭粉100重量部、エポキシ樹脂(商品名:エピコート828)20重量部、常温硬化用触媒0.2重量部を混合攪拌し、次いで実施例1で用いたと同様の乾燥培養物10重量部を加えて混合攪拌し成形体前駆体を得た。この成形体前駆体を型枠に入れて35℃で48時間静置してサイズ2cm×10cm×10cmのブロック状の水浄化用成形体を得た。得られた水浄化用成形体を、実施例3と同様にして睡蓮苗を定着して水が濁って睡蓮の成長が停滞した睡蓮鉢の水底に投入した。その後20日経過させたところ、水が澄んできて睡蓮の生育が進行しはじめた。さらにその後1ヶ月で睡蓮鉢の水面を満たすぼどに睡蓮が生育した。この間、水は清澄な状態を維持した。
Example 5
100 parts by weight of the same carbon powder as used in Example 1, 20 parts by weight of an epoxy resin (trade name: Epicoat 828), and 0.2 parts by weight of a room temperature curing catalyst were mixed and stirred, and then the same as that used in Example 1 10 parts by weight of the dried culture was added and mixed and stirred to obtain a molded body precursor. This molded body precursor was put into a mold and allowed to stand at 35 ° C. for 48 hours to obtain a block-shaped molded body for water purification having a size of 2 cm × 10 cm × 10 cm. In the same manner as in Example 3, the obtained water purification molded article was put into the water bottom of a water lily pot where water lily seedlings were fixed and the water became cloudy and the growth of water lily stagnated. After 20 days, the water became clear and the water lily began to grow. One month later, water lilies grew in the pot that filled the water surface of the water lilies. During this time, the water remained clear.

実施例6
乾燥培養物として、上水道用の浄化槽で採取した、Bacillus属細菌を含有する活性汚泥、の乾燥物(水分率15重量%)を用いた他は実施例1と同様にして水浄化用成形体を得た。得られた水浄化用成形体1個を、CODが50ppmの汚水を200cc入れたビーカー中に投入した。投入から24時間後の汚水のCODは25ppmであった。
Example 6
A molded product for water purification was obtained in the same manner as in Example 1 except that a dried product (active water sludge containing Bacillus genus bacteria) collected in a water purification tank was used as the dried culture. Obtained. One obtained water purification molding was put into a beaker containing 200 cc of sewage with a COD of 50 ppm. The COD of sewage after 24 hours from the introduction was 25 ppm.

その他、本発明は、主旨を逸脱しない範囲で当業者の知識に基づき種々なる改良、修正、変更を加えた態様で実施できるものである。   In addition, the present invention can be carried out in a mode in which various improvements, modifications, and changes are added based on the knowledge of those skilled in the art without departing from the spirit of the present invention.

水浄化に用いる、本発明の水浄化用成形体を用いた長尺複合体の断面図である。It is sectional drawing of the elongate composite_body | complex using the molded object for water purification of this invention used for water purification. 図1に示す長尺複合体を用いた水浄化実験の態様を示す側面模式図である。It is a side surface schematic diagram which shows the aspect of the water purification experiment using the elongate composite_body | complex shown in FIG.

符号の説明Explanation of symbols

2:樋状物
8:長尺複合体
16:循環ポンプ
18:導水パイプ
22:受け槽
2: Saddle-like object 8: Long composite 16: Circulation pump 18: Water guide pipe 22: Receiving tank

Claims (2)

乾気比重が0.5以下の南洋材を450℃以上800℃未満で炭化焼成してなる炭由来の炭粉100重量部と、
セメント15〜60重量部と、
乾燥により休眠状態にある、水中の有害物質を消費する菌と該菌の培養物のいずれかまたは両方5〜20重量部と、
金属イオンの水溶液を含むセメント用凝固剤0.5〜3重量部と、
水とを含み、前記水の配合比が全体の5〜30重量%である混合物
を静置することにより前記セメントを凝固させて成形体を得る水浄化用成形体の製造方法。
100 parts by weight of charcoal powder derived from charcoal obtained by carbonizing and firing a South Sea material having a dry air specific gravity of 0.5 or less at 450 ° C. or more and less than 800 ° C.
15-60 parts by weight of cement,
5 to 20 parts by weight of either or both of a bacterium that consumes harmful substances in water and is in a dormant state due to drying, and a culture of the bacterium,
0.5-3 parts by weight of a coagulant for cement containing an aqueous solution of metal ions;
The manufacturing method of the molded object for water purification which solidifies the said cement by leaving still the mixture which contains the said water and the mixing ratio of the said water is 5-30 weight% of the whole.
前記セメント用凝固剤が、塩化カルシウム、塩化カリウム、塩化第二鉄、酸化マグネシウム、塩化マグネシウム、塩化アンモニウムを含む請求項1に記載の水浄化用成形体の製造方法。 The method for producing a molded article for water purification according to claim 1, wherein the cement coagulant contains calcium chloride, potassium chloride, ferric chloride, magnesium oxide, magnesium chloride, and ammonium chloride.
JP2007268768A 2007-10-16 2007-10-16 Method for producing molded article for water purification Expired - Fee Related JP4856610B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2007268768A JP4856610B2 (en) 2007-10-16 2007-10-16 Method for producing molded article for water purification

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2007268768A JP4856610B2 (en) 2007-10-16 2007-10-16 Method for producing molded article for water purification

Publications (2)

Publication Number Publication Date
JP2009095738A JP2009095738A (en) 2009-05-07
JP4856610B2 true JP4856610B2 (en) 2012-01-18

Family

ID=40699255

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2007268768A Expired - Fee Related JP4856610B2 (en) 2007-10-16 2007-10-16 Method for producing molded article for water purification

Country Status (1)

Country Link
JP (1) JP4856610B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5070254B2 (en) * 2009-07-24 2012-11-07 株式会社アオヤマエコシステム Charcoal-metal composite for water treatment and molded product for charcoal-metal composite
JP5646895B2 (en) * 2010-07-20 2014-12-24 株式会社日立製作所 Culture tank
JP6099076B2 (en) * 2012-08-20 2017-03-22 多機能フィルター株式会社 Deodorant biodegradation promoting material and deodorant biodegradation promoting method

Family Cites Families (22)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6244184A (en) * 1985-08-20 1987-02-26 Ibiden Co Ltd Carrier suitable for immobilization of cell of microorganism and production thereof
JPH026897A (en) * 1988-01-21 1990-01-11 Nissei Food Kk Method of cleaning water by cleaning agent formed by mixing three materials
JPH02307593A (en) * 1989-05-22 1990-12-20 Kyodo Kumiai Okayamashi Kankyo Seibi Kyokai Microbe-containing seeding agent for water treatment facility
JPH084792B2 (en) * 1993-09-29 1996-01-24 関東くみあい化成工業株式会社 Wastewater treatment system
JPH11347321A (en) * 1998-06-03 1999-12-21 Denso Corp Filter element, manufacture thereof and bath water cleaning device
JP2000233195A (en) * 1999-02-12 2000-08-29 Kit:Kk Filter medium for treating water
JP2000308864A (en) * 1999-04-26 2000-11-07 Naoyoshi Kayama Solid material obtained using carbonized scrap wood
JP3972282B2 (en) * 1999-06-21 2007-09-05 大有コンクリート工業株式会社 Water purification method for rivers using porous material with aggregate of clinker ash
JP2002079285A (en) * 2000-06-27 2002-03-19 Yokohama Rubber Co Ltd:The Carbonaceous microorganism fixed carrier
JP2002018459A (en) * 2000-07-06 2002-01-22 Tokico Ltd Apparatus for cleaning water
JP2002096084A (en) * 2000-07-06 2002-04-02 Kawasaki Steel Corp Environment-purifying material produced from refuse solid fuel and method for producing the same
JP2002052339A (en) * 2000-08-10 2002-02-19 Takehiko Oki Purification body and purification material
JP2003190982A (en) * 2001-12-26 2003-07-08 Fukuoka Kimie Material for purifying water, bag-in material for purifying water, facility for purifying water using this, and method for purifying water
JP2003245681A (en) * 2002-02-22 2003-09-02 Miki Riken Kogyo Kk Microorganism immobilizing carrier for fluidized bed
JP2004230271A (en) * 2003-01-29 2004-08-19 Sekyurion Nijuyon Kk Solid material for treating wastewater, manufacturing method for the same, and wastewater treatment method
WO2006011280A1 (en) * 2004-07-29 2006-02-02 Komori Bio Laboratory Inc. Environmental purification method and environmental purification agent
JP2006136799A (en) * 2004-11-11 2006-06-01 Wako Concrete Kogyo Kk Water quality improvement method by napping microorganism
JP4627718B2 (en) * 2004-12-21 2011-02-09 株式会社静内衛生社 Method for solidifying seeding agent and solidified seeding agent
JP4722496B2 (en) * 2005-01-18 2011-07-13 株式会社アオヤマエコシステム Cut flowers
JP2006213547A (en) * 2005-02-02 2006-08-17 Team Work:Kk Wood-based granular activated carbon and its manufacturing method
JP2007302486A (en) * 2006-05-09 2007-11-22 Aoyama Eco System:Kk Heat insulating material
JP5008184B2 (en) * 2006-10-07 2012-08-22 武彦 大木 Sludge purification civil engineering method

Also Published As

Publication number Publication date
JP2009095738A (en) 2009-05-07

Similar Documents

Publication Publication Date Title
CN111285462B (en) Synergistic denitrification composite suspended filler, preparation method and application thereof
EA024049B1 (en) Sludge treatment method and apparatus and application of said method and apparatus for wastewater bio-treatment
CN105236564B (en) A kind of BAF combined stuffing and application
CN108658377B (en) Full-submerged sewage treatment method capable of simultaneously removing nitrogen and phosphorus
Dong et al. Nitrification characteristics of nitrobacteria immobilized in waterborne polyurethane in wastewater of corn-based ethanol fuel production
JP6621342B2 (en) Method for producing biological activated carbon to which nitrifying bacteria are attached and advanced water purification method
JP4856610B2 (en) Method for producing molded article for water purification
CA2348520C (en) Nitrification process
JP2022087164A (en) Microbial immobilization carrier
CN104098173A (en) Biological aerated filter provided with suspended bed
CN108249564B (en) Preparation method and use method of denitrification solid carbon source
CN201785245U (en) Compound biological packing and bioreactor thereof
Elmitwalli et al. Treatment of domestic sewage at low temperature in a two-anaerobic step system followed by a trickling filter
CN108017227A (en) A kind of charcoal filtration system and its method for operation for high-nitrogen waste water processing
CN108423797B (en) Treatment of Organic Wastewater filler
Lawal et al. Assessment of a submerged membrane bioreactor with composite ceramic filters for cassava wastewater treatment.
CN210030315U (en) Aquaculture sewage treatment equipment
CN113336329A (en) Granular biochar, preparation method thereof and application thereof in anaerobic digestion for methane production
Zhao et al. Enhancing the nitrogen removal from swine wastewater digested liquid in a trickling biofilter with a soil layer
CN112320949A (en) Nitrification-denitrification coupling biological membrane system for slowly releasing organic carbon source
JP3141250U (en) Water purification material
JP2007117967A (en) Carrier for autotrophic ammonia oxidizing bacterium, ammonia nitrogen removing bacterium-deposited body and method for removing ammonia nitrogen
CN113121080A (en) Biostimulation sediment repairing agent and preparation method thereof
CN109486697B (en) Bacillus licheniformis, preparation thereof and method for treating wastewater
KR100653950B1 (en) Water treatment using porous carriers spported microorganism

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20101013

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20110615

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20110712

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20110802

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20110823

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20110906

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20110928

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20111028

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20141104

Year of fee payment: 3

R150 Certificate of patent or registration of utility model

Ref document number: 4856610

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees