JPWO2012137752A1 - Organic substance adsorbent and organic substance adsorbent carrier containing the organic substance adsorbent - Google Patents

Organic substance adsorbent and organic substance adsorbent carrier containing the organic substance adsorbent Download PDF

Info

Publication number
JPWO2012137752A1
JPWO2012137752A1 JP2012516428A JP2012516428A JPWO2012137752A1 JP WO2012137752 A1 JPWO2012137752 A1 JP WO2012137752A1 JP 2012516428 A JP2012516428 A JP 2012516428A JP 2012516428 A JP2012516428 A JP 2012516428A JP WO2012137752 A1 JPWO2012137752 A1 JP WO2012137752A1
Authority
JP
Japan
Prior art keywords
organic
water
soluble polymer
organic substance
adsorbent
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP2012516428A
Other languages
Japanese (ja)
Other versions
JP5952187B2 (en
Inventor
安田 公昭
公昭 安田
大井 隆志
隆志 大井
吉田 隆
吉田  隆
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.)
Nagoya University NUC
Achilles Corp
Tokai National Higher Education and Research System NUC
Original Assignee
Nagoya University NUC
Achilles Corp
Tokai National Higher Education and Research System NUC
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 Nagoya University NUC, Achilles Corp, Tokai National Higher Education and Research System NUC filed Critical Nagoya University NUC
Publication of JPWO2012137752A1 publication Critical patent/JPWO2012137752A1/en
Application granted granted Critical
Publication of JP5952187B2 publication Critical patent/JP5952187B2/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/14Diatomaceous earth
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/26Synthetic macromolecular compounds
    • B01J20/265Synthetic macromolecular compounds modified or post-treated polymers
    • B01J20/267Cross-linked polymers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3202Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the carrier, support or substrate used for impregnation or coating
    • B01J20/3204Inorganic carriers, supports or substrates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • B01J20/3242Layers with a functional group, e.g. an affinity material, a ligand, a reactant or a complexing group
    • B01J20/3268Macromolecular compounds
    • B01J20/3272Polymers obtained by reactions otherwise than involving only carbon to carbon unsaturated bonds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • B01J20/3242Layers with a functional group, e.g. an affinity material, a ligand, a reactant or a complexing group
    • B01J20/3268Macromolecular compounds
    • B01J20/328Polymers on the carrier being further modified
    • B01J20/3282Crosslinked polymers
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N11/00Carrier-bound or immobilised enzymes; Carrier-bound or immobilised microbial cells; Preparation thereof
    • C12N11/02Enzymes or microbial cells immobilised on or in an organic carrier
    • C12N11/08Enzymes or microbial cells immobilised on or in an organic carrier the carrier being a synthetic polymer
    • C12N11/089Enzymes or microbial cells immobilised on or in an organic carrier the carrier being a synthetic polymer obtained otherwise than by reactions only involving carbon-to-carbon unsaturated bonds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/46Materials comprising a mixture of inorganic and organic materials

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Zoology (AREA)
  • Genetics & Genomics (AREA)
  • Health & Medical Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Wood Science & Technology (AREA)
  • Biotechnology (AREA)
  • Microbiology (AREA)
  • Biomedical Technology (AREA)
  • Inorganic Chemistry (AREA)
  • Biochemistry (AREA)
  • General Engineering & Computer Science (AREA)
  • General Health & Medical Sciences (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

耐久性および有機物吸着性に優れ、かつ、その用途を様々な分野に応用可能な有機物吸着材および有機物吸着体を含有してなる有機物吸着性担体を提供すること。本発明は、有機物を吸着するためのカチオン性の水溶性ポリマーと、架橋剤と、粉粒状態の珪藻土と、からなり、前記珪藻土中に、前記水溶性ポリマーの架橋体が埋入された状態で担持されてなる有機物吸着材を提供する。この有機物吸着材を合成樹脂中に含有させてなる有機物吸着性担体は、水溶性ポリマーが剥離して吸着性が低下するという従来の問題を解決することができ、耐久性および有機物吸着性が非常に優れる。To provide an organic substance adsorbing carrier comprising an organic substance adsorbing material and an organic substance adsorbing body, which are excellent in durability and organic substance adsorbing properties and can be used in various fields. The present invention comprises a cationic water-soluble polymer for adsorbing organic matter, a cross-linking agent, and a diatomaceous earth in a granular state, wherein the water-soluble polymer cross-linked body is embedded in the diatomaceous earth. An organic material adsorbent supported on the substrate is provided. The organic adsorbent carrier made by including this organic adsorbent in the synthetic resin can solve the conventional problem that the water-soluble polymer is peeled and the adsorbability is lowered, and the durability and the organic adsorbability are extremely high. Excellent.

Description

本発明は、有機物吸着材に関する。より詳しくは、新規な構造を有する有機物吸着材およびこれを含有してなる有機物吸着性担体に関する。   The present invention relates to an organic material adsorbent. More specifically, the present invention relates to an organic substance adsorbing material having a novel structure and an organic substance adsorbing carrier containing the same.

水処理分野、農学分野、バイオサイエンス分野、医療分野など、様々な分野で有機物に対して吸着性を有する製品が汎用されている。例えば、微生物などを吸着する製品は水処理分野で、微生物、細菌、ウイルス、花粉、ダストなどを吸着する製品は医療分野で、その他有機物などを吸着する製品は農学分野やバイオサイエンス分野などで多く用いられている。   Products having adsorptivity to organic substances are widely used in various fields such as water treatment field, agricultural field, bioscience field, and medical field. For example, products that adsorb microorganisms are in the water treatment field, products that adsorb microorganisms, bacteria, viruses, pollen, dust, etc. are in the medical field, and many other products that adsorb organic substances are in the agricultural and bioscience fields. It is used.

このような有機物吸着性を有する製品の一例として、水処理分野で用いられている微生物吸着性担体について以下説明する。   As an example of such an organic substance-adsorbing product, a microorganism-adsorbing carrier used in the water treatment field will be described below.

排水処理の分野では、微生物の吸着性能が高い、すなわち排水処理効率が高い排水処理用担体として、表面に微生物吸着性を有する物質が修飾された担体が広く用いられている。例えば、従来から、セルロース製ポリエチレンイミン多孔体が用いられている。この多孔体は、微生物の吸着速度・吸着密度を高めるために、セルロース製の多孔体の表面にポリエチレンイミンが結合された構造を呈している。ポリエチレンイミンはセルロースの持つ水酸基を化学修飾して、架橋剤を介して多孔体に共有結合されている。   In the field of wastewater treatment, a carrier having a surface modified with a substance having a microorganism-adsorbing property is widely used as a wastewater treatment carrier having high microorganism adsorption performance, that is, high wastewater treatment efficiency. For example, conventionally, a polyethylene imine porous body made of cellulose has been used. This porous body has a structure in which polyethyleneimine is bonded to the surface of a porous body made of cellulose in order to increase the adsorption rate and density of microorganisms. Polyethyleneimine is chemically bonded to the hydroxyl group of cellulose and covalently bonded to the porous body via a crosslinking agent.

1級、2級、3級のアミノ基を持つポリエチレンイミンは、高度に枝分かれした樹脂状構造を持つ水溶性ポリマーであり、最もカチオン化密度が高い物質である。そのため、細胞膜が負に荷電している微生物などの有機物を高密度に吸着できる。その結果、ポリエチレンイミンを結合したセルロース製の多孔体は、微生物の吸着速度が高く、微生物の吸着密度が高く、さらに吸着した微生物は剥離しにくいなどの種々の特徴を有している。   Polyethyleneimine having primary, secondary, and tertiary amino groups is a water-soluble polymer having a highly branched resinous structure, and has the highest cationization density. Therefore, organic substances such as microorganisms whose cell membrane is negatively charged can be adsorbed at high density. As a result, the porous body made of cellulose combined with polyethyleneimine has various characteristics such as a high adsorption rate of microorganisms, a high adsorption density of microorganisms, and further, the adsorbed microorganisms are difficult to peel off.

しかしながら、セルロース製の多孔体は微生物の生産する酵素により生物分解を受けるので、排水処理槽の中で長期間使用すると少しずつ減耗して、最終的には消滅してしまうという問題がある。セルロースに架橋処理を施すことによって寿命を延ばす事もできるが、完全に生物分解を抑制することは困難である。よって、現在市販されているセルロース製のポリエチレンイミン多孔体を排水処理用の担体として使用した場合は、一定の期間が経過した後、新たに同じ担体を補充する必要があり、排水処理設備の管理も煩雑になり、また補充する担体のコストも勘案しなければならない。このため、より耐久性の高い担体が求められている。   However, since the porous body made of cellulose undergoes biodegradation by enzymes produced by microorganisms, there is a problem that when it is used in a wastewater treatment tank for a long period of time, it gradually wears down and eventually disappears. Although it is possible to extend the lifetime by subjecting cellulose to a crosslinking treatment, it is difficult to completely suppress biodegradation. Therefore, when a polyethylene imine porous body made of cellulose currently on the market is used as a carrier for wastewater treatment, it is necessary to replenish the same carrier after a certain period of time, and management of wastewater treatment equipment And the cost of the carrier to be replenished must be taken into consideration. For this reason, a carrier having higher durability is demanded.

また、担体素材となるセルロース製多孔体は製造工程が複雑なために、製造原価が高く、そのセルロース製多孔体にポリエチレンイミンを結合した製品としての担体も必然的に高価となるといった問題があった。   In addition, the cellulose porous body used as a carrier material has a complicated manufacturing process, so the manufacturing cost is high, and the carrier as a product in which polyethyleneimine is bonded to the cellulose porous body is inevitably expensive. It was.

一方、同じように排水処理用の担体として用いられている合成樹脂製の多孔体は、セルロース製多孔体より安価で、生物分解を受けないため減耗することがないという二つの利点があるが、セルロース製ポリエチレンイミン多孔体と比べて微生物の吸着性能は劣るという問題があった。   On the other hand, a porous body made of a synthetic resin that is also used as a carrier for wastewater treatment is cheaper than a porous body made of cellulose, and has two advantages that it does not undergo biodegradation and does not wear out. There was a problem that the adsorption performance of microorganisms was inferior compared with the polyethyleneimine porous body made of cellulose.

そこで、本発明者らは、担体の表面に樹脂化させたポリエチレンイミンの薄い皮膜を形成した微生物固定化担体を発明した(特許文献1)。   Accordingly, the present inventors have invented a microorganism-immobilized carrier in which a thin film of polyethyleneimine resinized on the surface of the carrier is formed (Patent Document 1).

この特許文献1で開示された微生物吸着性担体は、従来のセルロース製ポリエチレンイミン多孔体と比べて耐久性に優れ、また、安価に製造することができるといった利点があり、さらに従来の合成樹脂製の多孔体と比べて微生物吸着能に優れるものである。   The microorganism-adsorbing carrier disclosed in Patent Document 1 has advantages that it is superior in durability and can be manufactured at a low cost compared to a conventional polyethylene imine porous body made of cellulose, and is made of a conventional synthetic resin. Compared to other porous bodies, it is excellent in microbial adsorption ability.

しかし、活性基を有さない樹脂、例えばポリエチレンなどを担体素材として用いた場合、ポリエチレンイミンの皮膜が剥離し易いという弱点があった。   However, when a resin having no active group, such as polyethylene, is used as a carrier material, there is a weak point that the polyethyleneimine film is easily peeled off.

一方、ヒドロキシ基を有するウレタンなどを担体素材として用いた場合、ポリエチレンイミンの皮膜は剥離し難いが、ウレタン自体が次亜塩素酸などの酸化物や紫外線などで一部が分解され脆弱化し、その寿命が5年程度であるという弱点があった。   On the other hand, when urethane having a hydroxyl group or the like is used as a carrier material, the polyethyleneimine film is difficult to peel off, but urethane itself is partially decomposed and weakened by oxides such as hypochlorous acid and ultraviolet rays. There was a weak point that the lifetime was about 5 years.

また、微生物吸着担体以外の用途に、特許文献1で開示された技術を利用したとしても、微生物吸着性担体と同様に、ポリエチレンイミンが表面を被覆した状態であるために耐久性の乏しく、実用的なものではなかった。   Moreover, even if the technique disclosed in Patent Document 1 is used for applications other than the microorganism-adsorbing carrier, the surface is covered with polyethyleneimine as in the case of the microorganism-adsorbing carrier, so that the durability is poor and practical use is not possible. It was n’t.

特開2001−128674号公報Japanese Patent Laid-Open No. 2001-128674

本発明は、耐久性および有機物吸着性に優れ、かつ、その用途を様々な分野に応用可能な有機物吸着材および該有機物吸着材を含有してなる有機物吸着性担体を提供することを主目的とする。   The main object of the present invention is to provide an organic adsorbent that is excellent in durability and organic adsorbability and that can be used in various fields, and an organic adsorbent carrier containing the organic adsorbent. To do.

そこで、本発明者らは、前記課題を解決するために鋭意研究した結果、微生物吸着性担体等の有機物吸着性担体の表面を有機物吸着材でコーティングするといった従来技術から発想を転換し、カチオン性の水溶性ポリマーを含有する特定の有機物吸着材を検討し、有機物吸着性担体等を構成する合成樹脂性成形体に前記有機物吸着材を含有させることを検討し、本発明を完成させるに至った。   Therefore, as a result of diligent research to solve the above-mentioned problems, the present inventors changed the idea from the conventional technique of coating the surface of an organic substance-adsorbing carrier such as a microorganism-adsorbing carrier with an organic substance-adsorbing material. The present inventors have studied a specific organic adsorbent containing a water-soluble polymer, and have studied the inclusion of the organic adsorbent in a synthetic resin-based molded article constituting an organic adsorbent carrier, etc., leading to the completion of the present invention. .

本発明は、まず、有機物を吸着するためのカチオン性の水溶性ポリマーと、
架橋剤と、
粉粒状態の珪藻土と、からなり、
前記珪藻土中に、前記水溶性ポリマーの架橋体が埋入された状態で担持されてなる有機物吸着材を提供する。
本発明では、粉粒状態の珪藻土を採用し、有機物を吸着する特定の水溶性ポリマー架橋体を、前記珪藻土中に埋入された状態で担持させることにより、新規な構造の有機物吸着材を製造することに成功した。
本発明に係る有機物吸着材において用いることができる前記水溶性ポリマーは、本発明の効果を損なわない限りその種類は特に限定されないが、アミノ基を備える水溶性ポリマーを用いることが好ましい。この場合、アミノ基を備える水溶性ポリマーとしては、ポリエチレンイミンを採用することが好ましい。
また、本発明に係る有機物吸着材において用いることができる前記架橋剤は、本発明の効果を損なわない限りその種類は特に限定されないが、エポキシ誘導体を用いることが好ましい。この場合、前記エポキシ誘導体としては、高分子体のものが好ましく、ポリグリセロールポリグリシジルエーテルを採用することが好ましい。
本発明に係る有機物吸着材において、前記水溶性ポリマーと前記架橋剤との配合割合は、本発明の効果を損なわない限りその種類は特に限定されず、自由に設定することが可能であるが、本発明では特に、前記水溶性ポリマーと前記架橋剤との配合割合を重量比で1〜10:1とすることが好ましい。
The present invention first comprises a cationic water-soluble polymer for adsorbing organic matter,
A crosslinking agent;
It consists of diatomaceous earth in powder form,
Provided is an organic substance adsorbent which is supported in a state where a crosslinked body of the water-soluble polymer is embedded in the diatomaceous earth.
In the present invention, a powdery diatomaceous earth is adopted, and a specific water-soluble polymer crosslinked body that adsorbs organic matter is supported while embedded in the diatomaceous earth to produce an organic matter adsorbent having a novel structure. Succeeded in doing.
The type of the water-soluble polymer that can be used in the organic adsorbent according to the present invention is not particularly limited as long as the effects of the present invention are not impaired, but a water-soluble polymer having an amino group is preferably used. In this case, it is preferable to employ polyethyleneimine as the water-soluble polymer having an amino group.
The type of the crosslinking agent that can be used in the organic adsorbent according to the present invention is not particularly limited as long as the effects of the present invention are not impaired, but an epoxy derivative is preferably used. In this case, the epoxy derivative is preferably a polymer, and polyglycerol polyglycidyl ether is preferably employed.
In the organic adsorbent according to the present invention, the mixing ratio of the water-soluble polymer and the crosslinking agent is not particularly limited as long as the effect of the present invention is not impaired, and can be freely set. In the present invention, it is particularly preferable that the mixing ratio of the water-soluble polymer and the crosslinking agent is 1 to 10: 1 by weight.

本発明に係る有機物吸着材を合成樹脂中に含有させることで、合成樹脂の表面のみならず合成樹脂中に前記水溶性ポリマー架橋体を埋入した状態の新規な有機物吸着性担体を提供することができる。   By providing the organic material adsorbent according to the present invention in a synthetic resin, a novel organic material-adsorbing carrier in which the crosslinked water-soluble polymer is embedded in the synthetic resin as well as the surface of the synthetic resin is provided. Can do.

ここで、本発明において用いられる技術用語について、以下に説明する。
本発明において、「有機物吸着材」とは、有機体すなわち動植物体を構成しているあらゆる物質に吸着性を有するものであり、例えば、微生物、細菌、ウイルス、花粉、ダストなどを吸着するものも本発明において「有機物吸着材」に包含される。
Here, technical terms used in the present invention will be described below.
In the present invention, the “organic substance adsorbent” is an adsorbent to all substances constituting an organic body, that is, an animal or plant body. For example, those adsorbing microorganisms, bacteria, viruses, pollen, dust, etc. In the present invention, it is included in the “organic adsorbent”.

本発明によれば、耐久性および有機物吸着性に優れ、かつ、その用途を様々な分野に応用可能な有機物吸着材を提供することができる。また、本発明の有機物吸着材を合成樹脂中に含有してなる有機物吸着性担体は、有機物吸着材が脱落することはなく、長期に亘って使用可能である。   ADVANTAGE OF THE INVENTION According to this invention, it is excellent in durability and organic substance adsorption | suction, and can provide the organic substance adsorbent which can apply the use to various fields. Moreover, the organic substance adsorbent carrier comprising the organic substance adsorbent of the present invention in a synthetic resin can be used for a long period of time without the organic substance adsorbent falling off.

以下、本発明を実施するための好適な形態について説明する。なお、以下に説明する実施形態は、本発明の代表的な実施形態の一例を示したものであり、これにより本発明の範囲が限定解釈されるものではない。   Hereinafter, preferred embodiments for carrying out the present invention will be described. In addition, embodiment described below shows an example of typical embodiment of this invention, and, thereby, the scope of the present invention is not limitedly interpreted.

1.有機物吸着材
本発明に係る有機物吸着材は、水溶性ポリマーと、架橋剤と、珪藻土と、からなる有機物吸着材であり、前記珪藻土中に、前記水溶性ポリマーの架橋体を埋入した状態で担持した構造を呈することを特徴とする。
なお、本発明に係る有機物吸着体は、前記珪藻土中に、前記水溶性ポリマー架橋体が少なくとも埋入された状態で担持されていればよく、例えば、水溶性ポリマー架橋体が、前記珪藻土中に埋入され且つ前記珪藻土の表面に被覆された状態で担持されたものも、本発明の有機物吸着体に含まれる。
1. Organic substance adsorbent The organic substance adsorbent according to the present invention is an organic substance adsorbent composed of a water-soluble polymer, a cross-linking agent, and diatomaceous earth, and in a state where a cross-linked body of the water-soluble polymer is embedded in the diatomaceous earth. It is characterized by exhibiting a supported structure.
In addition, the organic substance adsorbent according to the present invention is only required to be supported in the diatomaceous earth in a state where the water-soluble polymer crosslinked body is at least embedded, for example, the water-soluble polymer crosslinked body is contained in the diatomaceous earth. Those embedded and supported on the surface of the diatomaceous earth are also included in the organic matter adsorbent of the present invention.

本発明に係る有機物吸着材では、有機物を吸着するために、カチオン性の水溶性ポリマーを用いる。本発明の有機物吸着材に用いることができるカチオン性の水溶性ポリマーは、本発明の効果を損なわない限りその種類は特に限定されず、既存の有機物吸着材に用いることが可能で、使用される架橋剤に対して反応する官能基を有するものであれば、あらゆる種類の水溶性ポリマーを用いることができる。特に本発明においては、カチオン化密度が高い物質が好ましく、カチオン化密度の高い物質の一例として、アミノ基を備える水溶性ポリマーを用いることが好ましい。   In the organic adsorbent according to the present invention, a cationic water-soluble polymer is used to adsorb organic substances. The cationic water-soluble polymer that can be used in the organic adsorbent of the present invention is not particularly limited as long as the effects of the present invention are not impaired, and can be used in an existing organic adsorbent. Any type of water-soluble polymer can be used as long as it has a functional group that reacts with the crosslinking agent. In particular, in the present invention, a substance having a high cationization density is preferable, and a water-soluble polymer having an amino group is preferably used as an example of a substance having a high cationization density.

アミノ基を有する水溶性ポリマーとしては、アルキレンイミンポリマー(例えば、ポリエチレンイミン)、ポリアクリルアミド、ポリアミノ酸(例えば、ポリリジン、ポリアルギニン)を用いることが可能である。この中でも特に、本発明においては、ポリエチレンイミンを採用することが好ましい。   As the water-soluble polymer having an amino group, an alkyleneimine polymer (for example, polyethyleneimine), polyacrylamide, or polyamino acid (for example, polylysine or polyarginine) can be used. Among these, it is particularly preferable to employ polyethyleneimine in the present invention.

本発明の有機物吸着材において用いることが好ましいポリエチレンイミンには、線状構造を有するもののみならず分岐構造を有するものも広く含まれる。特に本発明においては、1級、2級、および3級アミンを含む分岐構造を有するポリエチレンイミンが好ましい。このようなポリエチレンイミンは、例えば、エチレンイミンを酸触媒の存在下、開環重合させることにより合成することができる。   The polyethyleneimine that is preferably used in the organic material adsorbent of the present invention includes not only those having a linear structure but also those having a branched structure. Particularly in the present invention, polyethyleneimine having a branched structure containing primary, secondary and tertiary amines is preferred. Such polyethyleneimine can be synthesized, for example, by ring-opening polymerization of ethyleneimine in the presence of an acid catalyst.

本発明に係る有機物吸着材において、架橋剤は、前記水溶性ポリマーを架橋するために用いる。本発明の有機物吸着材に用いることができる架橋剤は、前記水溶性ポリマーが有する官能基と反応して架橋することができ、かつ、後述する本発明の有機物吸着材の効果を損なわない限りその種類は特に限定されず、既存の有機物吸着材に用いることが可能なあらゆる種類の架橋剤を用いることができる。例えば、前記水溶性ポリマーとしてアミノ基を有する水溶性ポリマーを用いる場合、アミノ基と反応性のある架橋剤を用いることで、アミノ基を介して水溶性ポリマーを互いに架橋することにより不溶化することができる。   In the organic adsorbent according to the present invention, the crosslinking agent is used for crosslinking the water-soluble polymer. The crosslinking agent that can be used in the organic adsorbent of the present invention can be cross-linked by reacting with the functional group of the water-soluble polymer and does not impair the effects of the organic adsorbent of the present invention described later. The type is not particularly limited, and any type of crosslinking agent that can be used for existing organic adsorbents can be used. For example, when a water-soluble polymer having an amino group is used as the water-soluble polymer, the water-soluble polymer can be insolubilized by cross-linking each other through the amino group by using a crosslinking agent that is reactive with the amino group. it can.

本発明で用いることができるアミノ基と反応性のある架橋剤の種類は、特に限定されないが、例えば、一以上の官能性のエポキシ基を有するエポキシ誘導体を挙げることができる。本発明では特に、二つ以上のエポキシ基を有するエポキシ誘導体が好ましい。   The kind of the crosslinking agent that is reactive with an amino group that can be used in the present invention is not particularly limited, and examples thereof include an epoxy derivative having one or more functional epoxy groups. In the present invention, an epoxy derivative having two or more epoxy groups is particularly preferable.

本発明で用いることができるエポキシ誘導体としては、例えば、エチレングリコールジグリシジルエーテル、グリセロールジグリシジルエーテル、グリシドール、グリセロールポリグリシジルエーテル、ポリグリセロールポリグリシジルエーテル、ポリエチレングリコールジグリシジルエーテル、ポリプロピレングリコールジグリシジルエーテル、ソルビトールポリグリシジルエーテル、ソルビタンジグリシジルエーテルを挙げることができる。この中でも、本発明においては特に、ポリグリセロールポリグリシジルエーテルを採用することが好ましい。   Examples of the epoxy derivative that can be used in the present invention include ethylene glycol diglycidyl ether, glycerol diglycidyl ether, glycidol, glycerol polyglycidyl ether, polyglycerol polyglycidyl ether, polyethylene glycol diglycidyl ether, polypropylene glycol diglycidyl ether, Examples include sorbitol polyglycidyl ether and sorbitan diglycidyl ether. Among these, in the present invention, it is particularly preferable to employ polyglycerol polyglycidyl ether.

水溶性ポリマーと架橋剤の混合割合は特に限定されず、有機物吸着材の使用用途や、用いる水溶性ポリマーや架橋剤の種類などに応じて適宜設定することが可能である。本発明では特に、水溶性ポリマーと架橋剤とを、1〜10:1の重量比で混合することが好ましく、1〜5:1であることがさらに好ましい。架橋剤1に対し、水溶性ポリマーの配合割合を重量比で1以上とすることで、水溶性ポリマーが架橋された後においても有機物を吸着するための官能基をより多く残存させることができ、有機物吸着性を高めることができる。また、架橋剤1に対し、水溶性ポリマーの配合割合を重量比で10以下とすることで、架橋されない水溶性ポリマーの量を最小限に抑えることができ、例えば、水中において有機物吸着材を用いる際などに、水中に水溶性ポリマーが溶出して有機物吸着性が低減してしまうのを防ぐことができる。   The mixing ratio of the water-soluble polymer and the crosslinking agent is not particularly limited, and can be set as appropriate according to the intended use of the organic adsorbent, the type of the water-soluble polymer and the crosslinking agent used, and the like. In the present invention, the water-soluble polymer and the crosslinking agent are particularly preferably mixed at a weight ratio of 1 to 10: 1, and more preferably 1 to 5: 1. By setting the blending ratio of the water-soluble polymer to 1 or more in the weight ratio with respect to the crosslinking agent 1, more functional groups for adsorbing organic substances can be left even after the water-soluble polymer is crosslinked, Organic matter adsorption property can be improved. Moreover, the amount of the water-soluble polymer that is not crosslinked can be minimized by setting the blending ratio of the water-soluble polymer to 10 or less by weight with respect to the crosslinking agent 1. For example, an organic adsorbent is used in water. At this time, it is possible to prevent the water-soluble polymer from being eluted in water and reducing the organic matter adsorptivity.

本発明においては、前記水溶性ポリマーと前記架橋剤の担持体として、珪藻土を用いる。珪藻土を用いない場合、前記水溶性ポリマー架橋体のみでは微粉砕することが難しいため、様々な用途に応用することが困難である。しかし、本発明のように担持体として珪藻土を用いることで、例えば、有機物吸着材を粉砕することなども可能となり、様々な用途へ応用することが可能となる。   In the present invention, diatomaceous earth is used as a carrier for the water-soluble polymer and the crosslinking agent. When diatomaceous earth is not used, since it is difficult to pulverize only with the water-soluble polymer crosslinked body, it is difficult to apply to various uses. However, by using diatomaceous earth as the carrier as in the present invention, for example, it is possible to pulverize the organic substance adsorbing material, and it can be applied to various uses.

珪藻土は、二酸化ケイ素を主成分としてなる無機多孔質体であり、水分や油分等を大量に保持することができる。無機多孔質体としては、珪藻土の他、炭酸カルシウム、ゼオライト、セピオライト、酸化アルミニウム、シリカ等があるが、孔の大きさによっては前記水溶性ポリマー架橋体を埋入させることができない場合があり、また、その用途が限定されてしまう場合がある。そこで、本発明においては、前記水溶性ポリマーと前記架橋剤の担持性およびその用途が様々な分野に応用可能であることから珪藻土を採用した。   Diatomaceous earth is an inorganic porous body mainly composed of silicon dioxide, and can retain a large amount of moisture, oil, and the like. In addition to diatomaceous earth, inorganic porous bodies include calcium carbonate, zeolite, sepiolite, aluminum oxide, silica, etc., but depending on the size of the pores, the water-soluble polymer crosslinked body may not be embedded, Moreover, the use may be limited. Therefore, in the present invention, diatomaceous earth was adopted because the supportability of the water-soluble polymer and the crosslinking agent and the use thereof can be applied to various fields.

珪藻土は、また、化学的に安定物質であり、耐熱性に優れており、珪殻の多孔性と独特の形状とにより、極めて嵩高い粉体である。そのため、この珪藻土の細孔に、有機物を吸着するための前記水溶性ポリマーと架橋剤との反応物質が入り込み、本発明の有機物吸着材の耐熱性を高めることができ、耐久性の向上につながる。   Diatomaceous earth is also a chemically stable substance, has excellent heat resistance, and is a very bulky powder due to the porosity and unique shape of the silicate shell. Therefore, the reaction material of the water-soluble polymer and the crosslinking agent for adsorbing the organic matter enters the pores of the diatomaceous earth, and the heat resistance of the organic matter adsorbing material of the present invention can be increased, leading to improved durability. .

このように、本発明に係る有機物吸着材は、従来のものに比べて耐熱性が非常に高いため、有機物吸着材を様々な分野の製品に応用する場合、その製造工程において、前記水溶性ポリマーの有機物吸着性が熱により失活するのを防ぐことも可能である。例えば、後述する有機物吸着性担体には合成樹脂が用いられるが、本発明に係る有機物吸着材を用いることで、比較的高い融点を持つ合成樹脂まで選択することが可能となる。   As described above, the organic adsorbent according to the present invention has a very high heat resistance as compared with the conventional one. Therefore, when the organic adsorbent is applied to products in various fields, the water-soluble polymer is used in the production process. It is also possible to prevent the organic matter adsorptivity from being deactivated by heat. For example, although a synthetic resin is used for the organic substance-adsorbing carrier described later, it is possible to select a synthetic resin having a relatively high melting point by using the organic substance-adsorbing material according to the present invention.

本発明に係る有機物吸着材に用いる珪藻土は、粉粒状態のものを用いる。本発明で用いることが可能な珪藻土は、粉粒状態であれば、その粒径は特に限定されず、前記水溶性ポリマー架橋体を担持することができ、かつ、本発明の効果を損なわない限り、様々な粒径の珪藻土を用いることができるが、本発明では特に、レーザー回析法によって測定される平均粒径が3μm以上50μm以下の珪藻土を採用することが好ましい。粒径が3μm未満の珪藻土は、前記水溶性ポリマー架橋体を担持するための細孔が充分に確保されない可能性があり、粒径が50μmを超える珪藻土は、様々な分野の製品に応用する場合に扱い難い場合があるため、前記水溶性ポリマー架橋体を担持するのに十分な多孔質の状態が維持され、かつ、様々な分野の製品への応用がし易いといった観点から、粒径が5μm以上30μm以下の珪藻土を採用することがさらに好ましい。   The diatomaceous earth used for the organic material adsorbent according to the present invention is in a granular state. The diatomaceous earth that can be used in the present invention is not particularly limited as long as it is in a granular state, as long as the water-soluble polymer crosslinked body can be supported and the effects of the present invention are not impaired. In the present invention, it is particularly preferable to use diatomaceous earth having an average particle diameter measured by a laser diffraction method of 3 μm or more and 50 μm or less. Diatomaceous earth with a particle size of less than 3 μm may not have sufficient pores to support the water-soluble polymer crosslinked body, and diatomaceous earth with a particle size of more than 50 μm is applied to products in various fields. From the viewpoint of maintaining a porous state sufficient to support the water-soluble polymer crosslinked product and being easily applicable to products in various fields, the particle size is 5 μm. More preferably, diatomaceous earth of 30 μm or less is employed.

本発明において、水溶性ポリマーおよび架橋剤が珪藻土の細孔に入り込むように担持させることができれば、両者の混合割合は特に限定されず、用いる水溶性ポリマーや架橋剤の種類などに応じて自由に設定することが可能である。本発明においては特に、前記水溶性ポリマーと前記架橋剤の反応物と、前記珪藻土とを、1:1〜15の重量比で配合することが好ましい。上記配合割合にすることで、珪藻土の細孔内に有効に水溶性ポリマーと架橋剤の反応物を取り込むことができ、後述の混合・混練、乾燥固化、粉砕処理工程に支障をきたすことがない。   In the present invention, as long as the water-soluble polymer and the crosslinking agent can be supported so as to enter the pores of diatomaceous earth, the mixing ratio of both is not particularly limited, and can be freely selected depending on the type of the water-soluble polymer and the crosslinking agent used. It is possible to set. In the present invention, it is particularly preferable to blend the water-soluble polymer, the reaction product of the crosslinking agent, and the diatomaceous earth in a weight ratio of 1: 1 to 15. By using the above blending ratio, the reaction product of the water-soluble polymer and the crosslinking agent can be effectively taken into the pores of the diatomaceous earth, and there will be no hindrance to the mixing / kneading, drying and solidification, and pulverization processing steps described later. .

このような有機物吸着材は、水と水溶性ポリマーと架橋剤および珪藻土を混合・混練し、乾燥固化することで得られる。乾燥固化方法や有機物吸着材の使用用途に応じて、乾燥固化後に粉砕処理することによって有機物吸着材の粒径を調整してもよい。   Such an organic adsorbent can be obtained by mixing and kneading water, a water-soluble polymer, a crosslinking agent and diatomaceous earth, and then drying and solidifying the mixture. Depending on the drying and solidification method and the intended use of the organic material adsorbent, the particle size of the organic material adsorbent may be adjusted by pulverization after the solidification.

上記のようにして得られる有機物吸着材は、有機物吸着性を有する水溶性ポリマーの担持が強固であり、種々の有機物吸着性担体に含有させて使用することが可能である。   The organic adsorbent obtained as described above has a strong support of a water-soluble polymer having organic adsorbability, and can be used by being contained in various organic adsorbent carriers.

2.有機物吸着性担体
本発明に係る有機物吸着性担体は、前述した有機物吸着材を合成樹脂中に含有させて、使用する用途に適した形状に成形されたものである。本発明に係る有機物吸着性担体は、合成樹脂中に有機物吸着材を含有させてなることにより、樹脂の表面のみならず内部にまで前記有機物吸着材が埋入されている。そのため、本発明に係る有機物吸着性担体は、水溶性ポリマーが剥離して吸着性が低下するという従来の問題を解決することができ、耐久性および有機物吸着性が非常に優れる。
2. Organic substance-adsorbing carrier The organic substance-adsorbing carrier according to the present invention is one in which the organic substance adsorbing material described above is contained in a synthetic resin and formed into a shape suitable for the intended use. The organic substance adsorbing carrier according to the present invention includes an organic substance adsorbing material in a synthetic resin, so that the organic substance adsorbing material is embedded not only on the surface of the resin but also inside. Therefore, the organic matter adsorptive carrier according to the present invention can solve the conventional problem that the water-soluble polymer is peeled and the adsorptivity is lowered, and the durability and the organic matter adsorptivity are very excellent.

また、用いる樹脂素材や形状などが特に限定されないため、有機物吸着性担体の使用用途に適した樹脂を選定することが可能となり、有機物吸着性担体の耐久性を更に高めることも可能である。   In addition, since the resin material and shape to be used are not particularly limited, it is possible to select a resin suitable for the intended use of the organic matter adsorbing carrier, and it is possible to further enhance the durability of the organic matter adsorbing carrier.

本発明の有機物吸着性担体に用いることができる合成樹脂は、本発明の効果を損なわない限りその種類は特に限定されないが、具体的には、ポリアクリルアミド、ポリビニルアルコール、エポキシ樹脂、ポリエステル、ポリスチレン、ポリウレタン、ポリプロピレン及びポリエチレンで代表されるポリオレフィン系樹脂が好ましく用いられる。この中でも、特に、酸化剤や紫外線に強く、更に微生物による分解も受けにくいといったことからポリエチレンが好ましく、低密度ポリエチレン、直鎖状低密度ポリエチレンがさらに好ましい。
本発明の有機物吸着材は耐熱性に優れるため、従来の担体に比べて比較的融点の高い樹脂を選択することも可能であるが、低密度ポリエチレン、直鎖状低密度ポリエチレンは、融点が低いため、有機物吸着性担体の成形温度を低く抑えることができ、担体の成形時において、有機物吸着材に含まれる水溶性ポリマーの熱変性をより確実に抑制することができる。
The synthetic resin that can be used in the organic matter-adsorbing carrier of the present invention is not particularly limited as long as the effects of the present invention are not impaired, and specifically, polyacrylamide, polyvinyl alcohol, epoxy resin, polyester, polystyrene, Polyolefin resins represented by polyurethane, polypropylene and polyethylene are preferably used. Among these, polyethylene is preferable because it is particularly resistant to oxidizing agents and ultraviolet rays and is not easily decomposed by microorganisms, and low-density polyethylene and linear low-density polyethylene are more preferable.
Since the organic adsorbent of the present invention is excellent in heat resistance, it is possible to select a resin having a relatively high melting point compared to conventional carriers, but low-density polyethylene and linear low-density polyethylene have a low melting point. Therefore, the molding temperature of the organic substance-adsorbing carrier can be kept low, and thermal denaturation of the water-soluble polymer contained in the organic substance-adsorbing material can be more reliably suppressed during the molding of the carrier.

有機物吸着材の添加量は特に限定されないが、合成樹脂100重量部に対して、有機物吸着材は1〜20重量部含有されていることが好ましい。有機物吸着材を1重量部以上含有させることで、有機物吸着性能をより確実に発現させることができ、20重量部以下とすることで、有機物吸着性担体の機械的性質の低下を防止し、また有機物吸着性担体の重量の増加も防止することができる。   The addition amount of the organic adsorbent is not particularly limited, but it is preferable that the organic adsorbent is contained in an amount of 1 to 20 parts by weight with respect to 100 parts by weight of the synthetic resin. By containing 1 part by weight or more of the organic substance adsorbent, the organic substance adsorption performance can be expressed more reliably, and by setting it to 20 parts by weight or less, the deterioration of the mechanical properties of the organic substance adsorbent carrier is prevented, An increase in the weight of the organic substance-adsorbing carrier can also be prevented.

本発明の有機物吸着性担体は、担体を構成する合成樹脂の全量に有機物吸着材を添加して成形することも可能であるが、オレフィン系樹脂のようなペレット状の樹脂を用いる場合には、予め少量の樹脂に有機物吸着材を添加して有機物吸着材を含有するペレットを作製した上で、当該ペレットを残りの樹脂に分散させて成形する、いわゆるマスターバッチ化して成形することが分散性の点から好適である。   The organic matter adsorptive carrier of the present invention can be molded by adding an organic matter adsorbent to the total amount of the synthetic resin constituting the carrier, but when using a pellet-like resin such as an olefin resin, Dispersibility can be achieved by adding an organic adsorbent to a small amount of resin in advance to produce pellets containing the organic adsorbent, then dispersing the pellets in the remaining resin and forming the so-called master batch. From the point of view, it is preferable.

本発明に係る有機物吸着性担体は、微生物を利用して排水処理を行う際の微生物吸着性担体として好適に用いることができる。微生物吸着性担体は、担体に微生物を固定化し、排水中に含有している有機物を吸着、分解することにより排水の浄化が行われる。
排水処理用等に用いる微生物吸着性担体は、上述の合成樹脂中に有機物吸着体を含有させ、比重が0.98〜1.35g/cmとなるように比重を調整することが好ましい。比重を0.98g/cm以上に調整することで、排水処理槽中に微生物吸着性担体が沈みこみ易く、排水の処理効率を向上させることができる。また、比重を1.35g/cm以下に調整することで、重量が増えて取り扱い難くなることを防ぐことができ、また、微生物吸着性担体が排水処理層の下層の方へ沈み込んでしまうのを防いで、排水の処理効率を向上させることができる。
The organic substance-adsorbing carrier according to the present invention can be suitably used as a microorganism-adsorbing carrier when performing wastewater treatment using microorganisms. The microorganism-adsorbing carrier purifies the wastewater by immobilizing microorganisms on the carrier and adsorbing and decomposing organic substances contained in the wastewater.
The microorganism-adsorbing carrier used for wastewater treatment or the like preferably contains an organic substance adsorbent in the above-mentioned synthetic resin and adjusts the specific gravity so that the specific gravity becomes 0.98 to 1.35 g / cm 3 . By adjusting the specific gravity to 0.98 g / cm 3 or more, the microorganism-adsorbing carrier easily sinks in the wastewater treatment tank, and the wastewater treatment efficiency can be improved. Moreover, by adjusting the specific gravity to 1.35 g / cm 3 or less, it is possible to prevent weight from becoming difficult to handle, and the microorganism-adsorbing carrier sinks toward the lower layer of the wastewater treatment layer. It is possible to improve the wastewater treatment efficiency.

本発明においては、微生物吸着性担体を上記比重にするために比重調整剤を用いることができる。比重調整剤は、本発明の有機物吸着材の効果を損なわない限りその種類は特に限定されず、あらゆる種類の比重調整剤を用いることができる。例えば、タルク、炭酸カルシウム、炭酸マグネシウム、シリカ等を用いることができる。   In the present invention, a specific gravity adjusting agent can be used to make the microorganism-adsorbing carrier have the above specific gravity. The specific gravity adjuster is not particularly limited as long as the effect of the organic adsorbent of the present invention is not impaired, and any type of specific gravity adjuster can be used. For example, talc, calcium carbonate, magnesium carbonate, silica or the like can be used.

微生物吸着性担体の形状は、立方状、直方状、球状、円筒状、など任意の形状や寸法に成形することができ、中空でも中実でも差し支えないが、比較的小さいサイズの方が耐摩耗性に優れる傾向にあるので、3〜20mm角または3〜20mm径程度とすることが好ましい。   The shape of the microorganism-adsorbing carrier can be formed into any shape or size, such as cubic, rectangular, spherical, cylindrical, and can be hollow or solid, but a relatively small size is more resistant to wear. Therefore, it is preferable that the diameter is about 3 to 20 mm square or about 3 to 20 mm in diameter.

また、本発明に係る有機物吸着性担体は、有機物吸着用フィルムとして好適に用いることできる。より具体的には、本発明に係る有機物吸着材を合成樹脂中に含有させてフィルム状に成形することで、有機物吸着用フィルムとして応用することが可能である。この有機物吸着用フィルムは、例えば、排水処理層の固定床用担体などに応用することが可能である。   Moreover, the organic substance adsorptive carrier according to the present invention can be suitably used as an organic substance adsorption film. More specifically, the organic substance adsorbing material according to the present invention can be applied as a film for adsorbing organic substances by containing it in a synthetic resin and forming it into a film shape. This organic matter adsorption film can be applied to, for example, a fixed bed carrier for a wastewater treatment layer.

さらに、本発明に係る有機物吸着性担体は、有機物吸着用不織布、編布、織布として好適に用いることができる。より具体的には、本発明に係る有機物吸着材を合成樹脂中に含有させ繊維化し、この繊維を、熱、機械的もしくは化学的な作用によって接着または絡み合わせることで、有機物吸着用不織布として応用することが可能である。この有機物吸着用不織布は、例えば、医療現場などにおいて、マスク、フィルター、手袋、モップなどの清掃用具などに用いることで、微生物、ウイルス、ダストなどを吸着し、例えば、院内感染の防止などに貢献することが可能である。   Furthermore, the organic matter adsorbing carrier according to the present invention can be suitably used as a nonwoven fabric for organic matter adsorption, a knitted fabric, and a woven fabric. More specifically, the organic substance adsorbing material according to the present invention is contained in a synthetic resin to form a fiber, and this fiber is bonded or entangled by heat, mechanical or chemical action, and applied as an organic substance adsorbing nonwoven fabric. Is possible. This non-woven fabric for adsorbing organic substances can be used for cleaning tools such as masks, filters, gloves, mops, etc. in medical settings, etc., thereby adsorbing microorganisms, viruses, dust, etc., and contributing to prevention of nosocomial infections, for example. Is possible.

以上のように、有機物吸着材は、種々の有機物吸着性担体に含有させて使用することができる。その他にも、有機物吸着材をフィルム、シート、合板等の種々の材に塗布、圧着させることにより、有機物吸着性を付与することも可能である。   As described above, the organic substance adsorbing material can be used by being contained in various organic substance adsorbing carriers. In addition, it is also possible to impart organic matter adsorbing properties by applying an organic matter adsorbing material to various materials such as films, sheets, and plywood and press-bonding them.

以下、実施例に基づいて本発明を更に詳細に説明する。なお、以下に説明する実施例は、本発明の代表的な実施例の一例を示したものであり、これにより本発明の範囲が狭く解釈されることはない。   Hereinafter, the present invention will be described in more detail based on examples. In addition, the Example demonstrated below shows an example of the typical Example of this invention, and, thereby, the range of this invention is not interpreted narrowly.

[実験例1]
実験例1では、本発明に係る有機物吸着材を用いた微生物吸着性担体を製造し、有機物吸着性、耐薬品性、耐光性、耐摩耗性、樹脂への分散性について、それぞれ検討した。
[Experimental Example 1]
In Experimental Example 1, a microorganism-adsorbing carrier using the organic substance adsorbing material according to the present invention was produced, and the organic substance adsorbing property, chemical resistance, light resistance, abrasion resistance, and dispersibility in resin were examined.

<実施例1〜9、比較例1〜6>
実施例1〜9、比較例1〜6については、下記の表1に記載の配合で、有機物吸着材を得た。具体的には、340重量部の水に水溶性ポリマー(ポリエチレンイミン含有水溶液(固形分30%) 製品名「エポミンP−1000」(登録商標)株式会社日本触媒製)を添加した溶液Aと、70重量部の水に架橋剤(ポリグリセロールポリグリシジルエーテル 製品名「デナコールEX−512」(登録商標)ナガセケムテックス株式会社製)を添加した溶液Bを用意し、実施例1〜9および比較例2については珪藻土(レーザー回析法による平均粒子径15μm 製品名「ラヂオライト#300」(登録商標)昭和化学工業株式会社製)、比較例1については炭酸カルシウム(レーザー回析法による平均粒子径1.2μm 製品名「PC−700」白石カルシウム株式会社製)、比較例4についてはタルク(レーザー回析法による平均粒子径1.0μm 日本タルク株式会社製)、比較例5については粘土(製品名「ニッカゲルS」東新化成株式会社製)、比較例6についてはゼオライト(製品名「HSZ−700」東ソー株式会社製)中に溶液Aを添加し、次いで溶液Bを添加して撹拌混合した。その後、混合物の流動体を厚さ50mmとなるように容器に移し、100℃のオーブンで15h乾燥し含水率1.5%以下となるようにして、有機物吸着材の塊状物を得、粉砕し平均粒径72μmの有機物吸着材を得た。
なお、珪藻土を用いなかった比較例3については、前記乾燥後も粘性が高すぎて、粉砕することができず、下記の微生物吸着担体を製造することができなかった。
<Examples 1-9, Comparative Examples 1-6>
About Examples 1-9 and Comparative Examples 1-6, the organic substance adsorption material was obtained by the mixing | blending of following Table 1. Specifically, a solution A obtained by adding a water-soluble polymer (polyethyleneimine-containing aqueous solution (solid content: 30%), product name “Epomin P-1000” (registered trademark), manufactured by Nippon Shokubai Co., Ltd.)) to 340 parts by weight of water; A solution B in which a crosslinking agent (polyglycerol polyglycidyl ether product name “Denacol EX-512” (registered trademark) manufactured by Nagase ChemteX Corporation) was added to 70 parts by weight of water was prepared. Examples 1 to 9 and Comparative Examples For diatomaceous earth (laser diffraction method, average particle diameter 15 μm, product name “Radiolite # 300” (registered trademark) manufactured by Showa Chemical Industry Co., Ltd.), for comparative example 1, calcium carbonate (average particle diameter by laser diffraction method) 1.2 μm Product name “PC-700” manufactured by Shiraishi Calcium Co., Ltd.) and Comparative Example 4 for talc (average particle diameter by laser diffraction method) 0.0 μm manufactured by Nippon Talc Co., Ltd., Comparative Example 5 in clay (product name “Nikkagel S” manufactured by Toshin Kasei Co., Ltd.), and Comparative Example 6 in zeolite (product name “HSZ-700” manufactured by Tosoh Corporation) Solution A was added to, then Solution B was added and mixed with stirring. Thereafter, the mixture fluid is transferred to a container having a thickness of 50 mm, dried in an oven at 100 ° C. for 15 hours to obtain a water content of 1.5% or less, and an organic substance adsorbent mass is obtained and pulverized. An organic adsorbent having an average particle size of 72 μm was obtained.
In addition, about the comparative example 3 which did not use diatomaceous earth, the viscosity was too high after the said drying, and it was not able to grind | pulverize and the following microorganisms adsorption carrier was not able to be manufactured.

得られた有機物吸着材を用いて(比較例2については珪藻土のみを用いて)、微生物吸着性担体を成形した。成形方法は以下のとおりである。
低密度ポリエチレン100重量部に、実施例1〜9、比較例1、2、4〜6で得られた有機物吸着材3重量部およびタルク20重量部添加して押出成形して長さ5mmにカットし、外径5mm、肉厚0.25mmの中空状の微生物吸着性担体を得た。
A microorganism-adsorbing carrier was molded using the obtained organic substance adsorbent (only diatomaceous earth was used for Comparative Example 2). The molding method is as follows.
100 parts by weight of low density polyethylene, 3 parts by weight of the organic substance adsorbent obtained in Examples 1 to 9, Comparative Examples 1, 2, 4 to 6 and 20 parts by weight of talc were added and extruded to cut to a length of 5 mm Thus, a hollow microorganism-adsorbing carrier having an outer diameter of 5 mm and a wall thickness of 0.25 mm was obtained.

<参考例1>
低密度ポリエチレン100重量部にタルク20重量部を添加して押出成形し、長さ5mm、外径5mm、肉厚0.25mmの中空状の微生物吸着性担体を得た。得られた微生物吸着性担体を、ポリエチレンイミン(製品名「エポミンP−1000」(登録商標)株式会社日本触媒製)170gとポリグリセロールポリグリシジルエーテル(製品名「デナコールEX−512」(登録商標)ナガセケムテックス株式会社製)45g、水430gからなる溶液に含浸、乾燥して、表面に有機物吸着剤を被覆させた微生物吸着性担体を得た。
<Reference Example 1>
20 parts by weight of talc was added to 100 parts by weight of low density polyethylene, and extrusion molding was performed to obtain a hollow microorganism-adsorbing carrier having a length of 5 mm, an outer diameter of 5 mm, and a wall thickness of 0.25 mm. The obtained microorganism-adsorbing carrier was composed of 170 g of polyethyleneimine (product name “Epomin P-1000” (registered trademark) manufactured by Nippon Shokubai Co., Ltd.) and polyglycerol polyglycidyl ether (product name “Denacol EX-512” (registered trademark)). (Nagase ChemteX Co., Ltd.) 45 g of water and 430 g of water were impregnated and dried to obtain a microorganism-adsorbing carrier having a surface coated with an organic adsorbent.

実施例1〜9、比較例1、2、4〜6および参考例1で得られた微生物吸着性担体について、それぞれ下記に示す評価基準に基づいて、有機物吸着性、耐薬品性、耐光性、耐摩耗性、樹脂への分散性についての評価を行った。   About the microorganisms adsorptive carriers obtained in Examples 1 to 9, Comparative Examples 1, 2, 4 to 6 and Reference Example 1, based on the following evaluation criteria, organic matter adsorptivity, chemical resistance, light resistance, The wear resistance and dispersibility in the resin were evaluated.

<有機物吸着性>
アンモニウムイオンを含む合成排水を使用して、排水処理層の容器に対してみかけ体積にて20%の微生物吸着性担体を投入し、アンモニウムイオンの吸着性について、硝化速度が0.5kg−N/m3・day以上に達するまでに要した日数で評価した。
◎・・・15日未満
○・・・15日以上20日未満
△・・・20日以上25日未満
×・・・25日以上
NA・・・硝化速度が0.5kg−N/m・day以上にならない
<Organic adsorption>
Using synthetic waste water containing ammonium ions, a 20% microbial adsorbent carrier is introduced into the waste water treatment layer container in an apparent volume, and the nitrification rate is 0.5 kg-N / The evaluation was based on the number of days required to reach m3 · day or more.
◎ ... Less than 15 days ○ ... 15 days or more but less than 20 days △ ... 20 days or more but less than 25 days × ... 25 days or more NA ... Nitrification rate is 0.5 kg-N / m 3. not more than day

<耐薬品性>
有効塩素が0.1%の次亜塩素酸ナトリウム水溶液400cc中にみかけ体積100ccの微生物吸着性担体を投入し、撹拌羽を用いて400rpmの速度で回転させ、20時間後の担体の重量変化を以下のとおり評価した。
◎・・・重量変化が2%未満
×・・・重量変化が2%を超える
<Chemical resistance>
An apparently 100 cc microbial adsorbent carrier is put into 400 cc of a sodium hypochlorite aqueous solution containing 0.1% effective chlorine, and rotated at a speed of 400 rpm using a stirring blade, and the change in the weight of the carrier after 20 hours is observed. The evaluation was as follows.
◎ ・ ・ ・ Weight change is less than 2% × ・ ・ ・ Weight change is more than 2%

<耐光性>
フェードメーター(80±3℃、湿度50±5%以下の条件下)100時間照射後の微生物吸着性担体の表面状態の変化により耐光性を評価した。
◎・・・変化がほとんど認められない
×・・・劣化し、表面がボロボロになる
<Light resistance>
Light resistance was evaluated by a change in the surface state of the microorganism-adsorbing carrier after 100 hours of irradiation with a fade meter (under conditions of 80 ± 3 ° C. and humidity of 50 ± 5% or less).
◎ ... Almost no change is observed. × ... Deteriorated and the surface becomes tattered.

<耐摩耗性>
#100のサンドペーパーを内側全面に貼った500ccのビーカーに、水400cc、みかけ体積100ccの微生物吸着性担体を投入し、撹拌羽を用いて400rpmの速度で回転させて、10時間後の微生物吸着性担体の重量変化を下記のとおり評価した。
○・・・重量変化が2%未満
×・・・重量変化が2%を超える
<Abrasion resistance>
In a 500 cc beaker with sandpaper of # 100 pasted on the entire inner surface, 400 cc of water and an apparent volume of 100 cc of a microbial adsorbent carrier are added and rotated at a speed of 400 rpm using a stirring blade, and microbial adsorption after 10 hours is performed. The change in weight of the sex carrier was evaluated as follows.
○ ・ ・ ・ Weight change is less than 2% × ・ ・ ・ Weight change is more than 2%

<分散性>
微生物吸着性担体を成形する際の、低密度ポリエチレンへの有機物吸着材の分散性について、以下のように評価した。
◎・・・極めて良好
○・・・良好
△・・・均一に分散するまで時間を要す
<Dispersibility>
The dispersibility of the organic material adsorbent in low-density polyethylene when molding the microorganism-adsorbing carrier was evaluated as follows.
◎ ・ ・ ・ Very good ○ ・ ・ ・ Good △ ・ ・ ・ It takes time to disperse uniformly

結果を下記表1に示す。

Figure 2012137752
The results are shown in Table 1 below.
Figure 2012137752

表1の結果に示す通り、本発明に係る有機物吸着材を用いた実施例1〜9は、有機物である微生物に対し吸着性を示すことが確認できた。
珪藻土の代わりに炭酸カルシウムを用いた比較例1では、有機物吸着性を確認することができなかった。
また、珪藻土の代わりにタルクを用いた比較例4、珪藻土の代わりに粘土を用いた比較例5、珪藻土の代わりにゼオライトを用いた比較例6においても、有機物吸着性を確認することができなかった。
As shown in the results of Table 1, it was confirmed that Examples 1 to 9 using the organic adsorbent according to the present invention showed adsorptivity to microorganisms that are organic substances.
In Comparative Example 1 in which calcium carbonate was used instead of diatomaceous earth, organic matter adsorptivity could not be confirmed.
Further, in Comparative Example 4 using talc instead of diatomaceous earth, Comparative Example 5 using clay instead of diatomaceous earth, and Comparative Example 6 using zeolite instead of diatomaceous earth, organic matter adsorptivity cannot be confirmed. It was.

水溶性ポリマーと架橋剤の配合割合の違いによる各評価結果を検討すると、架橋剤1に対し水溶性ポリマーの配合割合が重量比で1未満である実施例6では、有機物吸着性が若干劣ることが分かった。逆に、架橋剤1に対し水溶性ポリマーの配合割合が重量比で10を超える実施例7では、有機物吸着性は良好であるが、分散性が若干劣ることが分かった。この結果から、水溶性ポリマーと架橋剤との好適な配合割合は、重量比で1〜10:1であることが分かった。   Examining each evaluation result based on the difference in the mixing ratio of the water-soluble polymer and the crosslinking agent, Example 6 in which the mixing ratio of the water-soluble polymer to the crosslinking agent 1 is less than 1 in weight ratio is slightly inferior in organic matter adsorption. I understood. On the contrary, it was found that in Example 7 in which the blending ratio of the water-soluble polymer with respect to the crosslinking agent 1 exceeds 10, the organic matter adsorptivity is good but the dispersibility is slightly inferior. From this result, it turned out that the suitable mixture ratio of a water-soluble polymer and a crosslinking agent is 1-10: 1 by weight ratio.

水溶性ポリマーおよび架橋剤と、珪藻土との配合割合の違いによる各評価結果を検討すると、水溶性ポリマーおよび架橋剤1に対し珪藻土の配合割合が重量比で1未満である実施例9では、分散性が若干劣ることが分かった。逆に、水溶性ポリマーおよび架橋剤1に対し珪藻土の配合割合が重量比で15を超える実施例8では、有機物吸着性が若干劣ることが分かった。この結果から、水溶性ポリマーおよび架橋剤と、珪藻土との好適な配合割合は、重量比で1:1〜15であることが分かった。   When each evaluation result by the difference in the blending ratio between the water-soluble polymer and the crosslinking agent and diatomaceous earth is examined, in Example 9 in which the blending ratio of the diatomaceous earth is less than 1 by weight with respect to the water-soluble polymer and the crosslinking agent 1, It was found that the properties were slightly inferior. On the contrary, in Example 8 where the blending ratio of diatomaceous earth with respect to the water-soluble polymer and the crosslinking agent 1 exceeds 15 by weight, it was found that the organic matter adsorptivity is slightly inferior. From this result, it turned out that the suitable mixture ratio of a water-soluble polymer and a crosslinking agent, and diatomaceous earth is 1: 1-15 by weight ratio.

[実験例2]
実験例2では、本発明に係る有機物吸着材を、排水処理などの水中で用いられる微生物吸着担体に応用する場合に、その好適な比重について検討を行った。具体的には、比重調整剤の一例としてタルクを用いて微生物吸着担体の比重を調整し、それぞれの初沈性を調べた。
[Experiment 2]
In Experimental Example 2, when the organic substance adsorbing material according to the present invention was applied to a microorganism-adsorbing carrier used in water such as wastewater treatment, a suitable specific gravity was examined. Specifically, the specific gravity of the microorganism-adsorbing carrier was adjusted using talc as an example of a specific gravity adjusting agent, and the initial sedimentation property of each was examined.

<実施例10〜14>
前記実験例1において製造した実施例1に係る有機物吸着材を用いて、下記の表2に記載の配合で、微生物吸着担体を得た。具体的には、低密度ポリエチレン100重量部に、前記実施例1に係る有機物吸着材3重量部および表2に記載の割合のタルクを添加して押出成形して長さ5mmにカットし、外径5mm、肉厚0.25mmの中空状の微生物吸着性担体を得た。
<Examples 10 to 14>
Using the organic adsorbent according to Example 1 manufactured in Experimental Example 1, a microorganism-adsorbing carrier was obtained with the formulation shown in Table 2 below. Specifically, to 100 parts by weight of low density polyethylene, 3 parts by weight of the organic matter adsorbent according to Example 1 and talc in the proportions shown in Table 2 were added and extruded to be cut to a length of 5 mm. A hollow microorganism-adsorbing carrier having a diameter of 5 mm and a wall thickness of 0.25 mm was obtained.

実施例10〜14で得られた微生物吸着性担体について、それぞれ下記に示す評価基準に基づいて、初沈性および流動性の評価を行った。   The microbial adsorbent carriers obtained in Examples 10 to 14 were evaluated for initial sedimentation and fluidity based on the evaluation criteria shown below.

<初沈性>
微生物吸着性担体を排水処理層に投入し、1時間後における排水処理層の水面に浮遊する微生物吸着性担体の重量の割合から、初沈性を評価した。評価基準は以下のとおりである。
◎・・・排水処理層の水面に浮遊する微生物吸着性担体の重量が投入量の1%未満
○・・・排水処理層の水面に浮遊する微生物吸着性担体の重量が投入量の1%以上50%未満
×・・・排水処理層の水面に浮遊する微生物吸着性担体の重量が投入量の50%以上
<Initial sedimentation>
The microorganism-adsorbing carrier was put into the wastewater treatment layer, and the initial sedimentation property was evaluated from the ratio of the weight of the microorganism-adsorbing carrier floating on the water surface of the wastewater treatment layer after 1 hour. The evaluation criteria are as follows.
◎ ・ ・ ・ The weight of the microorganism-adsorbing carrier floating on the water surface of the wastewater treatment layer is less than 1% of the input amount ○ ・ ・ ・ The weight of the microorganism-adsorbing carrier floating on the water surface of the wastewater treatment layer is 1% or more of the input amount Less than 50% × ・ ・ ・ The weight of the microorganism-adsorbing carrier floating on the water surface of the wastewater treatment layer is 50% or more of the input amount.

<流動性>
500ccのビーカーに水400cc、みかけ体積100ccの微生物吸着性担体を投入し、撹拌羽を用いて、400rpmの速度で回転させた際の、微生物吸着性担体の流動性を、以下の基準で評価した。
◎・・・微生物吸着性担体が、排水処理層中に均一に流動する。
○・・・微生物吸着性担体が、排水処理層の上方または下方に若干偏って流動するが排水処理能力にはほとんど影響がない
×・・・微生物吸着性担体が、排水処理層の上方または下方に偏って流動し、排水処理能力が発現しにくい。
<Fluidity>
The flowability of the microorganism-adsorbing carrier was evaluated according to the following criteria when a microorganism-adsorbing carrier having 400 cc of water and an apparent volume of 100 cc was put into a 500-cc beaker and rotated at a speed of 400 rpm using a stirring blade. .
A ... The microorganism-adsorbing carrier flows uniformly in the wastewater treatment layer.
○: The microorganism-adsorbing carrier flows slightly above or below the wastewater treatment layer, but has little effect on the wastewater treatment capacity. × ... The microorganism-adsorbing carrier is above or below the wastewater treatment layer. The wastewater treatment capacity is difficult to develop.

結果を下記表2に示す。

Figure 2012137752
The results are shown in Table 2 below.
Figure 2012137752

表2の結果に示す通り、本発明に係る有機物吸着性担体は、タルクなどの比重調整剤を用いて比重を調整することができることを確認できた。   As shown in the results of Table 2, it was confirmed that the organic substance-adsorbing carrier according to the present invention can adjust the specific gravity using a specific gravity adjusting agent such as talc.

比重の違いによる初沈性の評価結果を検討すると、比重の大きな微生物吸着性担体ほど、排水処理層の水面に浮遊するものが少なく、初沈性に優れることがわかる。
また、比重の違いによる流動性の評価結果を検討すると、排水処理層に微生物吸着性担体を投入した際には、比重の大きな微生物吸着性担体は排水処理層の下方に偏り、比重の小さな微生物吸着性担体は排水処理層の上方に偏って流動すること予想される。
Examining the evaluation results of the initial sedimentation property by the difference in specific gravity, it can be seen that the microorganism-adsorbing carrier having a larger specific gravity has less floating on the water surface of the wastewater treatment layer and is superior in initial sedimentation property.
In addition, when the evaluation results of the fluidity due to the difference in specific gravity are examined, when a microorganism-adsorbing carrier is introduced into the wastewater treatment layer, the microorganism-adsorbing carrier having a large specific gravity is biased below the wastewater treatment layer, The adsorptive carrier is expected to flow in an upward direction above the wastewater treatment layer.

この結果から、本発明に係る有機物吸着材を、排水処理などの水中で用いられる微生物吸着担体に応用する場合には、微生物吸着性担体の比重を0.98〜1.35g/cmとなるように調整することが好ましいことが分かった。From this result, when the organic matter adsorbent according to the present invention is applied to a microorganism adsorption carrier used in water such as waste water treatment, the specific gravity of the microorganism adsorption carrier becomes 0.98 to 1.35 g / cm 3. It was found that it was preferable to adjust the

Claims (7)

有機物を吸着するためのカチオン性の水溶性ポリマーと、
架橋剤と、
粉粒状態の珪藻土と、からなり、
前記珪藻土中に、前記水溶性ポリマーの架橋体が埋入された状態で担持されてなる有機物吸着材。
A cationic water-soluble polymer for adsorbing organic matter;
A crosslinking agent;
It consists of diatomaceous earth in powder form,
An organic substance adsorbent formed by supporting the crosslinked structure of the water-soluble polymer in the diatomaceous earth.
前記水溶性ポリマーは、アミノ基を備えることを特徴とする請求項1に記載の有機物吸着材。   The organic substance adsorbent according to claim 1, wherein the water-soluble polymer has an amino group. 前記水溶性ポリマーは、ポリエチレンイミンである請求項2記載の有機物吸着材。   The organic matter adsorbent according to claim 2, wherein the water-soluble polymer is polyethyleneimine. 前記架橋剤は、エポキシ誘導体であることを特徴とする請求項1から3のいずれか一項に記載の有機物吸着材。   The organic material adsorbent according to any one of claims 1 to 3, wherein the cross-linking agent is an epoxy derivative. 前記エポキシ誘導体は、ポリグリセロールポリグリシジルエーテルである請求項4記載の有機物吸着材。   The organic adsorbent according to claim 4, wherein the epoxy derivative is polyglycerol polyglycidyl ether. 前記水溶性ポリマーと前記架橋剤とが、1〜10:1の重量比で含有されてなることを特徴とする請求項1から5のいずれか一項に記載の有機物吸着材。   The organic adsorbent according to any one of claims 1 to 5, wherein the water-soluble polymer and the crosslinking agent are contained in a weight ratio of 1 to 10: 1. 前記請求項1から6のいずれか一項に記載の有機物吸着材が合成樹脂中に含有されてなる有機物吸着性担体。   The organic substance adsorbent support | carrier in which the organic substance adsorption material as described in any one of the said Claims 1-6 is contained in a synthetic resin.
JP2012516428A 2011-04-07 2012-04-03 Microbe adsorption carrier Expired - Fee Related JP5952187B2 (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP2011085442 2011-04-07
JP2011085442 2011-04-07
PCT/JP2012/059029 WO2012137752A1 (en) 2011-04-07 2012-04-03 Organic substance adsorbent material and organic substance adsorbent carrier comprising said organic substance adsorbent material

Publications (2)

Publication Number Publication Date
JPWO2012137752A1 true JPWO2012137752A1 (en) 2014-07-28
JP5952187B2 JP5952187B2 (en) 2016-07-13

Family

ID=46969150

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2012516428A Expired - Fee Related JP5952187B2 (en) 2011-04-07 2012-04-03 Microbe adsorption carrier

Country Status (2)

Country Link
JP (1) JP5952187B2 (en)
WO (1) WO2012137752A1 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP6607485B2 (en) * 2015-04-30 2019-11-20 国立大学法人名古屋大学 Method for removing suspended cesium
CN109264866B (en) * 2018-09-11 2021-08-20 湖北理工学院 Preparation method and application of hygrophyte plant fiber filler for strengthening denitrification of constructed wetland

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6274286A (en) * 1985-09-23 1987-04-06 マイルス・ラボラトリ−ス・インコ−ポレ−テツド Immobilization of bio-catalyst by granular diatomaceous earth
JPH07147981A (en) * 1993-09-01 1995-06-13 Solvay Enzymes Inc Method for production of immobilized enzyme complex and saidimmobilized enzyme complex produced by said method
JP2001128674A (en) * 1999-11-09 2001-05-15 Bio Carrier Technology:Kk Carrier coated with insolubilized water-soluble microorganism-adsorbing material
JP2002013146A (en) * 2000-06-28 2002-01-18 Shiima Consultant:Kk Slope stabilization working method
JP2004122032A (en) * 2002-10-03 2004-04-22 Bio Carrier Technology:Kk Water purifying treatment system
US20040144720A1 (en) * 2003-01-28 2004-07-29 Industrial Technology Research Institute Method for treating wastewater/water with fixed-film microorganism on porous carriers
JP2005500158A (en) * 2001-08-22 2005-01-06 コミツサリア タ レネルジー アトミーク Method for preparing composite solid material based on hexacyanoiron salt and method for immobilizing inorganic pollutants using the same
JP2009509513A (en) * 2005-09-30 2009-03-12 ノボザイムス アクティーゼルスカブ Immobilization of enzyme

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6274286A (en) * 1985-09-23 1987-04-06 マイルス・ラボラトリ−ス・インコ−ポレ−テツド Immobilization of bio-catalyst by granular diatomaceous earth
JPH07147981A (en) * 1993-09-01 1995-06-13 Solvay Enzymes Inc Method for production of immobilized enzyme complex and saidimmobilized enzyme complex produced by said method
JP2001128674A (en) * 1999-11-09 2001-05-15 Bio Carrier Technology:Kk Carrier coated with insolubilized water-soluble microorganism-adsorbing material
JP2002013146A (en) * 2000-06-28 2002-01-18 Shiima Consultant:Kk Slope stabilization working method
JP2005500158A (en) * 2001-08-22 2005-01-06 コミツサリア タ レネルジー アトミーク Method for preparing composite solid material based on hexacyanoiron salt and method for immobilizing inorganic pollutants using the same
JP2004122032A (en) * 2002-10-03 2004-04-22 Bio Carrier Technology:Kk Water purifying treatment system
US20040144720A1 (en) * 2003-01-28 2004-07-29 Industrial Technology Research Institute Method for treating wastewater/water with fixed-film microorganism on porous carriers
JP2009509513A (en) * 2005-09-30 2009-03-12 ノボザイムス アクティーゼルスカブ Immobilization of enzyme

Also Published As

Publication number Publication date
JP5952187B2 (en) 2016-07-13
WO2012137752A1 (en) 2012-10-11

Similar Documents

Publication Publication Date Title
Godiya et al. Functional biobased hydrogels for the removal of aqueous hazardous pollutants: current status, challenges, and future perspectives
Yamasaki et al. Preparation of crosslinked β‐cyclodextrin polymer beads and their application as a sorbent for removal of phenol from wastewater
US8852639B2 (en) Antimicrobial foam and method of manufacture
JP2020529917A (en) Removal of bacteria from drinking water by filtration
JP5952187B2 (en) Microbe adsorption carrier
Cui et al. Preparation and evaluation of self-assembled porous microspheres–fibers for removal of bisphenol A from aqueous solution
JP6364769B2 (en) Resin composition, microorganism-immobilized carrier and purification method
JP2007007575A (en) Microorganism carrier and its production method
CN1960793A (en) Gas porous polymer filter and methods of making it
CN107935618A (en) A kind of ecological decoration diatom ooze artificial sand rock composite plate and preparation method
Zendehdel et al. Investigation of removal of chemical oxygen demand (COD) wastewater and antibacterial activity of nanosilver incorporated in poly (acrylamide-co-acrylic acid)/NaY zeolite nanocomposite
Ghahramani et al. Open‐cell polyvinylidene fluoride foams as carriers to promote biofilm growth for biological wastewater treatment
JP2022087164A (en) Microbial immobilization carrier
JP2017094259A (en) Membrane fouling inhibitor
CN112980268A (en) Water-based paint coating with air purification function and preparation method thereof
KR101300645B1 (en) Antimicrobial wrap for food packaging
Zhao et al. Bisphenol A adsorption properties of mesoporous CaSiO3@ SiO2 grafted nonwoven polypropylene fiber
JP6263061B2 (en) Low swellable composition and method for producing the same
KR101765130B1 (en) Positive electric charge-coating agent for antivirus media, Antivirus media using that and Preparing method thereof
JP7101162B2 (en) Gas adsorbent carrier and its manufacturing method
WO2015076370A1 (en) Biopolymer-adsorbing composition and water treatment method using same
Katibi et al. Development of Novel Fouling-Resistant Hollow Fibre Nanocomposite Membrane Augmented with Iron Oxide Nanoparticles for Efficient Rejection of Bisphenol A from Water: Fouling, Permeability, and Mechanism Studies
Nazir et al. Polymeric membranes nanocomposites as effective strategy for dye removal
Garea et al. Hybrid materials based on dendritic polymer and halloysite
KR101398089B1 (en) Antimicrobial dehumidifier

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20150122

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20151104

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20151225

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20160301

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20160413

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: 20160517

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20160609

R150 Certificate of patent or registration of utility model

Ref document number: 5952187

Country of ref document: JP

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

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees