JPH10314782A - Water treatment carrier, its production method and nitrification denitrification method using the same - Google Patents

Water treatment carrier, its production method and nitrification denitrification method using the same

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Publication number
JPH10314782A
JPH10314782A JP13191797A JP13191797A JPH10314782A JP H10314782 A JPH10314782 A JP H10314782A JP 13191797 A JP13191797 A JP 13191797A JP 13191797 A JP13191797 A JP 13191797A JP H10314782 A JPH10314782 A JP H10314782A
Authority
JP
Japan
Prior art keywords
carrier
hydrogel
water
nitrification
ability
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
JP13191797A
Other languages
Japanese (ja)
Other versions
JP3686215B2 (en
Inventor
Tadao Shiotani
唯夫 塩谷
Hiroaki Fujii
弘明 藤井
Takanori Kitamura
隆範 北村
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.)
Kuraray Co Ltd
Original Assignee
Kuraray Co Ltd
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 Kuraray Co Ltd filed Critical Kuraray Co Ltd
Priority to JP13191797A priority Critical patent/JP3686215B2/en
Publication of JPH10314782A publication Critical patent/JPH10314782A/en
Application granted granted Critical
Publication of JP3686215B2 publication Critical patent/JP3686215B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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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

  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

PROBLEM TO BE SOLVED: To execute simultaneously nitrification and denitrification of organic wastewater by constituting so that a microbe having nitrification function lives near a surface of a carrier, and a microbe having a denitrification function lives near a central part. SOLUTION: For the water treating carrier, acetal-made PVA or polyethylene glycol water-containing gel having a network structure on a surface or inside is used. In this carrier, a microbe having a nitrification function lives near the surface of the carrier, and a microbe having a denitrification function lives near a central part. In order to manufacture such the carrier, for example, PVA is brought in contact with the microbe having denitrification function such as Pseudomonas denitrificans or the like, brought in contact with the microbe having nitrification function such as Nitrosomonas or the like after the microbe having denitrification function enters an inside of the carrier, and cultured to obtain such the carrier. Since the carrier has both of the nitrification function and the denitrification function, nitrification and denitrification can be simultaneously executed.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、水処理用担体、その製
造方法及びそれを用いた硝化脱窒方法に関する。さらに
詳しくは、表面近傍に硝化能を有する微生物が生息し、
中心部近傍に脱窒能を有する微生物が生息しているアセ
タ−ル化されたポリビニルアルコ−ル系の含水ゲル又は
ポリエチレングリコール系の含水ゲルからなる水処理用
担体、その製造方法及びそれを用いた硝化脱窒方法に関
する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a carrier for water treatment, a method for producing the same, and a method for nitrification and denitrification using the same. More specifically, microorganisms having nitrifying ability inhabit near the surface,
A water treatment carrier comprising an acetalized polyvinyl alcohol-based hydrogel or polyethylene glycol-based hydrogel in which microorganisms having a denitrifying ability inhabit in the vicinity of the center, a method for producing the same, and use thereof The nitrification and denitrification method.

【0002】[0002]

【従来の技術】従来、農村集落排水、家庭雑排水、都市
下水、養魚排水、各種産業排水などの窒素化合物を含む
有機性排水は、一般的に、好気性微生物及び嫌気性微生
物を使用して汚濁物質を浄化する方法により処理されて
きた。例えば、図1に示すように、排水を嫌気槽1に流
入し、BOD成分の大半を除去し、次いで好気槽2で好
気条件下に残りのBOD成分の酸化と硝化菌による窒素
化合物の硝化を行い、好気槽2から流出する処理水の一
部を嫌気槽1に循環し、嫌気条件下に脱窒菌を使用して
脱窒除去し、残りの好気槽からの流出水は沈殿槽3で汚
泥を沈降分離した後、放流していた。
2. Description of the Related Art Conventionally, organic wastewater containing nitrogen compounds, such as rural settlement wastewater, household wastewater, urban wastewater, fish culture wastewater and various industrial wastewater, generally uses aerobic microorganisms and anaerobic microorganisms. It has been treated by methods of purifying pollutants. For example, as shown in FIG. 1, the wastewater flows into the anaerobic tank 1 to remove most of the BOD components, and then oxidizes the remaining BOD components under aerobic conditions in the aerobic tank 2 and removes nitrogen compounds by nitrifying bacteria. Nitrification is performed, a part of the treated water flowing out of the aerobic tank 2 is circulated to the anaerobic tank 1, and denitrification is removed using denitrifying bacteria under anaerobic conditions, and the effluent from the remaining aerobic tank is settled. The sludge was settled and separated in the tank 3 and then discharged.

【0003】近年、微生物が付着増殖する担体を処理槽
に充填して排水処理装置の小型化を図る検討が進められ
ており、このような担体として各種のセラミックス、プ
ラスチックスなどの粒状体やハニカム状の構造体などが
開発されている。排水処理に使用する担体としては、含
水率が高いこと、酸素や基質の透過性に優れているこ
と、生体との親和性が高いことなどが要求され、このよ
うな排水処理用に好適な担体として各種の高分子担体が
提案されており、その一例としてポリビニルアルコール
系の含水ゲルがある。
In recent years, studies have been made to reduce the size of a wastewater treatment apparatus by filling a processing tank with a carrier to which microorganisms adhere and proliferate. As such a carrier, various types of granular materials such as ceramics and plastics, and honeycombs have been proposed. -Like structures have been developed. The carrier used for wastewater treatment is required to have a high water content, excellent oxygen and substrate permeability, high affinity with living organisms, etc. Various types of polymer carriers have been proposed as examples, and examples thereof include polyvinyl alcohol-based hydrogels.

【0004】ポリビニルアルコール含水ゲル(以下、ポ
リビニルアルコールをPVAと略称する)は、PVAと
アルギン酸ナトリウムの混合水溶液を塩化カルシウム水
溶液に接触させて球状化した後、凍結解凍を行う方法
(特開昭64−43188号公報)、PVA水溶液を飽
和ホウ酸水溶液に接触させて含水ゲル化する方法(下水
道協会誌、第23巻(1986)p41;用水と廃水、
第30巻(1986)p36)、PVA水溶液を鋳型に
注入後、凍結部分脱水を行う方法(特開昭58−366
30号公報)などによって得られ、このようなPVA含
水ゲルは水処理に使用されることが知られている。
A water-containing gel of polyvinyl alcohol (hereinafter, polyvinyl alcohol is abbreviated as PVA) is prepared by bringing an aqueous mixed solution of PVA and sodium alginate into contact with an aqueous calcium chloride solution to form a sphere, followed by freezing and thawing (Japanese Patent Laid-Open No. Sho 64). No. 43188), a method of bringing a PVA aqueous solution into contact with a saturated boric acid aqueous solution to form a hydrous gel (Sewer Association of Japan, Vol. 23 (1986) p41;
Vol. 30 (1986) p36), a method of injecting a PVA aqueous solution into a mold and then performing a partial dehydration by freezing (JP-A-58-366)
No. 30 publication), and such PVA hydrogel is known to be used for water treatment.

【0005】しかしながら、これらの有機性排水処理に
おいては、硝化反応用の好気槽と、脱窒反応用の嫌気槽
が別々に配置されており、したがって、担体を各槽に別
々に投入しなければならず、装置の小型化には限界があ
った。硝化及び脱窒を同時に行うことのできる担体を使
用することができれば、極めて効率的であり、装置をコ
ンパクト化することも可能となる。
[0005] However, in these organic wastewater treatments, an aerobic tank for the nitrification reaction and an anaerobic tank for the denitrification reaction are separately arranged. Therefore, the carrier must be separately charged into each tank. Therefore, miniaturization of the apparatus has its limits. If a carrier capable of simultaneously performing nitrification and denitrification can be used, it is extremely efficient and the apparatus can be made compact.

【0006】一方、硝化及び脱窒を同時に行うこともす
でに提案されており、例えば、特開平5−130867
号公報には、表面までの最短距離が2mm以上である点
を含水ゲル内部に有し、表面近傍に好気性菌が固定さ
れ、中心部近傍に嫌気性菌が固定されたPVAを主成分
とする生体触媒固定化含水ゲルが開示されており、特開
平8−224076号公報には、光硬化性樹脂等の合成
高分子担体にアンモニア酸化菌および/または脱窒菌等
の微生物を固定化した担体をチュ−ブ状、フィルム状等
に成形したものが開示されている。
On the other hand, it has already been proposed to simultaneously perform nitrification and denitrification.
The publication has a point that the shortest distance to the surface is 2 mm or more inside the hydrogel, aerobic bacteria are fixed near the surface, and PVA in which anaerobic bacteria are fixed near the center is the main component. JP-A-8-224076 discloses a carrier in which microorganisms such as ammonia-oxidizing bacteria and / or denitrifying bacteria are immobilized on a synthetic polymer carrier such as a photocurable resin. Is formed into a tube shape, a film shape, or the like.

【0007】[0007]

【発明が解決しようとする課題】しかしながら、特開平
5−130867号公報に開示された担体は凍結解凍に
より製造される含水ゲルであるため、得られた含水ゲル
は緻密層を有しており、該緻密層がバリヤーとなって、
脱窒能を有する微生物(以下、脱窒菌という)が内部に
進入することが困難であり、したがって、このような含
水ゲルを使用して脱窒菌が内部に生息する担体を得るた
めには、予め脱窒菌を担体内部に包括させて製造するい
わゆる包括固定法による必要がある。
However, since the carrier disclosed in Japanese Patent Application Laid-Open No. Hei 5-130867 is a hydrogel produced by freezing and thawing, the obtained hydrogel has a dense layer. The dense layer becomes a barrier,
It is difficult for microorganisms capable of denitrification (hereinafter, referred to as denitrifying bacteria) to enter inside. Therefore, in order to obtain a carrier in which denitrifying bacteria live inside using such a hydrogel, It is necessary to use a so-called entrapment fixing method in which denitrifying bacteria are produced by entrapping them in a carrier.

【0008】また特開平8−224076号公報に開示
された担体も、菌を合成高分子担体に包括固定したもの
であり、しかもこれをさらに成形したものであるため、
簡単に製造できない難点がある。したがって、本発明の
目的は、菌を包括固定せずに製造することができ、有機
性排水の硝化及び脱窒を同時に行うことができるアセタ
−ル化されたPVA系の含水ゲル又はポリエチレングリ
コール系の含水ゲルからなる水処理用の担体とその製造
方法を提供することにあり、またそれを用いた硝化脱窒
方法を提供することにある。
[0008] The carrier disclosed in Japanese Patent Application Laid-Open No. H8-224076 is also one in which bacteria are entrapped and immobilized on a synthetic polymer carrier, which is further molded.
There are difficulties that cannot be easily manufactured. Accordingly, an object of the present invention is to provide an acetalized PVA-based hydrous gel or polyethylene glycol-based gel that can be produced without entrapping and fixing bacteria and can simultaneously perform nitrification and denitrification of organic wastewater. Another object of the present invention is to provide a water treatment carrier comprising a hydrogel and a method for producing the same, and a nitrification denitrification method using the same.

【0009】[0009]

【課題を解決するための手段】本発明者らは、鋭意検討
を重ね、表面及び/又は内部に網目構造を有する、アセ
タール化されたPVA系含水ゲル又はポリエチレングリ
コール系の含水ゲルを担体として使用すれば、脱窒菌の
進入を阻止する緻密層がないため脱窒菌が担体内部に生
息しやすく、しかも硝化能を有する微生物(以下、硝化
菌という)は担体表面に生息しやすいので、有機性排水
の硝化及び脱窒を同時に行うことができることを見出だ
し、本発明に至った。すなわち本発明は、表面及び/又
は内部に網目構造を有するアセタ−ル化されたPVA系
の含水ゲル又はポリエチレングリコール系の含水ゲルか
らなる担体であって、該担体の表面近傍に硝化能を有す
る微生物が生息し、中心部近傍に脱窒能を有する微生物
が生息していることを特徴とする水処理用担体である。
Means for Solving the Problems The present inventors have conducted intensive studies and have used as a carrier a PVA-based hydrogel or a polyethylene glycol-based hydrogel having a network structure on the surface and / or inside. If there is no dense layer that prevents the invasion of denitrifying bacteria, the denitrifying bacteria can easily inhabit inside the carrier, and microorganisms having nitrification ability (hereinafter referred to as nitrifying bacteria) can easily invade on the carrier surface. It has been found that nitrification and denitrification can be carried out simultaneously, leading to the present invention. That is, the present invention relates to a carrier comprising an acetalized PVA-based hydrogel or a polyethylene glycol-based hydrogel having a network structure on the surface and / or inside, and having a nitrification ability near the surface of the carrier. A carrier for water treatment, wherein microorganisms inhabit, and microorganisms having a denitrifying ability inhabit in the vicinity of the center.

【0010】本発明の別の発明は、アセタ−ル化された
PVA系の含水ゲル又はポリエチレングリコール系の含
水ゲルを脱窒能を有する微生物と接触させ、該微生物が
含水ゲル内部に侵入した後、硝化能を有する微生物と接
触させ、該微生物を含水ゲル表面近傍に生息させること
を特徴とするアセタ−ル化されたPVA系の含水ゲル又
はポリエチレングリコール系の含水ゲルからなる水処理
用担体の製造方法である。
Another aspect of the present invention is to provide a method comprising contacting an acetalized PVA-based hydrogel or a polyethylene glycol-based hydrogel with a microorganism having a denitrifying ability, and the microorganism invading the interior of the hydrogel. A water treatment carrier comprising an acetalized PVA-based hydrogel or a polyethylene glycol-based hydrogel, which is brought into contact with a microorganism having a nitrifying ability, and the microorganism inhabits near the surface of the hydrogel. It is a manufacturing method.

【0011】本発明のさらに別の発明は、表面近傍に硝
化能を有する微生物が生息し、中心部近傍に脱窒能を有
する微生物が生息しているアセタ−ル化されたPVA系
の含水ゲル又はポリエチレングリコール系の含水ゲルか
らなる水処理用担体を用いて有機性排水の硝化脱窒を同
時に行うことを特徴とする硝化脱窒方法である。
[0011] Still another invention of the present invention is an acetalized PVA-based hydrogel in which microorganisms having nitrifying ability inhabit near the surface and microorganisms having denitrifying ability inhabit in the vicinity of the center. Alternatively, a nitrification denitrification method characterized by simultaneously performing nitrification denitrification of organic wastewater using a water treatment carrier comprising a polyethylene glycol-based hydrogel.

【0012】[0012]

【発明の実施の形態】以下、本発明を具体的に説明す
る。本発明の水処理用担体は、表面及び/又は内部に網
目構造を有しているが、このような構造を有する担体と
して、アセタール化されたPVA又はポリエチレングリ
コール系の含水ゲルが使用される。アセタール化された
PVA含水ゲル又はポリエチレングリコール系の含水ゲ
ルは、担体表面及び内部に網目構造を有し、菌が進入す
る際のバリヤーとなる緻密層を有していないので、脱窒
菌が内部に容易に進入しやすく、しかも表面には硝化菌
が生息しやすいので、本発明の目的に適った担体とな
り、製造も容易である。本発明の担体は、有機化合物の
除去能力に優れており、かつ機械的強度にも優れている
ので、水処理用の担体として好適である。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be specifically described below. The carrier for water treatment of the present invention has a network structure on the surface and / or inside. As the carrier having such a structure, acetalized PVA or a polyethylene glycol-based hydrogel is used. Acetalized PVA hydrogel or polyethylene glycol-based hydrogel has a network structure on the surface and inside of the carrier, and does not have a dense layer that serves as a barrier when bacteria enter, so that denitrifying bacteria are contained inside. Since it is easy to enter and nitrifying bacteria easily inhabit on the surface, it becomes a carrier suitable for the purpose of the present invention and is easy to manufacture. The carrier of the present invention is excellent as a carrier for water treatment because it has excellent ability to remove organic compounds and excellent mechanical strength.

【0013】PVAの平均重合度及び/又はケン化度は
高い方がPVAの濃度を低下することができるので、含
水ゲルの含水率を上げることができ、したがって、微生
物の生息性がよくなり好ましい。かかる点から、PVA
の平均重合度は1000以上のものが好ましく、とくに
1500以上のものがさらに好ましい。また、PVAの
ケン化度は95モル%以上のものが好ましく、とくに9
8モル%以上のものがさらに好ましい。
When the average degree of polymerization and / or saponification degree of PVA is higher, the concentration of PVA can be reduced, so that the water content of the hydrogel can be increased. . From this point, PVA
The average degree of polymerization is preferably 1,000 or more, more preferably 1500 or more. Further, the degree of saponification of PVA is preferably 95 mol% or more, particularly preferably 9 mol%.
More than 8 mol% is more preferable.

【0014】PVAの濃度は担体の強度面から大きい方
が好ましく、微生物の生息性からは小さい方が好ましい
ので、1wt%〜40wt%が好ましく、3wt%〜2
0wt%がさらに好ましい。
The concentration of PVA is preferably large from the viewpoint of the strength of the carrier, and is preferably small from the viewpoint of microbial habitat. Therefore, the concentration is preferably 1 wt% to 40 wt%, more preferably 3 wt% to 2 wt%.
0 wt% is more preferable.

【0015】本発明において、PVAの溶出や劣化を防
止するために、PVAはアセタ−ル化されるが、アセタ
−ル化剤としては、ホルムアルデヒド、グリオキザ−
ル、グルタルアルデヒド、ベンズアルデヒド、スクシン
アルデヒド、マロンジアルデヒド、アジピンアルデヒ
ド、テレフタルアルデヒド、ω,ω´−ノナンジア−ル
などを例示することができる。ポリビニルホルマ−ルは
このようなアセタ−ル化PVAの好ましい例である。ア
セタ−ル化度は、あまり低いと耐水性が低くなり、また
あまり高いと疎水化されて微生物の生息が悪くなるの
で、10〜60モル%が好ましく、20〜55モル%が
さらに好ましい。
In the present invention, PVA is acetalized in order to prevent elution or deterioration of PVA, and formaldehyde and glyoxal are used as acetalizing agents.
, Glutaraldehyde, benzaldehyde, succinaldehyde, malondialdehyde, adipaldehyde, terephthalaldehyde, ω, ω'-nonandial, and the like. Polyvinyl formal is a preferred example of such an acetalized PVA. If the degree of acetalization is too low, the water resistance will be low, and if it is too high, it will be hydrophobized and the inhabitation of microorganisms will deteriorate, so it is preferably from 10 to 60 mol%, more preferably from 20 to 55 mol%.

【0016】アセタ−ル化するために使用される酸とし
ては、硫酸、塩酸、リン酸、硝酸、酢酸、シュウ酸など
の酸をあげることができ、硫酸水素ナトリウム、硫酸水
素アンモニウムなどの酸性塩も使用される。アルデヒド
化合物や酸の存在下では、含水ゲルが過膨潤したり、溶
解する可能性があるので、アセタ−ル化液にはその抑制
剤として、PVAの離液作用のある硫酸ナトリウムなど
を添加してもよい。
Examples of the acid used for acetalization include acids such as sulfuric acid, hydrochloric acid, phosphoric acid, nitric acid, acetic acid and oxalic acid, and acidic salts such as sodium hydrogen sulfate and ammonium hydrogen sulfate. Is also used. In the presence of an aldehyde compound or acid, the hydrogel may overswell or dissolve, so that sodium acetate or the like, which has the effect of synthesizing PVA, is added to the acetalization solution as an inhibitor. You may.

【0017】PVAのアセタ−ル化を阻害しない範囲
で、例えばアルギン酸ナトリウム、カラギ−ナン、ホウ
酸などの成型助剤や炭酸イオン、炭酸水素イオン、硫酸
イオン、リン酸イオンなどの2種以上の高分子を相分離
させるような1価又は多価アニオンを添加してもよい。
アセタ−ル化したPVA系含水ゲルは、表面が凹凸構造
であるとともに、表面から中心部に連通孔を有している
ので、表面のみならず、内部まで有効に活用できる。
As long as the acetalization of PVA is not inhibited, for example, molding aids such as sodium alginate, carrageenan, boric acid, and two or more kinds of carbonate ions, hydrogen carbonate ions, sulfate ions, phosphate ions, etc. A monovalent or polyvalent anion for phase separation of the polymer may be added.
The acetalized PVA-based hydrated gel has an uneven surface and a communication hole from the surface to the center, so that it can be effectively used not only on the surface but also on the inside.

【0018】アセタ−ル化したPVA含水ゲルは、アセ
タ−ル化液と分離し、水洗や中和などの処理をして、排
水処理に使用できる担体となる。含水ゲル状担体は、一
旦乾燥させてもよい。水に浸漬すると再び含水ゲルとな
る。含水率は高い方が好ましく、湿潤重量基準で50〜
99%が好ましく、さらに好ましくは、60〜98%で
ある。湿潤重量基準の含水率の測定方法は、担体を25
℃の水に24時間以上浸漬した後、表面付着水を除いた
担体の重量を測定し(湿重量)、これを105℃で4時
間乾燥後、重量を測定する(乾重量)。湿潤重量基準の
含水率は、{(湿重量−乾重量)/湿重量}×100
(%)で表される。
The acetalized PVA hydrogel is separated from the acetalized solution, subjected to a treatment such as washing or neutralization, and becomes a carrier which can be used for wastewater treatment. The hydrogel carrier may be dried once. When immersed in water, it becomes a hydrogel again. The higher the water content, the better, and 50 to 50% by wet weight.
It is preferably 99%, more preferably 60 to 98%. The method for measuring the moisture content based on wet weight is as follows.
After immersion in water at 24 ° C. for 24 hours or more, the weight of the carrier excluding water adhering to the surface is measured (wet weight), and after drying at 105 ° C. for 4 hours, the weight is measured (dry weight). The moisture content based on wet weight is {(wet weight−dry weight) / wet weight} × 100
(%).

【0019】最も好ましいアセタール化PVA含水ゲル
は、特願平9−11057号として出願人によりすでに
出願されている、表面に平均径10〜100μm及び深
さ10〜100μmの凹部を表面の長さ1mm当たり1
0個以上有し、含水率が50重量%以上であるアセタ−
ル化PVA含水ゲルである。この含水ゲルを製造する方
法は、上記明細書に詳述されているが、一例をあげれ
ば、平均重合度1700、ケン化度99.8モル%のP
VA8wt%、アルギン酸ナトリウム1wt%、炭酸水
素ナトリウム0.3wt%の混合水溶液を調製し、該水
溶液を0.1モル/リットル(L)の塩化カルシウム水
溶液に滴下することにより、球状成形物として得、しか
る後、ホルムアルデヒド20g/L、硫酸200g/
L、硫酸ナトリウム100g/Lのアセタ−ル化用水溶
液に浸漬し、水洗して得ることができる。このようなP
VA含水ゲルは、前述したように、担体表面及び内部に
網目構造を有している。担体表面及び内部に網目構造を
有していることは、走査型電顕で確認することができ
る。
The most preferred acetalized PVA hydrated gel has a surface having an average diameter of 10 to 100 μm and a depth of 10 to 100 μm in a concave portion having a length of 1 mm, which has already been filed by the applicant as Japanese Patent Application No. 9-11057. 1 per
Acetator having 0 or more and having a water content of 50% by weight or more
Hydrated PVA hydrogel. The method for producing this hydrogel is described in detail in the above specification, but, for example, a P having an average degree of polymerization of 1700 and a degree of saponification of 99.8 mol% can be mentioned.
A mixed aqueous solution of 8 wt% of VA, 1 wt% of sodium alginate and 0.3 wt% of sodium hydrogen carbonate is prepared, and the aqueous solution is dropped into a 0.1 mol / L (L) aqueous solution of calcium chloride to obtain a spherical molded product. Then, formaldehyde 20g / L, sulfuric acid 200g / L
L, 100 g / L sodium sulfate can be obtained by immersion in an aqueous solution for acetalization and washing with water. Such a P
As described above, the VA hydrogel has a network structure on the surface and inside of the carrier. The presence of a network structure on the surface and inside of the carrier can be confirmed by a scanning electron microscope.

【0020】ポリエチレングリコール系の含水ゲルもB
OD除去能力、硝化能力及び脱窒能力の点で優れてお
り、好適な担体である。ポリエチレングリコール含水ゲ
ルは、例えば特公平6−32615号公報に開示された
方法で得ることができる。
Polyethylene glycol-based hydrogel is also B
It is excellent in OD removal ability, nitrification ability and denitrification ability, and is a suitable carrier. The polyethylene glycol hydrated gel can be obtained, for example, by the method disclosed in Japanese Patent Publication No. 6-32615.

【0021】本発明の水処理用担体は、前述のように、
担体の表面近傍に硝化能を有する微生物が生息し、中心
部近傍に脱窒能を有する微生物が生息している。このよ
うな水処理用担体を製造するには、例えば上記PVAを
シュ−ドモナスデニトリフィカンス(Pseudomo
nas denitrificans)などの脱窒能を
有する微生物と接触させ、脱窒能を有する微生物が担体
内部に侵入した後、ニトロソモナス(Nitrosom
onas)などの硝化能を有する微生物と接触させ、馴
養することにより、表面近傍に硝化能を有する微生物が
生息し、中心部近傍に脱窒能を有する微生物が生息する
担体を得ることができる。
The carrier for water treatment of the present invention comprises, as described above,
Microorganisms having nitrification ability live near the surface of the carrier, and microorganisms having denitrification ability live near the center. In order to manufacture such a carrier for water treatment, for example, the above PVA is prepared by using Pseudomonas denitrificans (Pseudomo).
nitrosomonas (Nitrosomnas) after the microorganisms having a denitrifying ability are brought into contact with a microorganism having a denitrifying ability such as nas denitrificans.
By contacting and acclimating with a microorganism having a nitrifying ability such as onas), a carrier in which a microorganism having a nitrifying ability inhabits near the surface and a microorganism having a denitrifying ability inhabits near the center can be obtained.

【0022】また、別の手法として、一般的な活性汚泥
などの微生物に、PVAなどの担体を接触させた後、ア
ンモニア性窒素を含む水とともに曝気馴養する方法によ
ってもよい。かかる方法によれば、担体表面は好気性雰
囲気であるため硝化能のある微生物が優勢となり、一
方、担体中心部近傍は嫌気性雰囲気となるため内部に侵
入した微生物は脱窒能のある微生物が優勢となるので、
本発明の、表面近傍に硝化能を有する微生物が生息し、
中心部近傍に脱窒能を有する微生物が生息している水処
理用担体を得ることができる。
As another method, a method may be employed in which a carrier such as PVA is brought into contact with microorganisms such as general activated sludge and then aerated with water containing ammonia nitrogen. According to this method, the surface of the carrier is an aerobic atmosphere, so that nitrifying microorganisms are dominant.On the other hand, the vicinity of the center of the carrier is an anaerobic atmosphere, and the microorganisms that have entered the inside are microorganisms capable of denitrification. Because it will be dominant,
In the present invention, microorganisms having nitrifying ability inhabit near the surface,
A water treatment carrier in which microorganisms having a denitrifying ability inhabit in the vicinity of the center can be obtained.

【0023】本発明の水処理用担体は、表面近傍に硝化
菌が生息し、中心部近傍に脱窒菌が生息する。本発明に
おいて、表面近傍及び中心部近傍の意味は厳密に規定さ
れるものではないが、表面近傍とは大略表面から10%
程度の範囲内であり、中心部近傍とは大略中心から90
%程度の範囲内である。また、硝化菌と脱窒菌の分布は
完全に分けられるものではなく、担体として硝化能及び
脱窒能を有している限り、ある程度、両方の菌が混在す
る領域があっても構わない。
In the water treatment carrier of the present invention, nitrifying bacteria inhabit near the surface and denitrifying bacteria inhabit near the center. In the present invention, the meaning of the vicinity of the surface and the vicinity of the center is not strictly defined, but the meaning of the vicinity of the surface is approximately 10% from the surface.
And the vicinity of the center is approximately 90 degrees from the center.
%. The distribution of nitrifying bacteria and denitrifying bacteria is not completely separated, and there may be a region where both bacteria are mixed to some extent as long as they have nitrifying ability and denitrifying ability as a carrier.

【0024】表面近傍に硝化能を有する微生物が生息
し、中心部近傍に脱窒能を有する微生物が生息している
ことは、例えば遺伝子プロ−ブによるFISH法(fl
uorescent in situ hybridi
zation)により確認することができる。すなわ
ち、FISH法は、対象とする微生物の遺伝子に特異的
に結合する遺伝子プロ−ブを利用する方法であり、この
ような遺伝子プロ−ブを作成し、該遺伝子プロ−ブの片
末端をFITC等の蛍光色素でラベルすることによって
特定の微生物を検出することができる。
The fact that microorganisms having nitrification ability inhabit near the surface and microorganisms having denitrification ability inhabit in the vicinity of the center can be confirmed, for example, by the FISH method using a gene probe (fl
urescent in situ hybridi
zation). That is, the FISH method is a method utilizing a gene probe that specifically binds to a gene of a target microorganism. Such a gene probe is prepared, and one end of the gene probe is FITC. Specific microorganisms can be detected by labeling with such a fluorescent dye.

【0025】アセタール化PVA含水ゲルの形状はとく
に限定されるものではなく、繊維状、サイコロ状、フィ
ルム状、円柱状、中空円筒状、球状、円盤状など任意の
形状に成形したものを使用することができるが、担体の
流動性の点で球状のものが好ましい。
The shape of the acetalized PVA hydrogel is not particularly limited, and a gel formed into an arbitrary shape such as a fibrous shape, a dice shape, a film shape, a columnar shape, a hollow cylindrical shape, a spherical shape, and a disk shape is used. However, spherical ones are preferred from the viewpoint of the fluidity of the carrier.

【0026】本発明の水処理用担体は、硝化能及び脱窒
能を有するため、硝化及び脱窒反応を同時に実施するこ
とができる。すなわち、本発明の水処理用担体を好気性
雰囲気下で流動させることにより、硝化反応が起こり、
また担体内部で脱窒反応が起こるので、1つのリアクタ
−内で排水処理などの水処理を合理的に実施することが
でき、装置をコンパクト化することができる。
Since the water treatment carrier of the present invention has a nitrifying ability and a denitrifying ability, the nitrifying and denitrifying reactions can be carried out simultaneously. That is, by flowing the water treatment carrier of the present invention under an aerobic atmosphere, a nitrification reaction occurs,
Further, since a denitrification reaction occurs inside the carrier, water treatment such as wastewater treatment can be rationally performed in one reactor, and the apparatus can be made compact.

【0027】従来、魚の棲息する水系の浄化は、餌の食
べ残しや排泄物などの固形物を除去する物理濾過と、担
体に微生物を生息させ、餌の食べ残しや排泄物などから
発生するアンモニア性窒素を硝酸性窒素にする生物濾過
がある。生物濾過は、魚にとって有害なアンモニア性窒
素を比較的害の少ない硝酸性窒素に硝化することを目的
とするが、アンモニア性窒素を硝化し続けると、硝酸性
窒素が増え続け、いずれは魚に有害な濃度となり、水を
交換しなければならなくなる。
Conventionally, purification of water systems inhabited by fish has been carried out by physical filtration for removing solids such as food leftovers and excrement, and ammonia generated from food leftovers and excrement by feeding microorganisms on carriers. There is a biofiltration that converts nitrogen into nitrate. Biofiltration aims to nitrify ammonia nitrogen, which is harmful to fish, into nitrate nitrogen, which is relatively harmless.If nitrification of ammonia nitrogen continues, nitrate nitrogen will continue to increase, eventually causing fish It will be harmful and water must be replaced.

【0028】本発明の水処理用担体は、このような魚の
棲息する水系を浄化する場合にも好適に使用することが
できる。すなわち、養殖用・観賞魚用水槽の浄化、生簀
・養殖水域の浄化、活魚輸送水の浄化など、魚の棲息す
る水系の浄化全般に利用することができる。
The water treatment carrier of the present invention can also be suitably used for purifying such a fish-inhabiting water system. In other words, the present invention can be used for general purification of water systems inhabited by fish, such as purification of aquariums for aquaculture and ornamental fish, purification of fish cages and aquaculture water areas, purification of live fish transport water, and the like.

【0029】[0029]

【実施例】以下、実施例により本発明を具体的に説明す
るが、本発明はこれらに限定されるものではない。 実施例1 (株)クラレ製のPVA(平均重合度1700、ケン化
度99.8モル%)6wt%、アルギン酸ナトリウム1
wt%及び炭酸水素ナトリウム0.35wt%からなる
水溶液を調製した。この水溶液を、先端に内径3mmの
ノズルを取り付けた内径4mmのシリコンチュ−ブを装
着したロ−ラ−ポンプにより、5ミリリットル(mL)
/分の速度で送液し、スタ−ラ−で撹拌した濃度0.1
モル/リットル(L)の塩化カルシウム水溶液に滴下し
た。滴下した液滴は塩化カルシウム水溶液中で球状化し
て沈降した。
EXAMPLES The present invention will now be described specifically with reference to examples, but the present invention is not limited to these examples. Example 1 6 wt% of PVA (average degree of polymerization 1700, degree of saponification 99.8 mol%) manufactured by Kuraray Co., Ltd., sodium alginate 1
An aqueous solution consisting of wt% and 0.35 wt% of sodium hydrogen carbonate was prepared. This aqueous solution was supplied to a roller pump equipped with a silicon tube having an inner diameter of 4 mm equipped with a nozzle having an inner diameter of 3 mm at the tip thereof to obtain 5 ml (mL).
/ Min, and agitated with a stirrer at a concentration of 0.1
It was added dropwise to an aqueous solution of calcium chloride at mol / liter (L). The dropped droplets became spherical and settled in the calcium chloride aqueous solution.

【0030】この球状成型物を、ホルムアルデヒド20
g/L、硫酸200g/L、硫酸ナトリウム90g/L
の40℃の水溶液に70分浸漬した後水洗し、直径約4
mmの柔軟性に富んだ球状の含水ゲルを得た。この含水
ゲルのアセタ−ル化度は39モル%、含水率は93%で
あった。光学顕微鏡及び電子顕微鏡により観察した結
果、アセタ−ル化したPVA担体の表面及び内部は網目
構造となっており、担体表面から中心部に直径1〜10
μmの連通孔が無数に存在していた。
[0030] The spherical molded product was treated with formaldehyde 20
g / L, sulfuric acid 200g / L, sodium sulfate 90g / L
Immersed in a 40 ° C. aqueous solution for 70 minutes, washed with water,
Thus, a spherical hydrogel having a thickness of 0.3 mm was obtained. The degree of acetalization of this hydrogel was 39 mol%, and the water content was 93%. As a result of observation with an optical microscope and an electron microscope, the surface and the inside of the acetalized PVA carrier have a network structure, and have a diameter of 1 to 10 from the carrier surface to the center.
There were countless μm communication holes.

【0031】この担体5kgを、脱窒能を有する微生物
が存在する汚泥10L(MLSS3000ppm)に3
日間浸漬後担体を取り出し、TOC100ppm、硝酸
性窒素100ppmに調整した排水10Lに入れ、空気
を巻き込まない程度に撹拌した。約3日間経過後、硝酸
性窒素はほぼ0ppmになり、担体は脱窒能を有するこ
とが確認された。
5 kg of this carrier is added to 10 L (MLSS 3000 ppm) of sludge containing microorganisms having a denitrifying ability.
After immersion for a day, the carrier was taken out, put into 10 L of waste water adjusted to 100 ppm of TOC and 100 ppm of nitrate nitrogen, and stirred to the extent that air was not involved. After about three days, the amount of nitrate nitrogen became almost 0 ppm, and it was confirmed that the carrier had a denitrifying ability.

【0032】さらにこの担体を、硝化能を有する微生物
が存在する汚泥10L(MLSS3000ppm)に3
日間浸漬し曝気した。担体を取り出し、アンモニア性窒
素50ppmに調整した排水10Lに入れ、曝気した。
約1週間経過後、アンモニア性窒素はほぼ0ppmにな
り、担体は硝化能を有することが確認された。
Further, this carrier is added to 10 L of sludge (MLSS 3000 ppm) in which microorganisms having nitrification ability are present.
It was immersed for a day and aerated. The carrier was taken out, put into 10 L of waste water adjusted to 50 ppm of ammonia nitrogen, and aerated.
After about one week, the amount of ammonia nitrogen became almost 0 ppm, and it was confirmed that the carrier had a nitrifying ability.

【0033】この担体を、10Lの曝気槽に入れ、TO
C100ppm、アンモニア性窒素50ppmに調整し
た排水を2L/時で供給した。溶存酸素は1〜3ppm
になるように曝気量を調整した。10日経過後、処理水
の水質を測定したところ、アンモニア性窒素0.0pp
m、亜硝酸性窒素0.2ppm、硝酸性窒素4.9pp
m、TOC5.1ppmであり、良好に硝化脱窒処理す
ることができた。
This carrier was placed in a 10 L aeration tank,
Wastewater adjusted to 100 ppm of C and 50 ppm of ammonia nitrogen was supplied at 2 L / hour. Dissolved oxygen is 1-3 ppm
The aeration amount was adjusted so that After a lapse of 10 days, the quality of the treated water was measured.
m, nitrite nitrogen 0.2 ppm, nitrate nitrogen 4.9 pp
m, the TOC was 5.1 ppm, and the nitrification and denitrification treatment was successfully performed.

【0034】この担体を、100Lの曝気槽に入れ、こ
の曝気槽と1m3 の水槽(魚体数100匹)を接続し、
水を10L/分で循環した。1カ月経過後、水質を測定
したところ、アンモニア性窒素0.1ppm、亜硝酸性
窒素0ppm、硝酸性窒素5.3ppmであり、良好な
水質であった。死亡した魚体はなかった。
This carrier was placed in a 100 L aeration tank, and this aeration tank was connected to a 1 m 3 water tank (100 fish).
Water was circulated at 10 L / min. After one month, when the water quality was measured, it was 0.1 ppm ammonia nitrogen, 0 ppm nitrite nitrogen, and 5.3 ppm nitrate nitrogen, and the water quality was good. No fish died.

【0035】実施例2 PVAとして、平均重合度4000、ケン化度99.8
モル%を使用し、PVA5wt%、アルギン酸ナトリウ
ム1wt%、硫酸ナトリウム0.25wt%からなる水
溶液を0.1モル/Lの塩化カルシウム水溶液に接触さ
せ、シ−ト状に成型した。これをホルムアルデヒド20
g/L、硫酸200g/L、硫酸ナトリウム100g/
Lの40℃の水溶液に60分浸漬した後、水洗した。こ
れを、直径約5mmのサイコロ状に切断し、電子顕微鏡
で観察したところ、表面及び内部に網目構造を有してい
るのが確認され、表面から中心部に直径1〜10μmの
無数の連通孔を有することが認められた。
Example 2 As PVA, the average degree of polymerization was 4000 and the degree of saponification was 99.8.
An aqueous solution consisting of 5% by weight of PVA, 1% by weight of sodium alginate, and 0.25% by weight of sodium sulfate was brought into contact with a 0.1 mol / L aqueous solution of calcium chloride to form a sheet. This is formaldehyde 20
g / L, sulfuric acid 200g / L, sodium sulfate 100g /
L was immersed in a 40 ° C. aqueous solution for 60 minutes, and then washed with water. This was cut into a die having a diameter of about 5 mm and observed with an electron microscope. As a result, it was confirmed that the mesh had a network structure on the surface and inside. Was found to have

【0036】この担体1kgを、(株)クラレ岡山工場
の排水処理槽から採取した活性汚泥10L(MLSS5
000ppm)に3日間浸漬した後、10Lの曝気槽に
入れ、TOC100ppm、アンモニア性窒素50pp
mに調整した排水を2L/時で供給した。溶存酸素は1
〜3ppmになるように曝気量を調整した。30日経過
後、処理水の水質を測定したところ、アンモニア性窒素
0.0ppm、亜硝酸性窒素0.1ppm、硝酸性窒素
6.2ppm、TOC5.5ppmであり、良好に硝化
脱窒処理することができた。
1 kg of this carrier was used for 10 L of activated sludge (MLSS5) collected from a wastewater treatment tank at the Kuraray Okayama Plant.
000 ppm) for 3 days, put into a 10 L aeration tank, TOC 100 ppm, ammonia nitrogen 50 pp
m was supplied at a rate of 2 L / hour. Dissolved oxygen is 1
The aeration amount was adjusted so as to be 3 ppm. After 30 days, the quality of the treated water was measured to be 0.0 ppm of ammoniacal nitrogen, 0.1 ppm of nitrite nitrogen, 6.2 ppm of nitrate nitrogen, and 5.5 ppm of TOC. did it.

【0037】この担体5kgを、(株)クラレ岡山工場
の排水処理槽から採取した活性汚泥100L(MLSS
5000ppm)に3日間浸漬した後、100Lの曝気
槽に入れ、この曝気槽と1m3 の水槽(魚体数100
匹)を接続し、水を10L/分で循環した。1カ月経過
後、水質を測定したところ、アンモニア性窒素0.1p
pm、亜硝酸性窒素0.0ppm、硝酸性性窒素8.7
ppmであり、良好な水質であった。死亡した魚体はな
かった。
5 kg of this carrier was used for 100 L of activated sludge (MLSS) collected from a wastewater treatment tank at the Kuraray Okayama Plant.
5,000 ppm) for 3 days, and then put in a 100 L aeration tank, and this aeration tank and a 1 m 3 water tank (100 fish
And the water was circulated at 10 L / min. After one month, when the water quality was measured, ammonia nitrogen 0.1p
pm, nitrite nitrogen 0.0 ppm, nitrate nitrogen 8.7
ppm and good water quality. No fish died.

【0038】実施例3 PVAとして、平均重合度1700、ケン化度99.8
モル%を使用し、PVA6wt%、アルギン酸ナトリウ
ム1wt%からなる水溶液を0.1モル/Lの塩化カル
シウム水溶液に滴下して球状に成型した。
Example 3 As PVA, the average degree of polymerization was 1700 and the degree of saponification was 99.8.
An aqueous solution consisting of 6 wt% of PVA and 1 wt% of sodium alginate was dropped into a 0.1 mol / L aqueous solution of calcium chloride to form a spherical shape.

【0039】この球状成型物を、ホルムアルデヒド18
g/L、硫酸210g/L、硫酸ナトリウム100g/
Lの40℃の水溶液に60分浸漬した後水洗し、直径約
5mmの柔軟性に富んだ球状の含水ゲルを得た。この含
水ゲルのアセタ−ル化度は39モル%、含水率は93%
であった。光学顕微鏡及び電子顕微鏡により観察した結
果、担体の表面及び内部は網目構造となってるのが観察
され、担体の表面から中心部に直径1〜10μmの連通
孔が無数に存在していた。
This spherical molded product was treated with formaldehyde 18
g / L, sulfuric acid 210 g / L, sodium sulfate 100 g /
L was immersed in an aqueous solution of 40 ° C. for 60 minutes and washed with water to obtain a flexible spherical hydrogel having a diameter of about 5 mm. The degree of acetalization of this hydrogel was 39 mol%, and the water content was 93%.
Met. As a result of observation with an optical microscope and an electron microscope, it was observed that the surface and the inside of the carrier had a network structure, and there were countless communication holes having a diameter of 1 to 10 μm from the surface of the carrier to the center.

【0040】この担体5kgを実施例1と同様に100
Lの曝気槽に入れ、この曝気槽と1m3の水槽(魚体数
100匹)を接続し、水を10L/分で循環した。1カ
月経過後、水質を測定したところ、アンモニア性窒素
0.1ppm、亜硝酸性窒素0ppm、硝酸性性窒素
7.6ppmであり、良好な水質であった。死亡した魚
体はなかった。
5 kg of this carrier was added to 100
L, and the aeration tank was connected to a 1 m 3 water tank (100 fish), and water was circulated at 10 L / min. After one month, when the water quality was measured, it was 0.1 ppm ammonia nitrogen, 0 ppm nitrite nitrogen, and 7.6 ppm nitrate nitrogen, and the water quality was good. No fish died.

【0041】[0041]

【発明の効果】本発明により、硝化能及び脱窒能を有す
るアセタール化されたPVA系の含水ゲル又はポリエチ
レングリコール系の含水ゲルからなる担体を提供するこ
とができる。本発明の担体によれば、硝化能及び脱窒能
の両機能を有しており、有機性排水の硝化及び脱窒を同
時に実施することができるので、合理的で、しかも処理
装置をコンパクト化することができる。
According to the present invention, it is possible to provide a carrier comprising an acetalized PVA-based hydrogel or a polyethylene glycol-based hydrogel having a nitrifying ability and a denitrifying ability. According to the carrier of the present invention, it has both functions of nitrification and denitrification, and can simultaneously perform nitrification and denitrification of organic wastewater. can do.

【図面の簡単な説明】[Brief description of the drawings]

【図1】従来の有機性排水処理装置を示すフロ−チャ−
トである。
FIG. 1 is a flowchart showing a conventional organic wastewater treatment apparatus.
It is.

【符号の説明】[Explanation of symbols]

1 嫌気槽 2 好気槽 3 沈殿槽 4 有機性排水 5 散気装置 6 処理水 DESCRIPTION OF SYMBOLS 1 Anaerobic tank 2 Aerobic tank 3 Sedimentation tank 4 Organic drainage 5 Air diffuser 6 Treated water

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 表面及び/又は内部に網目構造を有する
アセタ−ル化されたポリビニルアルコ−ル系の含水ゲル
又はポリエチレングリコール系の含水ゲルからなる担体
であって、該担体の表面近傍に硝化能を有する微生物が
生息し、中心部近傍に脱窒能を有する微生物が生息して
いることを特徴とする水処理用担体。
1. A carrier comprising an acetalized polyvinyl alcohol-based hydrogel or a polyethylene glycol-based hydrogel having a network structure on the surface and / or inside thereof, wherein nitrification occurs near the surface of the carrier. A carrier for water treatment, wherein microorganisms having the ability are inhabited and microorganisms having the denitrification ability inhabit in the vicinity of the center.
【請求項2】 アセタ−ル化されたポリビニルアルコ−
ル系の含水ゲルがポリビニルホルマ−ル含水ゲルである
請求項1の水処理用担体。
2. Acetalized polyvinyl alcohol
2. The carrier for water treatment according to claim 1, wherein the water-containing gel is a polyvinyl formal water-containing gel.
【請求項3】 アセタ−ル化されたポリビニルアルコ−
ル系の含水ゲル又はポリエチレングリコール系の含水ゲ
ルを脱窒能を有する微生物と接触させ、該微生物が含水
ゲル内部に侵入した後、硝化能を有する微生物と接触さ
せ、該微生物を含水ゲル表面近傍に生息させることを特
徴とするアセタ−ル化されたポリビニルアルコ−ル系の
含水ゲル又はポリエチレングリコール系の含水ゲルから
なる水処理用担体の製造方法。
3. Acetalized polyvinyl alcohol
A hydrogel of polyethylene type or a hydrogel of polyethylene glycol type with a microorganism having a denitrifying ability, and after the microorganisms enter the interior of the hydrogel, contact with a microorganism having a nitrifying ability, thereby bringing the microorganism into the vicinity of the surface of the hydrogel. A method for producing a water treatment carrier comprising an acetalized polyvinyl alcohol-based hydrogel or a polyethylene glycol-based hydrogel, wherein the water-treating carrier is acetalized.
【請求項4】 表面近傍に硝化能を有する微生物が生息
し、中心部近傍に脱窒能を有する微生物が生息している
アセタ−ル化されたポリビニルアルコ−ル系の含水ゲル
又はポリエチレングリコール系の含水ゲルからなる水処
理用担体を用いて有機性排水の硝化脱窒を同時に行うこ
とを特徴とする硝化脱窒方法。
4. Acetalized polyvinyl alcohol-based hydrogel or polyethylene glycol-based microorganism in which a microorganism having a nitrifying ability inhabits near the surface and a microorganism having a denitrifying ability inhabits near the center. A nitrification and denitrification method for organic wastewater using a water treatment carrier comprising a water-containing gel.
JP13191797A 1997-05-22 1997-05-22 Water treatment carrier, production method thereof, and nitrification denitrification method using the same Expired - Lifetime JP3686215B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13191797A JP3686215B2 (en) 1997-05-22 1997-05-22 Water treatment carrier, production method thereof, and nitrification denitrification method using the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13191797A JP3686215B2 (en) 1997-05-22 1997-05-22 Water treatment carrier, production method thereof, and nitrification denitrification method using the same

Publications (2)

Publication Number Publication Date
JPH10314782A true JPH10314782A (en) 1998-12-02
JP3686215B2 JP3686215B2 (en) 2005-08-24

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Country Status (1)

Country Link
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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001005877A1 (en) * 1999-07-15 2001-01-25 Kuraray Co., Ltd. Aqueous polyvinyl alcohol gel, process for producing the same, and wastewater treatment apparatus
US6551511B1 (en) 1999-05-31 2003-04-22 Matsushita Electric Industrial Co. Ltd. Denitrification promoter and a method of water treatment using the same
JP2009208024A (en) * 2008-03-05 2009-09-17 Nippon Kensetsu Gijutsu Kk Water purification apparatus
US9212358B2 (en) 2012-06-15 2015-12-15 Microvi Biotech, Inc. Biocatalyst compositions and processes for their use
US9255281B2 (en) 2012-06-15 2016-02-09 Microvi Biotech Inc. Bioconversion processes using water-insoluble liquids
US9334507B2 (en) 2012-06-15 2016-05-10 Microvi Biotech, Inc. Bioprocesses for making butanol
US9752164B2 (en) 2012-06-15 2017-09-05 Microvi Biotech, Inc. Enhanced efficiency ethanol and sugar conversion processes
CN111099741A (en) * 2018-10-26 2020-05-05 中国石油化工股份有限公司 Method for improving denitrification effect of nitrification and denitrification process
WO2021182603A1 (en) * 2020-03-13 2021-09-16 株式会社クラレ Wastewater treatment method

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6551511B1 (en) 1999-05-31 2003-04-22 Matsushita Electric Industrial Co. Ltd. Denitrification promoter and a method of water treatment using the same
WO2001005877A1 (en) * 1999-07-15 2001-01-25 Kuraray Co., Ltd. Aqueous polyvinyl alcohol gel, process for producing the same, and wastewater treatment apparatus
JP2009208024A (en) * 2008-03-05 2009-09-17 Nippon Kensetsu Gijutsu Kk Water purification apparatus
US9212358B2 (en) 2012-06-15 2015-12-15 Microvi Biotech, Inc. Biocatalyst compositions and processes for their use
US9255281B2 (en) 2012-06-15 2016-02-09 Microvi Biotech Inc. Bioconversion processes using water-insoluble liquids
US9334507B2 (en) 2012-06-15 2016-05-10 Microvi Biotech, Inc. Bioprocesses for making butanol
US9752164B2 (en) 2012-06-15 2017-09-05 Microvi Biotech, Inc. Enhanced efficiency ethanol and sugar conversion processes
CN111099741A (en) * 2018-10-26 2020-05-05 中国石油化工股份有限公司 Method for improving denitrification effect of nitrification and denitrification process
WO2021182603A1 (en) * 2020-03-13 2021-09-16 株式会社クラレ Wastewater treatment method

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