JPH0716586A - Organism fixing carrier for waste water treatment, method and apparatus for clarifying waste water - Google Patents

Organism fixing carrier for waste water treatment, method and apparatus for clarifying waste water

Info

Publication number
JPH0716586A
JPH0716586A JP5161585A JP16158593A JPH0716586A JP H0716586 A JPH0716586 A JP H0716586A JP 5161585 A JP5161585 A JP 5161585A JP 16158593 A JP16158593 A JP 16158593A JP H0716586 A JPH0716586 A JP H0716586A
Authority
JP
Japan
Prior art keywords
sewage
carrier
waste water
biological
raw material
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
JP5161585A
Other languages
Japanese (ja)
Other versions
JP3252158B2 (en
Inventor
Masayoshi Iwasaki
正良 岩崎
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.)
DAISEI SANGYO KK
Original Assignee
DAISEI SANGYO KK
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 DAISEI SANGYO KK filed Critical DAISEI SANGYO KK
Priority to JP16158593A priority Critical patent/JP3252158B2/en
Publication of JPH0716586A publication Critical patent/JPH0716586A/en
Application granted granted Critical
Publication of JP3252158B2 publication Critical patent/JP3252158B2/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

  • Biological Treatment Of Waste Water (AREA)

Abstract

PURPOSE:To improve the clarification efficiency of waste water by increasing the deposition and proliferation rate of organism by giving a flocking treatment on the surface, which contacts at least waste water, of a solid carrier raw material which forms an organism fixing solid carrier for clarifying waste water by biological treatment. CONSTITUTION:This organism fixing carrier used for an apparatus for clarifying dirty water in a river polluted with waste water of various kinds by biological treatment is prepared by a method in which flocking process is provided on the surface, which contacts at least waste water, of a solid carrier raw material selected from crushed stone, ceramics, blast furnace slag, ceramic pieces, pulverized concrete block, plastics, and so forth. Fibers of a nylon, cotton, a polyethylene, and others, in particular, fibers having a porous core indicating capillarity are preferably used as flocks. More than one solid carrier raw material is bonded together forming spaces between the solids to penetrates them. The carrier is loaded with microorganisms for treating waste water and nutriment for the microorganisms.

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、工業廃水、生活廃水等
の汚水又はこれら各種廃水により汚染された河川等にお
ける汚水を、生物的処理により浄化するための汚水処理
用生物固定担体、該生物固定担体を使用した汚水浄化方
法及び汚水浄化装置に関する。
FIELD OF THE INVENTION The present invention relates to an organism-fixing carrier for sewage treatment for purifying sewage such as industrial effluent, household effluent or the like or sewage in rivers contaminated by these various effluents by biological treatment. The present invention relates to a wastewater purification method and a wastewater purification device using a fixed carrier.

【0002】[0002]

【従来の技術】各種廃水又は河川等における汚水の浄化
方法として、従来から微生物により処理する生物的処理
方法が知られている。このような生物的処理方法として
は、活性汚泥又は生物固定担体に微生物を保持させ、汚
水を接触処理し、フロック状等にして沈澱又は分離除去
する方法が提案され実施されている。このような生物固
定担体としては、例えば表面積の大きい繊維状物で形成
された生物膜、不織布成形物又はロープ;活性炭、ゼオ
ライト、モスピート等の多孔性物質;棒状のプラスチッ
ク物に表面積の大きい特殊合成繊維を螺旋状に絡ませた
形態物;2以上の採石を集合接合し、細孔を形成した砕
石集合体等が提案されている他、礫間接触酸化法を行な
うために、河川等の底床に直接礫を敷設した礫床、複数
の汚水流入出口を設けたコンクリート箱体内に砕石を複
数個充填したもの等も提案されている。
2. Description of the Related Art As a method for purifying various kinds of waste water or sewage in rivers, a biological treatment method of treating with a microorganism has been known. As such a biological treatment method, a method has been proposed and carried out in which microorganisms are held in activated sludge or a biological fixed carrier, sewage is subjected to contact treatment, and flocculated to precipitate or separate and remove. Such bio-immobilized carriers include, for example, biofilms formed of fibrous materials having a large surface area, non-woven fabric moldings or ropes; porous materials such as activated carbon, zeolite, and mospite; special synthetic materials having a large surface area on rod-shaped plastic materials. Form in which fibers are entwined in a spiral shape; crushed stone aggregates in which two or more quarries are aggregated and joined to form pores are proposed, and in order to perform the inter-gravel catalytic oxidation method, the bottom floor of rivers, etc. It has also been proposed that a gravel bed directly laying gravel on it, a concrete box body having a plurality of wastewater inflow / outflow ports filled with a plurality of crushed stones, and the like.

【0003】しかしながら、前記多孔性物質若しくは砕
石等を利用する方法では、微生物の固定が未だ十分でな
かったり、十分であっても汚水処理後のフロック状物の
沈澱、除去が煩雑であったりする等の問題がある。一方
前記繊維を利用した生物固定担体の場合には、十分な微
生物の固定ができ、しかも汚水処理後のフロック状物の
剥離若しくは沈澱も容易に行なうことができるが、汚水
流に浮遊させたり、特殊な装置に固定しなければならな
かったりするため、設置箇所が限定され、しかも設置方
法が煩雑化する等の問題がある。
However, in the method using the above-mentioned porous material or crushed stone, immobilization of microorganisms is still insufficient, or even if it is sufficient, precipitation and removal of floc-like substances after wastewater treatment are complicated. There is a problem such as. On the other hand, in the case of a bio-immobilized carrier using the fibers, sufficient microorganisms can be immobilized, and the flocs can be easily peeled off or precipitated after the sewage treatment, but they may be suspended in the sewage stream, Since it has to be fixed to a special device, there are problems that the installation location is limited and the installation method becomes complicated.

【0004】[0004]

【発明が解決しようとする課題】従って本発明の目的
は、微生物の付着率及び増殖率が極めて高く、また好気
性及び嫌気性微生物をバランス良く付着させることがで
き、効率良く汚水を浄化することが可能な汚水浄化用生
物固定担体、汚水浄化方法又は汚水浄化装置を提供する
ことにある。
SUMMARY OF THE INVENTION Therefore, an object of the present invention is to have an extremely high rate of attachment and growth of microorganisms, to attach aerobic and anaerobic microorganisms in a well-balanced manner, and to efficiently purify wastewater. An object of the present invention is to provide a biological fixed carrier for sewage purification, a sewage purification method, or a sewage purification device.

【0005】本発明の別の目的は、汚水処理により発生
するフロック状物の除去が容易な汚水浄化用生物固定担
体、汚水浄化方法又は汚水浄化装置を提供することにあ
る。
Another object of the present invention is to provide a biological fixed carrier for sewage purification, a sewage purification method, or a sewage purification device, in which flocs generated by sewage treatment can be easily removed.

【0006】[0006]

【課題を解決するための手段】本発明によれば、汚水を
生物的処理により浄化する生物固定担体であって、該担
体を形成する担体原料固形物の少なくとも汚水と接触す
る表面が植毛処理されてなることを特徴とする汚水処理
用生物固定担体が提供される。
According to the present invention, there is provided a biological fixed carrier for purifying sewage by biological treatment, wherein at least the surface of the solid carrier raw material forming the carrier, which is in contact with sewage, is subjected to flocking treatment. A biological fixed carrier for sewage treatment is provided.

【0007】また本発明によれば、前記汚水処理用生物
固定担体に、汚水を流通接触させて生物的浄化処理する
ことを特徴とする汚水浄化方法が提供される。
Further, according to the present invention, there is provided a sewage purification method characterized in that sewage is brought into flow contact with the biological fixed carrier for sewage treatment for biological purification treatment.

【0008】更に本発明によれば、前記汚水処理用生物
固定担体を、汚水の流入出口を設けた枠体内に、汚水と
接触するよう配置したことを特徴とする汚水浄化装置が
提供される。
Further, according to the present invention, there is provided a sewage purification apparatus characterized in that the sewage treatment biological fixed carrier is arranged in a frame body provided with an inflow / outflow port of the sewage so as to come into contact with the sewage.

【0009】以下本発明を更に詳細に説明する。The present invention will be described in more detail below.

【0010】本発明の汚水浄化用生物固定担体は、例え
ば、砕石、セラミック、高炉滓、陶磁片、粉砕コンクリ
ートブロック、プラスチック等の担体原料固形物の少な
くとも汚水と接触する表面に、植毛を施したものであ
る。
The biological fixed carrier for purifying sewage of the present invention is, for example, crushed stone, ceramic, blast furnace slag, porcelain pieces, crushed concrete block, plastic, etc. It is a thing.

【0011】前記担体原料固形物の材質、大きさ、形状
等は水中に浮上しない比重を有しておれば特に限定され
るものではないが、通常大きさは、平均径1〜30cm
であるのが好ましい。また担体原料固形物は、単体であ
っても良いが、好ましくは複数の担体原料固形物の単体
を、セメント、接着剤等により接合し、各担体原料固形
物単体の間隙によって、内外部を連通する連通気孔を形
成した集合体等であるのが好ましい。即ち該集合体と
は、担体原料固形物の単体表面部分の全てが密着せず、
接合部分以外の各担体原料固形物の単体面により形成さ
れる間隙が、集合体の内外部を連通する連通気孔となっ
た集合体であれば良い。
The material, size, shape, etc. of the solid carrier raw material are not particularly limited as long as they have a specific gravity that does not float in water, but the normal size is usually an average diameter of 1 to 30 cm.
Is preferred. The carrier raw material solid may be a single substance, but preferably, a plurality of carrier raw material solid substances are joined by cement, an adhesive or the like, and the inside and outside are communicated with each other by the gap between the carrier raw material solid substances. It is preferably an aggregate or the like in which continuous ventilation holes are formed. That is, the aggregate does not adhere to all of the surface portion of the solid material of the carrier raw material,
It is sufficient that the gap formed by the single surface of each solid solid material of the carrier other than the joint portion is a communicating hole that communicates the inside and outside of the collecting body.

【0012】前記担体原料固形物の単体を接合する接着
剤としては、材質に応じて公知の接着剤を用いることが
できるが、特に陶磁片等の産業廃棄物を接着するには、
エポキシ系のポリマーモルタル接着剤等を好ましく用い
ることができる。この際各担体原料固形物の間隙によっ
て形成される気孔は、必ずしもその全てが連通気孔であ
る必要はなく、内部で閉塞状態となっている気孔を備え
ていても良い。また気孔径は、1mm以上、特に1〜5
mmが好ましく、更に気孔率は70%以上、特に70〜
90%であるのが好ましい。
As the adhesive agent for bonding the solid material of the carrier raw material, a known adhesive agent can be used depending on the material. Particularly, for adhering industrial waste such as ceramic pieces,
Epoxy polymer mortar adhesives and the like can be preferably used. At this time, all the pores formed by the gaps of the solid materials of the carrier raw materials do not necessarily have to be the continuous ventilation holes, and may have the pores that are closed inside. The pore diameter is 1 mm or more, especially 1 to 5
mm is preferable, and the porosity is 70% or more, particularly 70 to
It is preferably 90%.

【0013】前記担体原料固形物の単体又は集合体の少
なくとも汚水と接触する表面に施す植毛は、例えばナイ
ロン、レーヨン、綿、ポリエチレン、ポリプロピレン、
アクリル等の繊維物、特に好ましくは、繊維内部が多孔
質であり、通気性を有し、毛細管現象の作用を示し、水
を吸収する機能を有する、例えば商品名「アクワロン」
(カネボウ株式会社製)等の多孔質の繊維物等を接着さ
せることにより行なうことができる。前記繊維物の繊維
径は3〜15デニルが好ましく、繊維長は3〜10mm
が望ましい。繊維長が3mm未満の場合には微生物の付
着量が十分でなく、10mmを超える場合には微生物の
フロックが剥がれやすくなるので好ましくない。また繊
維物の植毛量は、50〜200g/cm2であるのが望
ましい。この際少なくとも汚水と接触する表面に施す植
毛とは、担体原料固形物が単体であれば表面全体若しく
は、河川の底床に敷設する場合には、該底床と接触する
部分を除く表面に植毛されておれば良く、また担体原料
固形物が集合体である場合には、集合体の表面に植毛さ
れておれば十分であり、必ずしも汚水が通水する内部の
気孔内表面まで植毛されていなくても良い。
The flocking applied to at least the surface of the solid material of the carrier raw material or the aggregate which comes into contact with the dirty water is, for example, nylon, rayon, cotton, polyethylene, polypropylene,
A fibrous material such as acrylic, particularly preferably, the inside of the fiber is porous, has air permeability, exhibits a capillary action, and has a function of absorbing water, for example, trade name "Aqualon"
This can be performed by adhering a porous fiber material such as (manufactured by Kanebo Co., Ltd.). The fiber diameter of the fiber material is preferably 3 to 15 denier, and the fiber length is 3 to 10 mm.
Is desirable. If the fiber length is less than 3 mm, the amount of adhered microorganisms is not sufficient, and if it exceeds 10 mm, the flocs of microorganisms are easily peeled off, which is not preferable. Further, it is desirable that the amount of fibers to be transplanted is 50 to 200 g / cm 2 . In this case, at least flocking applied to the surface that comes into contact with the dirty water means flocking on the entire surface if the carrier raw material solid is a single substance or, in the case of laying on the bottom floor of a river, on the surface excluding the part that comes into contact with the bottom floor. If the solid material of the carrier raw material is an aggregate, it is sufficient that the surface of the aggregate is flocked, and it is not always necessary to flock the inner surface of the pores through which sewage passes. May be.

【0014】前記植毛処理を行なうには、例えば担体原
料固形物の植毛する部分に、公知のエマルジョン型又は
ソルベント型接着剤、具体的にはビニル系、エチレン
系、アクリル系、メラミン系、ウレタン系、エポキシ
系、ポリエステル系、酢酸ビニル系、ポリアミド系、ゴ
ム系、シリコン系等の接着剤を塗布し、次いで例えば静
電植毛等により必要量の繊維物を植毛する方法等により
行なうことができる。この際、担体原料固形物の単体に
植毛する場合には、少なくとも汚水に接触する表面に植
毛すれば良いが、担体原料固形物の集合体に植毛するに
は、集合体とした後に植毛する他、各担体原料固形物の
単体に植毛した後、該植毛された単体を接合して集合体
としても良い。
To carry out the above-mentioned flocking treatment, for example, a known emulsion-type or solvent-type adhesive, specifically vinyl-based, ethylene-based, acrylic-based, melamine-based, urethane-based, is applied to the flocked portion of the solid carrier raw material. , Epoxy, polyester, vinyl acetate, polyamide, rubber, silicone or the like may be applied, and then a required amount of fibrous material may be flocked by, for example, electrostatic flocking. At this time, in the case of flocking the carrier raw material solids alone, at least the surface contacting the sewage may be flocked. In order to flock the aggregates of the carrier raw material solids, the flocking is performed after forming the aggregates. Alternatively, after flocking the individual solid material of each carrier material, the flocked single elements may be joined together to form an aggregate.

【0015】本発明の汚水処理用生物固定担体は、前記
植毛された担体原料固形物の単体又は集合体を、汚水と
接触させる箇所に配置することにより使用することがで
きるが、汚水処理を更に効率良く行なうために、予め生
物処理を行なう微生物及び/又は該微生物の栄養源、具
体的にはアンモニウム塩、亜硝酸塩、硝酸塩、リン酸塩
等を植毛部分に保持させた後使用に供することもでき
る。微生物及び/又は該微生物の栄養源を汚水処理用生
物固定担体に保持させるには、例えば微生物及び/又は
該微生物の栄養源を含む溶液に浸漬させるか、若しくは
該溶液を散布する方法等により行なうことができる。
The biological fixed carrier for treating sewage of the present invention can be used by arranging the above-mentioned flocked carrier raw material solid material alone or in an aggregate at a position where it is brought into contact with sewage. In order to carry out efficiently, microorganisms to be biologically treated and / or nutrient sources of the microorganisms, specifically ammonium salts, nitrites, nitrates, phosphates, etc. may be retained on the hair-implanted portion before being used. it can. In order to retain the microorganisms and / or the nutrient source of the microorganisms on the biological fixed carrier for treating sewage, it is carried out by, for example, immersing in a solution containing the microorganisms and / or the nutrient source of the microorganisms, or by spraying the solution. be able to.

【0016】本発明の汚水浄化方法は、前記汚水処理用
生物固定担体に、汚水を流通接触させることができれ
ば、公知の方法等により適当な箇所に配置して行なうこ
とができる。具体的には例えば、汚水処理生物固定担体
を、従来の礫間接触酸化処理における砂利、砕石等の礫
の代わりに配設する方法、河川の底床に直接敷設させる
方法、汚水の流入出口を設けた、箱体、導管、カラム等
の枠体内に前記汚水処理用生物固定担体を充填若しくは
汚水と接触する箇所に配置した汚水浄化装置を、汚水が
流通する河川又は工業用廃水、生活廃水等の廃水流通管
内、若しくは河川の流水を分岐させて汚水処理する公知
の方法における砕石等の代わりに配設する方法等によ
り、汚水を前記生物固定担体に接触させることができ
る。
The method for purifying sewage of the present invention can be carried out by arranging it at an appropriate place by a known method, etc., if sewage can be brought into flow contact with the biological fixed carrier for treating sewage. Specifically, for example, a sewage treatment organism fixed carrier, a method of arranging instead of gravel such as gravel and crushed stone in the conventional gravel contact oxidation treatment, a method of laying directly on the bottom floor of the river, inflow and outflow of sewage A box, conduit, column, or other such frame body is filled with the sewage treatment biological immobilization carrier or is disposed at a location that comes into contact with sewage, and a sewage purification device is installed in a river or industrial wastewater through which sewage flows, domestic wastewater, etc. The sewage can be brought into contact with the organism-fixing carrier by a method of arranging in place of crushed stone or the like in a known method of sewage treatment by branching the effluent of a wastewater distribution pipe or the flowing water of a river.

【0017】この際前記生物固定担体は、水に浮遊しな
いのでその設置方法は従来の砕石等と同様に行なうこと
ができる。また前記生物固定担体は、植毛を有するので
効率良く微生物を付着させ、汚水を生物的処理する。生
物的処理された汚水物は、フロック状となって植毛され
た繊維物に付着するが、該フロック状物がある程度(汚
水の流速、フロック状物の重量等に左右されるが)増量
成長すると植毛された部分から自然に剥離して沈澱若し
くは流れるので、生物固定担体からフロック状物を剥離
する作業を行なう必要がない。従って設置方法によって
は、半永久的に使用することもできる。
At this time, since the organism-fixing carrier does not float in water, it can be installed in the same manner as conventional crushed stone. Also, since the biological fixing carrier has hair transplants, microorganisms are efficiently attached to the biological fixed carrier to biologically treat the sewage. The biologically treated wastewater adheres to the fibrous material that has been flocculated and flocked, but when the flocs grow to some extent (depending on the flow rate of the wastewater, the weight of the flocs, etc.) There is no need to perform the work of peeling the floc-like material from the biological fixed carrier, because it spontaneously peels from the planted portion and precipitates or flows. Therefore, it can be used semipermanently depending on the installation method.

【0018】本発明の汚水浄化装置は、前述のとおり、
汚水の流入出口を設けた、箱体、導管、カラム等の枠体
内に前記汚水処理用生物固定担体を充填若しくは汚水と
接触する箇所に配置したものであり、またこのような汚
水処理用生物固定担体を有する枠体を複数組み合わせた
物であっても良い。
The sewage purification apparatus of the present invention is as described above.
The sewage inflow / outflow port is provided, and the box, conduit, column, or other frame body is filled with the sewage treatment organism-immobilizing carrier or disposed at a position in contact with sewage. It may be a combination of a plurality of frame bodies having a carrier.

【0019】前記枠体に設けた汚水の流入出口は、各々
1箇所づつでも良いが、枠体内の汚水の流れをなるべく
一定方向とせずに、好ましくは生物的処理をより効率的
に行なうように汚水の流れを変化させ曝気状態を作り出
すため、複数設けるのが好ましく、特に流入出口の形状
を変えたり、また同じ形状であっても例えば楕円形状の
口を縦、横、斜め等の種々の方向に配置することにより
曝気状態を作り出すことができる。更にこのような曝気
状態を、公知の機械的方法により作り出す装置を付加し
ても良く、また枠体内の生物固定担体を、段差を設けて
配置する方法等によっても曝気状態を作り出すことがで
きる。
The sewage inflow and outflow ports provided in the frame body may be provided at one place each, but the sewage flow in the frame body is preferably not directed in a constant direction as much as possible, and preferably the sewage water is more efficiently used for biological treatment. In order to change the flow of water and create an aeration state, it is preferable to provide a plurality of them. In particular, the shape of the inflow / outlet may be changed, or even if the shape is the same, for example, an elliptical mouth can be formed in various directions such as vertical, horizontal, and diagonal. An aeration state can be created by arranging them. Further, a device for creating such an aerated state by a known mechanical method may be added, and the aerated state can also be created by a method of disposing the biological fixed carrier in the frame with steps.

【0020】本発明の汚水浄化装置において、枠体内に
配置する前記汚水処理用生物固定担体の量は、特に限定
されるものではなく、汚水の流速等により異なるが、好
ましくは接触時間が10〜15分となる量配置するのが
望ましい。
In the sewage purification apparatus of the present invention, the amount of the sewage treatment biologically fixed carrier placed in the frame body is not particularly limited, and varies depending on the flow rate of sewage, but the contact time is preferably 10 to 10. It is desirable to arrange the amount to be 15 minutes.

【0021】[0021]

【発明の効果】本発明の汚水処理用生物固定担体は、少
なくとも汚水と接触する表面に植毛が施されているの
で、微生物の付着率及び増殖率に優れる。また汚水処理
用生物固定担体が、複数の担体原料固形物を接合した集
合体である場合、若しくはその単体を複数枠体に充填し
た場合等においては、各単体の間隙により形成される異
なる気孔径の気孔を流通する汚水の流速が相違するの
で、好気性及び嫌気性微生物をバランス良く付着させる
ことができ、より効率的に汚水を浄化させることができ
る。しかも浄化された後のフロック状物は、植毛部分か
ら自然剥離するのでメンテナンスフリーで使用すること
もできる。一方本発明の汚水浄化方法及び汚水浄化装置
では、前記汚水処理用生物固定担体を使用するので、従
来の生物固定担体を使用した方法又は装置に比して効率
良く汚水の浄化を行なうことができる。
EFFECTS OF THE INVENTION The biological fixed carrier for treating sewage of the present invention is excellent in the attachment rate and the growth rate of microorganisms because at least the surface in contact with sewage is flocked. Further, when the biological fixed carrier for treating wastewater is an aggregate in which a plurality of carrier raw material solids are joined, or when a single body of the solid fixed body is filled in a plurality of frames, etc., different pore diameters formed by the gaps of the single bodies. Since the flow rates of the sewage flowing through the pores are different, aerobic and anaerobic microorganisms can be attached in a well-balanced manner, and the sewage can be purified more efficiently. Moreover, since the floc-like material after purification is naturally peeled off from the flocked portion, it can be used without maintenance. On the other hand, in the sewage purification method and the sewage purification device of the present invention, since the biological fixed carrier for treating sewage is used, the sewage can be efficiently purified as compared with the conventional method or device using the biological fixed carrier. .

【0022】[0022]

【実施例】以下実施例及び比較例により更に詳細に説明
するが、本発明はこれらに限定されるものではない。
EXAMPLES The present invention will be described in more detail with reference to Examples and Comparative Examples below, but the present invention is not limited thereto.

【0023】[0023]

【実施例1】20×35×40mmの表面に凹凸を有す
る産業廃棄物である陶磁片表面に、商品名「TSKモル
タルボンド」(大晴産業株式会社製)の接着剤を塗布し
た。次いで繊維長3mm、繊維径20デニルの吸水性ア
クリル繊維(商品名「アクワロン」、カネボウ株式会社
製)を、50g/cm2の割合で、静電植毛機(メサッ
ク社製)を用いて静電植毛し、生物固定担体を調製し
た。次いで得られた生物固定担体45個を、図1に示す
汚水流入口2及び汚水流出口3を備えた400×650
×450cmの箱体1に、ランダムに充填した。次に、
流速250mm/sで、汚水を3日間流した後、汚水流
入口2及び汚水流出口3における汚水のBOD(生物化
学的酸素消費量)、SS(浮遊物質)及びCOD(化学
的酸素消費量)を測定した。その結果を表1に示す。ま
た前記汚水を10日間流通した後、生物固定担体を観察
したところ植毛部分に10mm幅のフロック状物が付着
しており、更に15日間汚水を流通させたところ、フロ
ック状物が自然剥離した。
Example 1 An adhesive of trade name "TSK Mortar Bond" (manufactured by Taisei Sangyo Co., Ltd.) was applied to the surface of a ceramic piece, which is an industrial waste having irregularities on the surface of 20 × 35 × 40 mm. Next, electrostatically absorb water-absorbing acrylic fiber (product name "Aqualon", manufactured by Kanebo Ltd.) having a fiber length of 3 mm and a fiber diameter of 20 densi at a rate of 50 g / cm 2 by using an electrostatic flocking machine (manufactured by Mesac). The hair was transplanted to prepare a biological fixed carrier. Then, the obtained 45 biological fixed carriers were used as 400 × 650 equipped with the wastewater inlet 2 and the wastewater outlet 3 shown in FIG.
The box 1 of × 450 cm was randomly filled. next,
After flowing sewage at a flow rate of 250 mm / s for 3 days, BOD (biochemical oxygen consumption), SS (suspended substances) and COD (chemical oxygen consumption) of sewage at sewage inlet 2 and sewage outlet 3 Was measured. The results are shown in Table 1. Further, when the biological fixed carrier was observed after circulating the sewage for 10 days, a flock-like substance having a width of 10 mm was attached to the flocked portion, and when the sewage was allowed to flow for another 15 days, the floc-like substance spontaneously peeled off.

【0024】[0024]

【実施例2】平均40×30×20mmの表面に凹凸を
有する産業廃棄物である複数の陶磁片表面に、商品名
「TSKモルタルボンド」(大晴産業株式会社製)のエ
ポキシ系ポリマーモルタル接着剤を塗布した後、各々の
面が完全接合しないように貼着し、直径約20cm程度
の陶磁片集合体を調製した。得られた集合体は、各陶磁
片の間隙により1〜5mmの多数の気孔が形成されてお
り、そのいくつかは集合体の内外を連通する気孔であっ
た。次いでこの集合体表面に、実施例1と同様に植毛を
行なって生物固定担体を作製後、実施例1と同様な箱体
1にランダムに充填し各測定を行なった。その結果を表
1に示す。また前記汚水を10日間流通した後、生物固
定担体を観察したところ植毛部分に10mm幅のフロッ
ク状物が付着しており、更に15日間汚水を流通させた
ところ、フロック状物が自然剥離した。
[Example 2] Epoxy polymer mortar bonding under the trade name "TSK mortar bond" (manufactured by Taisei Sangyo Co., Ltd.) on the surface of a plurality of ceramic pieces, which are industrial wastes having an average surface of 40 x 30 x 20 mm with irregularities After the agent was applied, the surfaces were adhered so that the respective surfaces were not completely joined, and a ceramic piece aggregate having a diameter of about 20 cm was prepared. In the obtained aggregate, a large number of pores of 1 to 5 mm were formed due to the gaps between the respective ceramic pieces, and some of them were pores communicating the inside and outside of the aggregate. Then, on the surface of this aggregate, hair was transplanted in the same manner as in Example 1 to prepare a biological fixed carrier, and then the same box 1 as in Example 1 was randomly filled and each measurement was performed. The results are shown in Table 1. Further, when the biological fixed carrier was observed after circulating the sewage for 10 days, a flock-like substance having a width of 10 mm was attached to the flocked portion, and when the sewage was allowed to flow for another 15 days, the floc-like substance spontaneously peeled off.

【0025】[0025]

【実施例3】実施例2で作製した生物固定担体に、微生
物栄養源アンモニウム塩を散布した以外は、実施例2と
同様に行なって各測定を行なった。その結果を表1に示
す。また前記汚水を10日間流通した後、生物固定担体
を観察したところ植毛部分に30mm幅のフロック状物
が付着しており、更に15日間汚水を流通させたとこ
ろ、フロック状物が自然剥離した。
[Example 3] Each measurement was performed in the same manner as in Example 2 except that the microorganism-fixing source ammonium salt was sprayed on the biological fixed carrier prepared in Example 2. The results are shown in Table 1. Also, when the biological fixed carrier was observed after circulating the sewage for 10 days, a flock-like substance having a width of 30 mm was adhered to the flocked portion, and when the sewage was allowed to flow for another 15 days, the flock-like substance spontaneously peeled off.

【0026】[0026]

【比較例1】実施例2で作製した集合体に植毛を施さな
かった以外は、実施例2と同様に行なって各測定を行な
った。その結果を表1に示す。また前記汚水を10日間
流通した後、生物固定担体を観察したところ、集合体表
面全体ではなく、まばらにフロック状物が付着してお
り、更に15日間汚水を流通させたがフロック状物は自
然剥離せず、エアーガンによりフロック状物の除去を試
みたが、全てを剥離することはできなかった。
Comparative Example 1 Each measurement was performed in the same manner as in Example 2 except that the aggregate produced in Example 2 was not flocked. The results are shown in Table 1. Further, when the biological fixed carrier was observed after circulating the sewage for 10 days, the floc-like substances adhered to the sparsely instead of the entire surface of the aggregate, and the sewage was allowed to circulate for 15 days, but the floc-like substances were natural. An attempt was made to remove the flock-like material with an air gun without peeling, but it was not possible to peel all.

【0027】[0027]

【表1】 [Table 1]

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

【図1】図1は、実施例及び比較例に使用した生物固定
担体を充填する箱体を示す斜視図である。
FIG. 1 is a perspective view showing a box body filled with a biological fixed carrier used in Examples and Comparative Examples.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 汚水を生物的処理により浄化する生物固
定担体であって、該担体を形成する担体原料固形物の少
なくとも汚水と接触する表面が植毛処理されてなること
を特徴とする汚水処理用生物固定担体。
1. A biological fixed carrier for purifying sewage by biological treatment, characterized in that at least the surface of the solid carrier raw material forming the carrier, which is in contact with sewage, is subjected to flocking treatment. Biologically fixed carrier.
【請求項2】 前記生物固定担体が、複数の担体原料固
形物を接合し、各担体原料固形物の間隙によって、少な
くとも内外部を連通する連通気孔を形成してなることを
特徴とする請求項1記載の汚水処理用生物固定担体。
2. The biological fixed carrier is formed by joining a plurality of carrier raw material solids, and forming communication holes at least between the inside and the outside by the gaps between the carrier raw material solids. 1. The biological fixed carrier for treating sewage according to 1.
【請求項3】 前記生物固定担体が、汚水処理を行なう
微生物及び/又は該微生物の栄養源を保持してなること
を特徴とする請求項1又は2記載の汚水処理用生物固定
担体。
3. The biological fixed carrier for sewage treatment according to claim 1 or 2, wherein the biological fixed carrier holds a microorganism for treating sewage and / or a nutrient source of the microorganism.
【請求項4】 請求項1〜3のいずれか1項記載の汚水
処理用生物固定担体に、汚水を流通接触させて生物的浄
化処理することを特徴とする汚水浄化方法。
4. A method for purifying biological wastewater, which comprises biologically purifying treatment by bringing wastewater into circulation contact with the biological fixed carrier for treating wastewater according to any one of claims 1 to 3.
【請求項5】 請求項1〜3のいずれか1項記載の汚水
処理用生物固定担体を、汚水の流入出口を設けた枠体内
に、汚水と接触するよう配置したことを特徴とする汚水
浄化装置。
5. A sewage purification characterized in that the biological fixed carrier for sewage treatment according to any one of claims 1 to 3 is arranged so as to come into contact with sewage in a frame body provided with an inlet / outlet for sewage. apparatus.
JP16158593A 1993-06-30 1993-06-30 Biological fixed carrier for sewage treatment, sewage purification method and sewage purification device Expired - Lifetime JP3252158B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16158593A JP3252158B2 (en) 1993-06-30 1993-06-30 Biological fixed carrier for sewage treatment, sewage purification method and sewage purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16158593A JP3252158B2 (en) 1993-06-30 1993-06-30 Biological fixed carrier for sewage treatment, sewage purification method and sewage purification device

Publications (2)

Publication Number Publication Date
JPH0716586A true JPH0716586A (en) 1995-01-20
JP3252158B2 JP3252158B2 (en) 2002-01-28

Family

ID=15737928

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16158593A Expired - Lifetime JP3252158B2 (en) 1993-06-30 1993-06-30 Biological fixed carrier for sewage treatment, sewage purification method and sewage purification device

Country Status (1)

Country Link
JP (1) JP3252158B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2002070103A1 (en) * 2001-03-08 2002-09-12 Korea Terrafil Co., Ltd. Media for use in pollution control and apparatus for and method of manufacturing the same
CN107098481A (en) * 2017-04-26 2017-08-29 中林山水(北京)生态科技股份有限公司 Specificity microorganism for handling black and odorous water activates inserts

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2002070103A1 (en) * 2001-03-08 2002-09-12 Korea Terrafil Co., Ltd. Media for use in pollution control and apparatus for and method of manufacturing the same
CN107098481A (en) * 2017-04-26 2017-08-29 中林山水(北京)生态科技股份有限公司 Specificity microorganism for handling black and odorous water activates inserts

Also Published As

Publication number Publication date
JP3252158B2 (en) 2002-01-28

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