JP2000061487A - Carrier for microorganism and its production - Google Patents

Carrier for microorganism and its production

Info

Publication number
JP2000061487A
JP2000061487A JP10239187A JP23918798A JP2000061487A JP 2000061487 A JP2000061487 A JP 2000061487A JP 10239187 A JP10239187 A JP 10239187A JP 23918798 A JP23918798 A JP 23918798A JP 2000061487 A JP2000061487 A JP 2000061487A
Authority
JP
Japan
Prior art keywords
polystyrene
carrier
microorganisms
porous
water
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.)
Withdrawn
Application number
JP10239187A
Other languages
Japanese (ja)
Inventor
Kiyoshi Kurihara
清 栗原
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.)
Kankyo Engineering Co Ltd
Original Assignee
Kankyo Engineering 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 Kankyo Engineering Co Ltd filed Critical Kankyo Engineering Co Ltd
Priority to JP10239187A priority Critical patent/JP2000061487A/en
Publication of JP2000061487A publication Critical patent/JP2000061487A/en
Withdrawn legal-status Critical Current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

Abstract

PROBLEM TO BE SOLVED: To improve the efficiency of biological treatment in an aeration tank by constituting a carrier for microorganisms of a porous polystyrene body. SOLUTION: A carrier for microorganisms arranged in an aeration tank is made essentially of polystyrene, preferably polystyrene obtd. by recovering foamed polystyrene products, pelletizing and making porous, thereby the carrier has an excellent function and can be obtained at a moderate price. Furthermore, as a method of making polystyrene porous, water-soluble crystalline compounds are incorporated into polystyrene melt to disperse them and formed articles obtained from the mixture are immersed in water to dissolve the crystals, and then a porous polystyrene body can be easily obtained. The carrier for microorganisms excellent in property with which the efficiency of biological treatment in the aeration tank can be improved can be produced at a moderate price. As a result, without changing a conventional active sludge treating device, treatment of organic waste water can be economically realized.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、有機性廃水を活性
汚泥により処理する際に使用する微生物用担体及びその
製造方法に関する。
TECHNICAL FIELD The present invention relates to a carrier for microorganisms used in treating organic wastewater with activated sludge and a method for producing the same.

【0002】[0002]

【従来の技術】水中の汚濁物質は、河川や湖沼等の自然
の中で、沈殿、凝集、酸化、還元等の物理化学的、生物
学的な作用を受けて分解除去されて浄化される。特に有
機物を含んだ汚濁は、微生物によって生物学的な作用で
浄化され易い。これを利用した有機性廃水の浄化方法と
して、好気性微生物を含んだ活性汚泥により有機性廃水
を処理する活性汚泥法があるが、該方法は、浄化能力が
高く、比較的、処理経費が少なくて済む等の利点がある
ため、下水処理や産業廃水処理等において広く一般に使
用されている。
2. Description of the Related Art Pollutants in water are decomposed and purified in nature such as rivers and lakes by being subjected to physicochemical and biological actions such as precipitation, aggregation, oxidation and reduction. In particular, contaminants containing organic substances are easily purified by microorganisms by a biological action. As a method for purifying organic wastewater using this, there is an activated sludge method of treating organic wastewater with activated sludge containing aerobic microorganisms, but the method has a high purification capacity and relatively low treatment cost. Therefore, it is widely used in sewage treatment, industrial wastewater treatment, etc.

【0003】上記活性汚泥法では、調整槽等で廃水のp
H調整や均一化といった前処理を行なった後、有機性廃
水をエアレーションタンク(曝気槽)へと導き、この曝
気槽内で、酸素を吹き込みながら好気性微生物を含んだ
活性汚泥によりBODで示される廃水中の有機汚濁成分
を分解して浄化処理を行っている。従って、曝気槽にお
いて効率的な生物処理を実現するためには、有機性廃水
の空気との接触面積が大きい曝気槽を用いることが好ま
しいため、有機性廃水の処理量にもよるが、活性汚泥法
による有機性廃水の処理設備は、比較的広い敷地を要
し、大型化する傾向がある。
In the above-mentioned activated sludge method, waste water p
After pretreatment such as H adjustment and homogenization, the organic wastewater is led to an aeration tank (aeration tank), and in this aeration tank, BOD is shown by activated sludge containing aerobic microorganisms while blowing oxygen. Purification is performed by decomposing organic pollutants in wastewater. Therefore, in order to realize efficient biological treatment in the aeration tank, it is preferable to use an aeration tank that has a large contact area with the organic wastewater air. The organic wastewater treatment facility by the law requires a relatively large site and tends to be large.

【0004】これに対し、処理設備をコンパクト化する
ために、曝気槽内に微生物を担持するための微生物用担
体を配置し、微生物が快適に棲息できる環境を作ること
によって処理効率の向上を図り、高濃度・高負荷の有機
性廃水処理することが行なわれている。この際に使用さ
れる微生物用担体としては、例えば、ポリビニルアルコ
ールを不溶化処理して作製されたものや、ポリエチレン
グリコール、ポリウレタン或いは高密度ポリエチレン等
からなる成形体が知られている。
On the other hand, in order to make the treatment equipment compact, a carrier for microorganisms for supporting microorganisms is arranged in the aeration tank to improve the treatment efficiency by creating an environment in which the microorganisms can comfortably live. , High-concentration and high-load organic wastewater treatment is performed. As the carrier for microorganisms used at this time, for example, those prepared by insolubilizing polyvinyl alcohol, and molded products made of polyethylene glycol, polyurethane, high density polyethylene, or the like are known.

【0005】しかしながら、良好な微生物用担体には、
微生物との親和性が高く、毒性がなく、水中での流動性
に優れ、更に、微生物や酵素によって劣化を生じたり、
曝気処理によって摩耗したりすることがないこと等の各
種性能が要求されるため、微生物用担体として特別に調
製される必要があり、単価が高くなるという問題があっ
た。即ち、活性汚泥法で用いる曝気槽は大きな容積を占
めるので、処理効率の向上を図るには微生物用担体を数
多く必要とし、該担体の単価が高いと処理コストが増大
してしまう。
However, a good carrier for microorganisms is
It has a high affinity with microorganisms, is not toxic, has excellent fluidity in water, and causes deterioration due to microorganisms and enzymes,
Since various performances such as no abrasion due to aeration treatment are required, it is necessary to be specially prepared as a carrier for microorganisms, and there is a problem that the unit price becomes high. That is, since the aeration tank used in the activated sludge method occupies a large volume, a large number of microbial carriers are required in order to improve the treatment efficiency, and if the unit price of the carrier is high, the treatment cost will increase.

【0006】一方、全く別の問題として、近年における
流通機構は広範に渡るため、包装用材料として、軽くて
丈夫な発泡スチロールが、食品トレーや梱包用容器、或
いは梱包用クッション材として大量に使用されており、
その廃棄処理の問題が深刻化している。更に、発泡スチ
ロールは、有限な地球資源である石油を原料としている
ため、資源の有効活用を図ることが求められている。
On the other hand, as a completely different problem, since the distribution mechanism in recent years is widespread, light and durable Styrofoam is widely used as a packaging material for food trays, packaging containers, or packaging cushioning materials. And
The problem of disposal is becoming more serious. Further, since Styrofoam is made from petroleum, which is a finite earth resource, as a raw material, effective utilization of resources is required.

【0007】このため、食品用トレー等の発泡スチロー
ル製品の一部は流通機関を通じて回収され、再生して再
利用することが行なわれ始めている。この際、回収され
た発泡スチロールは非常に嵩ばるため、そのままの状態
で再生工場に搬送したのでは運送コストが高くなるの
で、早い段階で、回収した発泡スチロール製品を溶融し
てペレット化することが行なわれている。しかし、上記
のようにして得られる再生ポリスチレンペレットは、不
純物の問題もあり、用途によっては使用することができ
ず、利用できたとしてもバージン材料に少量混入させた
状態で使用しているのが現状である。このように、使用
済みの発泡スチロール製品については、回収システムが
かなり充実し、回収に対する消費者の意識も高まってき
てはいるものの、再生されたポリスチレンペレットの有
効利用が図られておらず、大量に利用される用途を探し
ているのが現状である。
For this reason, a part of Styrofoam products such as food trays is being collected through a distribution organization, and is being recycled and reused. At this time, since the collected Styrofoam is very bulky, transporting it to the recycling factory as it is will increase the transportation cost, so at an early stage, the Styrofoam product collected is melted and pelletized. Has been. However, the regenerated polystyrene pellets obtained as described above cannot be used depending on the application because of the problem of impurities, and even if it can be used, it is used in a state mixed with a small amount of virgin material. The current situation. In this way, for used Styrofoam products, although the collection system is considerably enhanced and consumers are more conscious of collection, effective use of regenerated polystyrene pellets has not been achieved and a large amount At present, we are looking for applications to be used.

【0008】[0008]

【発明が解決しようとする課題】従って本発明の目的
は、曝気槽内における生物処理の効率向上を有効に図る
ことが可能な優れた特性の微生物用担体を安価に提供す
ることにある。更に本発明の別の目的は、再生されたポ
リスチレンペレットの有効利用を図り、地球規模での環
境保護を達成することにある。
SUMMARY OF THE INVENTION Therefore, an object of the present invention is to provide a carrier for microorganisms having excellent characteristics, which can effectively improve the efficiency of biological treatment in an aeration tank, at low cost. Still another object of the present invention is to make effective use of regenerated polystyrene pellets and achieve environmental protection on a global scale.

【0009】[0009]

【課題を解決するための手段】上記の目的は、下記の本
発明によって達成される。即ち、本発明は、多孔質ポリ
スチレン体からなることを特徴とする微生物用担体、及
び該微生物用担体の製造方法である。
The above objects can be achieved by the present invention described below. That is, the present invention is a carrier for microorganisms comprising a porous polystyrene body and a method for producing the carrier for microorganisms.

【0010】[0010]

【発明の実施の形態】以下、本発明の好ましい実施の形
態を挙げて本発明を詳細に説明する。本発明者らは、上
記従来技術の問題点を解決すべく鋭意研究の結果、有機
性廃水を、好気性微生物を含む活性汚泥で効率よく処理
することを目的として、曝気槽内に配置される微生物用
担体を、ポリスチレンを主原料とし、好ましくは発泡ス
チロール製品を回収してペレット化したポリスチレン原
料を用い、該ポリスチレンを多孔質化すれば、優れた機
能を有し、しかも安価な微生物用担体が得られることを
知見して本発明に至った。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in detail below with reference to preferred embodiments of the present invention. As a result of intensive research to solve the above-mentioned problems of the prior art, the inventors of the present invention arranged in an aeration tank for the purpose of efficiently treating organic wastewater with activated sludge containing aerobic microorganisms. Microorganism carrier, polystyrene as the main raw material, preferably using a polystyrene raw material obtained by collecting and pelletizing expanded polystyrene products, if the polystyrene is made porous, it has an excellent function, yet an inexpensive microbial carrier The present invention has been accomplished by finding that it can be obtained.

【0011】更に、ポリスチレンを多孔質化する方法と
して、ポリスチレン溶融物中に水溶性の結晶性化合物を
混合して分散させ、該混合物から得られた成形品を水中
に浸漬して上記結晶を溶解すれば、多孔質ポリスチレン
体が容易に得られることがわかった。更に、ポリスチレ
ン溶融物中に、密度が高い無機充填材を添加させれば、
その比重を、微生物用担体として好適な範囲に容易に調
整することが可能であることもわかった。
Further, as a method for making polystyrene porous, a water-soluble crystalline compound is mixed and dispersed in a polystyrene melt, and a molded article obtained from the mixture is immersed in water to dissolve the above crystals. It was found that a porous polystyrene body can be easily obtained by doing so. Furthermore, if a high density inorganic filler is added to the polystyrene melt,
It was also found that its specific gravity can be easily adjusted to a range suitable as a carrier for microorganisms.

【0012】以下、本発明の微生物用担体、及びその製
造方法について更に詳細に説明する。先に述べたよう
に、本発明の微生物用担体は、多孔質ポリスチレンから
なるが、特に、経済性及び環境問題の観点から、廃棄さ
れた発泡スチロールから回収されたポリスチレンを主成
分として構成することが好ましい。即ち、食品トレーや
包装容器或いはクッション材に用いられている発泡スチ
ロールは、通常、回収された後、350℃程度の熱風炉
で溶融されてペレット化され、再生原料として比較的安
価に市場を流通しているので、本発明においては、微生
物用担体の原料として、この再生ポリスチレンペレット
を使用することが好ましい。
The carrier for microorganisms of the present invention and the method for producing the same will be described below in more detail. As described above, the carrier for microorganisms of the present invention is made of porous polystyrene, and in particular, from the viewpoint of economical efficiency and environmental problems, it may be composed mainly of polystyrene recovered from discarded expanded polystyrene. preferable. That is, Styrofoam used in food trays, packaging containers or cushion materials is usually recovered, then melted in a hot air oven at about 350 ° C. and pelletized, and is marketed at a relatively low cost as a recycled material. Therefore, in the present invention, it is preferable to use the regenerated polystyrene pellets as the raw material of the carrier for microorganisms.

【0013】以下、本発明の微生物用担体の好ましい製
造方法について説明する。上記で述べたように、本発明
の微生物用担体は、多孔質ポリスチレン体からなるが、
経済性及び地球環境保護の観点から、その主原料として
発泡スチロールから回収された再生ポリスチレンペレッ
トを使用することが好ましいが、再生ポリスチレンペレ
ットから、以下の方法で多孔質体を簡易に得ることがで
きる。先ず、再生ポリスチレンペレットを溶融し、溶融
物の中に水溶性の結晶性化合物を混合して分散させ、得
られた混合物を押出成形機で、200〜250℃程度の
温度で押出成形した後、所望の大きさに切断等して成形
品を得る。次に、得られた成形品を水中に浸漬して、成
形品内に分散している水溶性の結晶性化合物を溶解させ
る。この結果、成形品の表面部、更には、それに続く内
部にある結晶性化合物が水中に溶解するので、溶解した
部分に孔が形成されて多孔質の成形体が得られる。この
ようにして形成された多孔質ポリスチレン体を微生物用
担体として曝気槽内に投入すれば、より多くの微生物を
棲息させることが可能となり、曝気槽内の微生物濃度が
高まり、処理効率の向上が達成される。
The preferred method for producing the carrier for microorganisms of the present invention will be described below. As described above, the carrier for microorganisms of the present invention comprises a porous polystyrene body,
From the viewpoint of economy and protection of the global environment, it is preferable to use regenerated polystyrene pellets recovered from expanded polystyrene as the main raw material, but a porous body can be easily obtained from the regenerated polystyrene pellets by the following method. First, the regenerated polystyrene pellets are melted, a water-soluble crystalline compound is mixed and dispersed in the melt, and the obtained mixture is extrusion-molded at a temperature of about 200 to 250 ° C. by an extruder. A molded product is obtained by cutting into a desired size. Next, the obtained molded product is immersed in water to dissolve the water-soluble crystalline compound dispersed in the molded product. As a result, the surface of the molded product, and further the crystalline compound present inside the molded product, is dissolved in water, so that pores are formed in the dissolved part and a porous molded product is obtained. If the porous polystyrene body formed in this way is introduced into the aeration tank as a carrier for microorganisms, it becomes possible to inhabit more microorganisms, the concentration of microorganisms in the aeration tank is increased, and the treatment efficiency is improved. To be achieved.

【0014】上記で使用する水溶性の結晶性化合物とし
ては、成形品の中に良好に分散し、且つ、成形品を水槽
の中に浸漬した場合に、水中に良好に溶け出すものであ
って、更に、担体内部に残留することを考慮して、微生
物や処理水に悪影響を及ぼさないものを使用することが
好ましい。具体的には、炭酸水素塩、炭酸塩、硫酸水素
塩、食塩等が挙げられる。例えば、炭酸水素カリウム、
炭酸ナトリウム、炭酸水素ナトリウムカリウム、硫酸水
素カリウム、硫酸水素ナトリウム、塩化ナトリウム等の
水溶性の結晶性化合物を使用することが好ましい。
The water-soluble crystalline compound used above is a compound which is well dispersed in a molded article and dissolves well in water when the molded article is immersed in a water tank. Furthermore, it is preferable to use a substance that does not adversely affect microorganisms or treated water in consideration of the fact that it remains inside the carrier. Specific examples include hydrogen carbonate, carbonate, hydrogen sulfate, and salt. For example, potassium hydrogen carbonate,
It is preferable to use water-soluble crystalline compounds such as sodium carbonate, sodium hydrogencarbonate, potassium hydrogensulfate, sodium hydrogensulfate and sodium chloride.

【0015】更に、本発明の微生物用担体は、曝気槽内
に収容された場合に、有機性廃水の表面に浮かんでしま
うことなく、有機性廃水中の好適な位置に配置されるよ
うに、その比重が適宜な範囲に調整されていることが好
ましい。例えば、0.80以上1.20以下の範囲に更
に、水中での流動性に優れたものとするためには、比重
が1.00〜1.10の範囲に調整されたものであるこ
とが好ましい。本発明の微生物用担体を構成する主成分
であるポリスチレンの比重は、通常、1.04〜1.1
程度であるが、多孔質体とするため、これよりも比重が
軽くなると考えられる。従って、本発明においては、微
生物用担体の比重を、好適な範囲に調整することが好ま
しい。
Further, the microbial carrier of the present invention, when stored in an aeration tank, is arranged at a suitable position in the organic wastewater without floating on the surface of the organic wastewater. It is preferable that its specific gravity is adjusted to an appropriate range. For example, in order to further improve the fluidity in water in the range of 0.80 or more and 1.20 or less, the specific gravity should be adjusted in the range of 1.00 to 1.10. preferable. The specific gravity of polystyrene, which is the main component of the carrier for microorganisms of the present invention, is usually 1.04 to 1.1.
It is considered that the specific gravity is lighter than that of the porous body because it is a porous body. Therefore, in the present invention, it is preferable to adjust the specific gravity of the carrier for microorganisms to a suitable range.

【0016】多孔質ポリスチレン体からなる本発明の微
生物用担体の比重を調整する方法としては、上記の多孔
質ポリスチレン体の製造方法において、ポリスチレンの
溶融物の中に、密度の高い無機充填材を微生物用担体中
に添加する方法が挙げられる。この際に使用し得る無機
充填材としては、密度が高く、多孔質ポリスチレン体中
に含有させた場合に、所望の比重の成形体が得られ、且
つ毒性がなく、しかも、添加することによって多孔質ポ
リスチレン体の耐久性や物性が損なわれなければ、いず
れのものも使用できる。具体的には、例えば、ゼオライ
ト、金属鉄、鉄を含む各種合金、炭酸カルシウム、硫酸
バリウム等が挙げられる。これらの中でもゼオライト
は、無機の多孔質体であり、それ自体、微生物担体とし
て有効なものであるので、本発明においては特に好まし
く使用できる。
As a method for adjusting the specific gravity of the carrier for microorganisms of the present invention comprising a porous polystyrene body, in the above-mentioned method for producing a porous polystyrene body, a high density inorganic filler is added to the polystyrene melt. A method of adding it to the carrier for microorganisms may be mentioned. The inorganic filler that can be used in this case has a high density, and when it is contained in a porous polystyrene body, a molded body having a desired specific gravity can be obtained, and it is non-toxic, and when it is added, it becomes porous. Any of them can be used as long as the durability and physical properties of the high quality polystyrene body are not impaired. Specific examples include zeolite, metallic iron, various iron-containing alloys, calcium carbonate, barium sulfate, and the like. Of these, zeolite is an inorganic porous material, and as such is effective as a microorganism carrier, it can be particularly preferably used in the present invention.

【0017】本発明者らの検討によれば、特に、無機充
填材としてゼオライトを用い、且つ水溶性の結晶性化合
物として炭酸水素塩或いは炭酸塩の結晶を用いて本発明
の微生物用担体を作製すれば、これらの材料はいずれも
安価であり、微生物や処理水に悪影響を及ぼすこともな
く、しかも、上記結晶は、水中に容易に溶け出すので機
能性に優れる微生物用担体が容易に得られる。尚、本発
明の微生物用担体を作製する場合に、その強度や耐久性
を向上させる等の目的で、他の添加物を混合してもよい
のは勿論である。
According to the studies by the present inventors, in particular, zeolite is used as the inorganic filler, and hydrogencarbonate or carbonate crystals are used as the water-soluble crystalline compound to prepare the carrier for microorganisms of the present invention. If so, all of these materials are inexpensive, do not adversely affect microorganisms and treated water, and since the crystals are easily dissolved in water, a carrier for microorganisms having excellent functionality can be easily obtained. . In addition, in the case of producing the carrier for microorganisms of the present invention, it is needless to say that other additives may be mixed for the purpose of improving the strength and durability thereof.

【0018】[0018]

【実施例】次に本発明の実施例及び比較例を挙げて本発
明を更に詳細に説明する。実施例1 通常の活性汚泥処理フローに従って建設した500リッ
トル/day規模のパイロットプラントを使用して、有
機性廃水の活性汚泥処理を行った。下記の表1に処理に
用いた原水の性状を示したが、原水として、食品工場か
らの有機性廃水を用いた。
EXAMPLES The present invention will be described in more detail with reference to Examples and Comparative Examples of the present invention. Example 1 An activated sludge treatment of organic wastewater was carried out using a 500 liter / day scale pilot plant constructed according to a normal activated sludge treatment flow. The properties of the raw water used for the treatment are shown in Table 1 below, and as the raw water, organic wastewater from a food factory was used.

【0019】表1 原水性状(食品工場の廃水) Table 1 Raw water condition (waste water of food factory)

【0020】先ず、上記の原水について、pH7.0、
BOD負荷量1.0kg/m3、HRT2.0日の運転
条件で活性汚泥処理を行った。その際に、本発明の微生
物用担体を、みかけ体積で20%の割合で投入し、曝気
流動させながら活性汚泥処理を行った。本実施例で使用
した微生物用担体は、次のようにして調製したものを用
いた。先ず、発泡スチロールの再生ペレットを溶融し、
その中に、炭酸水素カリウム結晶及びゼオライトを混合
して分散させ、該混合物を押出機にかけてφ20mmの
円柱状に押し出し、長さ30mmに切断した円柱状の成
形体を得た。次に、得られた成形体を充分な量の水の中
に浸漬し、炭酸水素カリウムを溶解させた。得られた多
孔質体の平均比重を測定したところ、1.10であっ
た。本実施例では、この微生物用担体を活性汚泥中に7
日間浸漬したものを使用した。
First, with respect to the above raw water, pH 7.0,
The activated sludge treatment was performed under the operating conditions of a BOD load of 1.0 kg / m 3 and an HRT of 2.0 days. At that time, the carrier for microorganisms of the present invention was introduced at a ratio of 20% in apparent volume, and activated sludge treatment was carried out while aerated and flowing. The carrier for microorganisms used in this example was prepared as follows. First, melt the recycled pellets of Styrofoam,
Crystals of potassium hydrogen carbonate and zeolite were mixed and dispersed therein, and the mixture was extruded into a cylinder having a diameter of 20 mm by an extruder to obtain a cylindrical molded body cut into a length of 30 mm. Next, the obtained molded body was immersed in a sufficient amount of water to dissolve potassium hydrogen carbonate. The average specific gravity of the obtained porous body was measured and found to be 1.10. In this example, the microbial carrier was added to the activated sludge.
What was soaked for a day was used.

【0021】比較例1 本発明の微生物用担体を投入しない以外は実施例1と同
様にして、活性汚泥処理試験を行った。
Comparative Example 1 An activated sludge treatment test was conducted in the same manner as in Example 1 except that the carrier for microorganisms of the present invention was not added.

【0022】[0022]

【評価】曝気処理後、実施例1及び比較例1における曝
気槽内の活性汚泥中の汚泥濃度を測定したところ、実施
例1では8,000mg/lであったのに対し、比較例
1では、4,000mg/lであった。この結果、本発
明の微生物用担体を使用した実施例1の場合は、曝気槽
内の微生物濃度が高くなっていることが確認できた。更
に、実施例1及び比較例1で行なった処理後の処理水に
ついて、BODを測定したところ、比較例1の場合と比
べてBOD値を低下させることができ、効率のよい活性
汚泥処理が行なわれたことを確認できた。
[Evaluation] After the aeration treatment, the sludge concentration in the activated sludge in the aeration tank in Example 1 and Comparative Example 1 was measured, and in Example 1, it was 8,000 mg / l, whereas in Comparative Example 1, , 4,000 mg / l. As a result, in the case of Example 1 using the carrier for microorganisms of the present invention, it was confirmed that the concentration of microorganisms in the aeration tank was high. Furthermore, when the BOD of the treated water after the treatment performed in Example 1 and Comparative Example 1 was measured, the BOD value could be reduced as compared with the case of Comparative Example 1, and efficient activated sludge treatment was performed. I was able to confirm that it was done.

【0023】[0023]

【発明の効果】上記に説明したように、本発明によれ
ば、曝気槽内における生物処理の効率向上を達成し得る
特性に優れた微生物用担体が安価に提供される。この結
果、従来の活性汚泥処理装置に変更を加えることなく、
経済的な有機性廃水の処理が実現される。更に本発明に
よれば、再生された発泡スチロール用ペレットの有効利
用の途が開け、地球規模での環境保護が達成できる。
As described above, according to the present invention, a carrier for microorganisms having excellent characteristics capable of achieving an improvement in the efficiency of biological treatment in an aeration tank is provided at low cost. As a result, without changing the conventional activated sludge treatment device,
Economical treatment of organic wastewater is realized. Further, according to the present invention, the recycled styrofoam pellets can be effectively utilized, and environmental protection on a global scale can be achieved.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 多孔質ポリスチレン体からなることを特
徴とする微生物用担体。
1. A carrier for microorganisms comprising a porous polystyrene body.
【請求項2】 廃棄された発泡スチロールから回収した
ポリスチレンを主成分として構成されている請求項1に
記載の微生物用担体。
2. The carrier for microorganisms according to claim 1, which is composed mainly of polystyrene recovered from the discarded expanded polystyrene.
【請求項3】 廃棄された発泡スチロールを溶融して得
られたポリスチレン溶融物中に水溶性の結晶性化合物を
混合して分散させ、該混合物から得られた成形品を水中
に浸漬させて上記結晶性化合物を溶解して多孔質ポリス
チレン体を得ることを特徴とする微生物用担体の製造方
法。
3. A water-soluble crystalline compound is mixed and dispersed in a polystyrene melt obtained by melting discarded Styrofoam, and a molded article obtained from the mixture is immersed in water to form the above crystal. A method for producing a carrier for microorganisms, which comprises dissolving a hydrophilic compound to obtain a porous polystyrene body.
【請求項4】 更に、ポリスチレン溶融物中に無機充填
材を添加して多孔質ポリスチレン体の比重を調整する請
求項3に記載の微生物用担体の製造方法。
4. The method for producing a carrier for microorganisms according to claim 3, further comprising adding an inorganic filler to the polystyrene melt to adjust the specific gravity of the porous polystyrene body.
JP10239187A 1998-08-25 1998-08-25 Carrier for microorganism and its production Withdrawn JP2000061487A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10239187A JP2000061487A (en) 1998-08-25 1998-08-25 Carrier for microorganism and its production

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10239187A JP2000061487A (en) 1998-08-25 1998-08-25 Carrier for microorganism and its production

Publications (1)

Publication Number Publication Date
JP2000061487A true JP2000061487A (en) 2000-02-29

Family

ID=17041019

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10239187A Withdrawn JP2000061487A (en) 1998-08-25 1998-08-25 Carrier for microorganism and its production

Country Status (1)

Country Link
JP (1) JP2000061487A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007197471A (en) * 2005-12-27 2007-08-09 Kurita Water Ind Ltd Manufacturing method of carrier for forming biomembrane and carrier for forming biomembrane
JP2007283222A (en) * 2006-04-18 2007-11-01 Unitika Ltd Biological treatment carrier
CN102249402A (en) * 2011-04-27 2011-11-23 合肥工业大学 Low-density zeolite biological aerated filter filling and preparation method thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007197471A (en) * 2005-12-27 2007-08-09 Kurita Water Ind Ltd Manufacturing method of carrier for forming biomembrane and carrier for forming biomembrane
JP2007283222A (en) * 2006-04-18 2007-11-01 Unitika Ltd Biological treatment carrier
CN102249402A (en) * 2011-04-27 2011-11-23 合肥工业大学 Low-density zeolite biological aerated filter filling and preparation method thereof

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