JPH09253681A - Bacteria carrier - Google Patents

Bacteria carrier

Info

Publication number
JPH09253681A
JPH09253681A JP8067708A JP6770896A JPH09253681A JP H09253681 A JPH09253681 A JP H09253681A JP 8067708 A JP8067708 A JP 8067708A JP 6770896 A JP6770896 A JP 6770896A JP H09253681 A JPH09253681 A JP H09253681A
Authority
JP
Japan
Prior art keywords
length
bacteria carrier
specific gravity
carrier
microbial carrier
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
JP8067708A
Other languages
Japanese (ja)
Other versions
JP3171554B2 (en
Inventor
Yoshio Tomita
美穂 富田
Tomoaki Inagaki
智亮 稲垣
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators 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 NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP06770896A priority Critical patent/JP3171554B2/en
Publication of JPH09253681A publication Critical patent/JPH09253681A/en
Application granted granted Critical
Publication of JP3171554B2 publication Critical patent/JP3171554B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

PROBLEM TO BE SOLVED: To facilitate the uniform mixing with treated water and the separation from activated sludge by reduced aeration power by using a plate-shaped member composed of a polymeric material of which the specific gravity is within a specific range and made specific in the length of one side thereof as a bacteria carrier. SOLUTION: A plate-shaped member composed of a plymeric material with specific gravity of 1.0-1.1 such as a polyvinyl alcohol gel and having a square shape of which one side has a length of 7-20mm and an aspect ratio (length of one side/thickness) of 3.5 or more is used as a plate-shaped bacteria carrier. The min. air passing quantity required in the uniform fluidization of the bacteria carrier is shown in a graph in terms of a fluidization enabling air passing ratio. That is, the bacteria carrier having a thickness of 2mm or less and a length of one side of 7-20mm shows good fluidizing properties. By increasing a length of one side as compared with a conventional product, the mesh size of a screen separating activated sludge and the bacteria carrier can be made large. Since this bacteria carrier is hard to sediment and rich in fluidizing properties, even if specific gravity is set to about 1.1, fluidizing properties are not damaged.

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、下水、ゴミ浸出
水、産業廃水等の有機性廃水の生物処理に使用される微
生物担体に関するものである。
TECHNICAL FIELD The present invention relates to a microbial carrier used for biological treatment of organic wastewater such as sewage, leachate leachate, and industrial wastewater.

【0002】[0002]

【従来の技術】有機性廃水の生物処理においては、従来
から高負荷対策、硝化/脱窒時間の短縮等の目的で種々
の微生物担体が曝気槽に投入され、MLSS(活性汚
泥)単独の場合と比較してより短時間で処理を完了させ
る工夫がなされている。これらの微生物担体は浮遊状態
で用いるために、比重が1程度で大きさが3〜7mmの略
立方体または球状体とされており、材質としてはポリビ
ニルアルコール、ポリエチレングリコール、ポリウレタ
ン、セルロース等が普通である。
2. Description of the Related Art In the biological treatment of organic wastewater, various microbial carriers have been conventionally introduced into the aeration tank for the purpose of high load countermeasures, shortening of nitrification / denitrification time, etc., and MLSS (activated sludge) alone The device is designed to complete the process in a shorter time than the above. Since these microbial carriers are used in a suspended state, they are formed into a substantially cubic or spherical body having a specific gravity of about 1 and a size of 3 to 7 mm, and the material is usually polyvinyl alcohol, polyethylene glycol, polyurethane, cellulose or the like. is there.

【0003】微生物担体の大きさは大きければ大きいほ
どMLSS(活性汚泥)との分離が簡単となり、曝気槽
からの流失を防止し易くなる。しかし上記のように大き
さが10mm以下に制限されていたのは、大きさが10mmを越
えると沈降し易くなり、MLSSとの比重差を僅かにし
ても処理水との均一な混合が困難となるためである。
The larger the size of the microbial carrier, the easier the separation from MLSS (activated sludge), and the easier it is to prevent runoff from the aeration tank. However, as described above, the size was limited to 10 mm or less because if the size exceeds 10 mm, sedimentation is likely to occur, and uniform mixing with treated water is difficult even if the specific gravity difference with MLSS is small. This is because

【0004】また微生物担体の大きさを小さくするほど
比表面積が増加するため、微生物の付着量を増大させる
ことができるとともに、処理水との均一な混合が容易と
なる。しかし小さ過ぎるとMLSSとの分離が困難とな
る。このために従来通常に使用されている微生物担体は
比重が1.02〜1.05で大きさが3〜7mmの粒子である。
Since the specific surface area increases as the size of the microbial carrier decreases, the amount of microorganisms attached can be increased and uniform mixing with the treated water becomes easy. However, if it is too small, separation from MLSS becomes difficult. For this reason, conventionally used microorganism carriers are particles having a specific gravity of 1.02 to 1.05 and a size of 3 to 7 mm.

【0005】上記したように、微生物担体の大きさ/形
状に関しては性能及び沈降しにくさと、MLSSとの分
離の容易さとは相反するものであり、特に深槽曝気槽の
ように散気設備が槽の中間深さの部分に設置されている
ために槽底部の流速が小さい場合には、通常の微生物担
体では槽底部に沈殿してしまうことがあった。なおこの
問題を解決するために、散気量を過大にし槽底部に流速
を大きくして沈降を防止する方法や、深槽を縦に2分割
して死水域を減少させる方法等があるが、いずれの方法
も旋回流速が大きくなることによる微生物担体の損耗が
激しくなったり、曝気動力のための運転費がかさんだ
り、設備改造に多大の費用がかかる等の実用上の問題が
あった。
As described above, regarding the size / shape of the microbial carrier, the performance and the difficulty in sedimentation conflict with the ease of separation from the MLSS. Especially, the aeration equipment such as the deep tank aeration tank. However, when the flow velocity at the bottom of the tank is low because it is installed at the intermediate depth of the tank, the usual microbial carrier may precipitate at the bottom of the tank. In order to solve this problem, there is a method of increasing the aeration amount and increasing the flow velocity at the bottom of the tank to prevent sedimentation, a method of vertically dividing the deep tank into two and reducing the dead water area, Both methods had practical problems such as severe wear of the microbial carrier due to high swirling velocity, high operating cost for aeration power, and great cost for equipment modification.

【0006】[0006]

【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決し、微生物の付着量を増大させることが
でき、少ない曝気動力で処理水との均一な混合が容易で
あり、しかもMLSSとの分離も容易な微生物担体を提
供するためになされたものである。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned conventional problems, can increase the amount of adhered microorganisms, can easily mix uniformly with treated water with less aeration power, and The purpose is to provide a microbial carrier that can be easily separated from MLSS.

【0007】[0007]

【課題を解決するための手段】上記の課題を解決するた
めになされた本発明の微生物担体は、比重が1.0 〜1.1
の高分子材料からなり、一辺の長さが7〜20mmの板状体
であることを特徴とするものである。なお、一辺の長さ
/厚みとして定義されるアスペクト比を3.5 以上とする
ことが好ましい。使用される高分子材料は例えばポリビ
ニルアルコールゲルとすることができる。また平板体の
表面は平面とするほか、湾曲面とすることも可能であ
る。
Means for Solving the Problems The microbial carrier of the present invention made to solve the above problems has a specific gravity of 1.0 to 1.1.
It is characterized by being a plate-like body made of the above polymer material and having a side length of 7 to 20 mm. The aspect ratio defined as the length / thickness of one side is preferably 3.5 or more. The polymeric material used can be, for example, a polyvinyl alcohol gel. The surface of the flat plate body may be a flat surface or a curved surface.

【0008】[0008]

【発明の実施の形態】以下に図面を参照しつつ本発明の
好ましい実施の形態を示す。図1は平板状の微生物担体
の例を示すもので、ポリビニルアルコールゲル等の高分
子材料からなる一辺の長さが7〜20mmの正方形状であ
り、厚み一辺の長さ/厚みとして定義されるアスペクト
比を3.5 以上としたものである。なおこれらの値から機
械的に計算すると、厚みの最大値は5.7mm となるが、厚
みを増加させると内部が微生物の付着に寄与しないデッ
ドゾーンとなるので、実際には厚みは2mm以下とするこ
とが好ましい。最も好ましい厚みは0.5 〜1.5mm であ
り、アスペクト比は5〜100 程度の範囲とすることが好
ましい。なお図2は表面を湾曲させた微生物担体の例を
示すもので、材料、サイズ、厚み等は図1のものと同様
である。また湾曲状態は図示のような単純な形状の他に
W状等としてもよいが、水中でひらひらと舞うことがで
きることが必要であるため、板状の形態から大きく外れ
ることは好ましくない。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of the present invention will be described below with reference to the drawings. FIG. 1 shows an example of a plate-shaped microbial carrier, which is made of a polymer material such as polyvinyl alcohol gel and has a square shape with a side length of 7 to 20 mm, and is defined as thickness / length / side length. The aspect ratio is 3.5 or more. When calculated mechanically from these values, the maximum thickness is 5.7 mm, but if the thickness is increased, the inside becomes a dead zone that does not contribute to the attachment of microorganisms, so the actual thickness is 2 mm or less. It is preferable. The most preferable thickness is 0.5 to 1.5 mm, and the aspect ratio is preferably in the range of 5 to 100. Note that FIG. 2 shows an example of a microorganism carrier having a curved surface, and the material, size, thickness, etc. are the same as those in FIG. The curved state may be a W shape or the like in addition to the simple shape shown in the figure, but it is necessary to be able to flutter in water, so it is not preferable that the curved shape greatly deviates from the plate shape.

【0009】このような本発明の微生物担体は、従来の
粒状の微生物担体に比較してMLSS中で沈降する際の
抵抗が大きくなり、沈降しにくくなる。図3は本発明の
微生物担体と従来の微生物担体との沈降速度を比較した
グラフである。本発明の微生物担体としては厚みを1.0m
m の一定値とし、一辺の長さを様々に変えた図1の形状
のものを準備し、また対照品として一辺の長さが5mmの
立方体の微生物担体を準備した。なお材質はともに比重
が1.03のポリビニルアルコールゲルとした。
[0009] Such a microbial carrier of the present invention has a greater resistance when settling in MLSS and is less likely to settle than conventional granular microbial carriers. FIG. 3 is a graph comparing the sedimentation rates of the microbial carrier of the present invention and the conventional microbial carrier. The microbial carrier of the present invention has a thickness of 1.0 m
A sample having the shape shown in FIG. 1 in which the length of one side was varied with the constant value of m was prepared, and as a control product, a cubic microbial carrier having a side length of 5 mm was prepared. The material was polyvinyl alcohol gel having a specific gravity of 1.03.

【0010】次に本発明の微生物担体の流動性を確認す
るため、図4に示した深槽曝気槽のスケールモデルを用
いて、テストを行なった。この図4のモデルは槽体1の
中段に散気装置2を配置するとともに、槽体1の幅方向
の中央に垂直な隔壁3を設けたものである。本発明の微
生物担体としては一辺の長さ及び厚みを様々に変えた図
1の形状のものを準備し、また対照品として一辺の長さ
が5mmの立方体の微生物担体を準備した。なお材質はと
もに比重が1.03のポリビニルアルコールゲルとした。
Next, in order to confirm the fluidity of the microbial carrier of the present invention, a test was conducted using the scale model of the deep tank aeration tank shown in FIG. In the model of FIG. 4, the air diffuser 2 is arranged in the middle stage of the tank body 1, and a vertical partition wall 3 is provided at the center of the tank body 1 in the width direction. As the microbial carrier of the present invention, the shape of FIG. 1 in which the length and thickness of one side were variously changed was prepared, and as a control product, a cubic microbial carrier having a side length of 5 mm was prepared. The material was polyvinyl alcohol gel having a specific gravity of 1.03.

【0011】図5はこれらの微生物担体を均一に流動さ
せるために要する最低通気量を示すグラフであり、流動
化可能通気率(水量1m3 当り1時間に要する散気空気
量)に換算して示してある。なお図5中の破線は、実規
模の深槽曝気槽で通常の散気量とした場合の槽底部の流
速を与えるスケールモデル槽での通気量であり、この通
気量以下で微生物担体が均一に流動化すれば、実規模の
深槽曝気槽でも良好な流動が可能なことを意味する。こ
の図5に示されるように、厚みが2mm以下で一辺の長さ
を7〜20mmの範囲内としたものは、良好な流動性を示
す。
FIG. 5 is a graph showing the minimum aeration amount required to evenly flow these microbial carriers, which is converted into a fluidizable aeration ratio (aeration air amount required for 1 hour per 1 m 3 of water amount). It is shown. Note that the broken line in Fig. 5 is the aeration amount in the scale model tank that gives the flow velocity at the bottom of the tank in the case of a normal-scale deep aeration tank with a normal aeration amount. If it is fluidized, it means that good flow is possible even in a full-scale deep tank aeration tank. As shown in FIG. 5, those having a thickness of 2 mm or less and a side length in the range of 7 to 20 mm show good fluidity.

【0012】また、微生物担体の一辺の長さを従来品よ
りも大きくすることによって、MLSSと微生物担体と
をスクリーン等で分離する場合の目開きを大きくするこ
とができる。例えば、一辺が7mmの微生物担体ならば目
開きが5mm□のスクリーンが使用でき、一辺が20mmの微
生物担体ならば目開きが15mm□のスクリーンが使用でき
る。このため、目開きの細かいスクリーンを使用せざる
を得なかった従来品に比較して、スクリーンの目詰まり
の清掃等の維持管理作業を大幅に低減することができ
る。
Further, by making the length of one side of the microbial carrier larger than that of the conventional product, it is possible to increase the opening when separating the MLSS and the microbial carrier by a screen or the like. For example, a screen having a 5 mm square opening can be used for a microbial carrier having a side of 7 mm, and a screen having a 15 mm square opening can be used for a microbial carrier having a 20 mm side. Therefore, maintenance and management work such as cleaning of clogging of the screen can be significantly reduced as compared with the conventional product in which a screen with a small opening has to be used.

【0013】上記したように、本発明の微生物担体は沈
降しにくく、流動性が良好であるので、従来品よりも比
重を大きくすることができる。即ち、従来品の比重は最
大でも1.05程度とする必要があったが、本発明の微生物
担体は比重を1.1程度としても流動性が損なわれない。
図6は本発明品の比重を変化させた場合の流動化可能通
気率を示すグラフであり、一辺の長さが20mmで、厚みが
0.5mm 、1.0mm 、2.0mm の3種類の微生物担体を使用し
た。この図6のグラフから分かるように、本発明の微生
物担体は比重を1.1 まで増加させても流動性が良好であ
る。また当然のことであるが、微生物担体の浮上を防止
するためには比重は1.0 以上とする必要がある。
As described above, the microbial carrier of the present invention is unlikely to settle and has good fluidity, so that it can have a higher specific gravity than conventional products. That is, the specific gravity of the conventional product had to be about 1.05 at the maximum, but the microbial carrier of the present invention does not impair the fluidity even when the specific gravity is about 1.1.
FIG. 6 is a graph showing the fluidizable air permeability when the specific gravity of the product of the present invention is changed. The length of one side is 20 mm and the thickness is
Three types of microbial carriers of 0.5 mm, 1.0 mm and 2.0 mm were used. As can be seen from the graph of FIG. 6, the microbial carrier of the present invention has good fluidity even when the specific gravity is increased to 1.1. As a matter of course, the specific gravity must be 1.0 or more to prevent the microbial carrier from floating.

【0014】[0014]

【発明の効果】以上に説明したように、本発明の微生物
担体は沈降しにくく流動性が良好であるので、従来品よ
りも通気率を減少させることができ、曝気動力を10〜30
%程度削減することができる。また本発明の微生物担体
はMLSSとの比重差を大きくとることができるので、
担体分離槽における担体流出の危険性をなくすることが
できる。更に本発明の微生物担体は一辺の長さを大きく
したので、スクリーン等により担体分離を行なう場合で
も目詰まりのおそれのない目開きが5mm以上のスクリー
ンを使用することができる。しかも板状体としたので微
生物の付着に寄与する比表面積を大きくとることがで
き、多量の微生物を担持させることができる。
As described above, since the microbial carrier of the present invention is hard to settle and has good fluidity, it is possible to reduce the aeration rate as compared with the conventional product, and the aeration power is 10 to 30.
It can be reduced by about%. Further, since the microbial carrier of the present invention can have a large difference in specific gravity from MLSS,
The risk of carrier outflow in the carrier separation tank can be eliminated. Furthermore, since the length of one side of the microbial carrier of the present invention is increased, it is possible to use a screen having an opening of 5 mm or more which does not cause clogging even when the carrier is separated by a screen or the like. Moreover, since the plate-shaped body is used, a large specific surface area that contributes to the attachment of microorganisms can be obtained, and a large amount of microorganisms can be supported.

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

【図1】平板状の微生物担体の例を示す斜視図である。FIG. 1 is a perspective view showing an example of a plate-shaped microorganism carrier.

【図2】湾曲状の微生物担体の例を示す斜視図である。FIG. 2 is a perspective view showing an example of a curved microbial carrier.

【図3】担体寸法と沈降速度との関係を示すグラフであ
る。
FIG. 3 is a graph showing the relationship between carrier size and sedimentation rate.

【図4】実験に使用したスケールモデルの断面図であ
る。
FIG. 4 is a sectional view of a scale model used in an experiment.

【図5】担体寸法と流動化可能通気率との関係を示すグ
ラフである。
FIG. 5 is a graph showing the relationship between carrier size and fluidizable air permeability.

【図6】担体の比重と流動化可能通気率との関係を示す
グラフである。
FIG. 6 is a graph showing the relationship between the specific gravity of the carrier and the fluidizable air permeability.

【符号の説明】[Explanation of symbols]

1 槽体、2 散気槽、3 隔壁 1 tank body, 2 aeration tank, 3 bulkheads

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 比重が1.0 〜1.1 の高分子材料からな
り、一辺の長さが7〜20mmの板状体であることを特徴と
する微生物担体。
1. A microbial carrier characterized by being a plate-like body having a specific gravity of 1.0 to 1.1 and having a side length of 7 to 20 mm.
【請求項2】 一辺の長さ/厚みとして定義されるアス
ペクト比が3.5 以上である請求項1記載の微生物担体。
2. The microbial carrier according to claim 1, which has an aspect ratio defined as one side length / thickness of 3.5 or more.
【請求項3】 高分子材料がポリビニルアルコールゲル
である請求項1または2記載の微生物担体。
3. The microbial carrier according to claim 1, wherein the polymer material is polyvinyl alcohol gel.
【請求項4】 表面を湾曲させた請求項1〜3のいずれ
かに記載の微生物担体。
4. The microbial carrier according to claim 1, which has a curved surface.
JP06770896A 1996-03-25 1996-03-25 Microbial carrier Expired - Fee Related JP3171554B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP06770896A JP3171554B2 (en) 1996-03-25 1996-03-25 Microbial carrier

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP06770896A JP3171554B2 (en) 1996-03-25 1996-03-25 Microbial carrier

Publications (2)

Publication Number Publication Date
JPH09253681A true JPH09253681A (en) 1997-09-30
JP3171554B2 JP3171554B2 (en) 2001-05-28

Family

ID=13352737

Family Applications (1)

Application Number Title Priority Date Filing Date
JP06770896A Expired - Fee Related JP3171554B2 (en) 1996-03-25 1996-03-25 Microbial carrier

Country Status (1)

Country Link
JP (1) JP3171554B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009072785A (en) * 2008-12-01 2009-04-09 Metawater Co Ltd Nitrification carrier circulation method of deep aeration tank

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009072785A (en) * 2008-12-01 2009-04-09 Metawater Co Ltd Nitrification carrier circulation method of deep aeration tank

Also Published As

Publication number Publication date
JP3171554B2 (en) 2001-05-28

Similar Documents

Publication Publication Date Title
EP3146035B1 (en) Biofilm media, treatment system and method of treatment
US7862711B2 (en) Biofilter units and water treatment facilities with using the same biofilter units
KR101686484B1 (en) Method of sewage treatment
US3623976A (en) Liquid wastes treatment method
JP2019130528A (en) Reduction of substance in contaminated fluid using natural product growth media
US6004456A (en) Equalization basin-reactor system
US8226828B2 (en) SAF system and method involving specific treatments at respective stages
US7270750B2 (en) Clarifier recycle system design for use in wastewater treatment system
US4282102A (en) Activated sludge wastewater treatment having suspended inert media for biota growth
CN210915499U (en) Activated sludge screening device for sewage treatment
KR800000035B1 (en) Integral circular wastewater treatment plant
JPH09253681A (en) Bacteria carrier
GB1584373A (en) Process for purifying waste waters
JP3395927B2 (en) Biological treatment method and apparatus using microorganism-adhered carrier
JPH02122891A (en) Aerobic waste water treatment equipment
JPS586555Y2 (en) Biological treatment equipment for wastewater
US4978445A (en) Aeration chamber for a sewage treatment system
JPH0463198A (en) Activated sludge treating equipment
JPH08215694A (en) Highly functional biological treatment apparatus
JP2001070985A (en) Waste water treatment apparatus
Mendez et al. Biofilm reactors technology in wastewater treatment
JPH07108291A (en) Biological treatment method and device using immobilized microorganism carrier
JPH029495A (en) Suspension type activated sludge treating equipment
JP2818081B2 (en) Sewage treatment equipment
JP3228455B2 (en) Deep aeration tank

Legal Events

Date Code Title Description
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20010306

LAPS Cancellation because of no payment of annual fees