JP2000325984A - Aeration treatment method and apparatus - Google Patents

Aeration treatment method and apparatus

Info

Publication number
JP2000325984A
JP2000325984A JP11142254A JP14225499A JP2000325984A JP 2000325984 A JP2000325984 A JP 2000325984A JP 11142254 A JP11142254 A JP 11142254A JP 14225499 A JP14225499 A JP 14225499A JP 2000325984 A JP2000325984 A JP 2000325984A
Authority
JP
Japan
Prior art keywords
aeration
centrifugal
rotating disk
plate
chamber
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Withdrawn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
JP11142254A
Other languages
Japanese (ja)
Inventor
Michiaki Saito
通明 斎藤
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.)
Fuji Resin Kogyo Kk
Original Assignee
Fuji Resin Kogyo 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 Fuji Resin Kogyo Kk filed Critical Fuji Resin Kogyo Kk
Priority to JP11142254A priority Critical patent/JP2000325984A/en
Publication of JP2000325984A publication Critical patent/JP2000325984A/en
Withdrawn legal-status Critical Current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

  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To perform a highly efficient aeration treatment of pumped-up water containing an org. compd. without being affected by hardness components, turbidity and concn. of pumped-up water. SOLUTION: An aeration treatment apparatus A is equipped with a casing having at least one aeration chamber 5 having an opening part 7 provided to the center part of the side wall 2 thereof, a centrifugal rotary plate 11 having a plurality of blades arranged in opposed relation to the opening part provided to the center part of the side wall 2 of the aeration chamber of the casing, a drive means 22 for rotationally driving the centrifugal rotary plate through a rotary shaft 12 and an injection pipe 27 injecting water charged in the aeration chamber of the casing through the opening part toward the center part of the centrifugal rotary plate. The water injected by the injection pipe is finely pulverized by the centrifugal force caused by the rotation of the centrifugal rotary plate to be brought into contact with air sucked from the opening part to be subjected to aeration treatment.

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、揮発性有機化合物
で汚染された井戸水や地下水などを揚水後に曝気処理し
たり、揮発性有機化合物を含む工場排水を曝気処理した
りする曝気処理方法及びその装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an aeration method for performing aeration treatment after pumping well water or groundwater contaminated with volatile organic compounds after pumping, and aeration treatment of industrial wastewater containing volatile organic compounds. Related to the device.

【0002】[0002]

【従来の技術】近年、揮発性有機化合物、特にトリクロ
ロエチレンやテトラクロロエチレン等の有機塩素系化合
物による井戸水や地下水などの汚染が社会問題となって
きている。
2. Description of the Related Art In recent years, pollution of well water and groundwater by volatile organic compounds, particularly organic chlorine compounds such as trichloroethylene and tetrachloroethylene, has become a social problem.

【0003】一方、汚染物質の除去あるいは無害化する
浄化技術は、例えば環境庁水質保全局編の「土壌・地下
水汚染に係る調査・対策指針運用基準」に記載されてい
るように、種々のものが検討され、実用化と同時に実用
化に向けて実証試験などが広範囲に実施されている。そ
の中で、揚水曝気処理法は、従来技術で対応できかつ簡
単なために実績も多い。曝気処理後の排ガスは活性炭な
どを使用し、浄化処理されるのが一般的である。
[0003] On the other hand, various purification techniques for removing or detoxifying contaminants are described in, for example, "Operation Standards for Investigation and Countermeasures for Soil and Groundwater Pollution" edited by the Water Quality Conservation Bureau of the Environment Agency. Have been studied, and demonstration tests and the like have been extensively conducted for practical use at the same time as practical use. Among them, the pumping aeration method has a good track record because it can be handled by the conventional technology and is simple. The exhaust gas after the aeration treatment is generally subjected to a purification treatment using activated carbon or the like.

【0004】そして、曝気処理をする装置としては、充
填塔や多段棚塔などを使用した塔式曝気処理装置と、槽
に空気を吹き込む空気吹込式曝気処理装置とが化学工場
や排ガス処理に実績があり、多用されている。また、特
開平2−75391号公報に開示されるように、空気を
吹き込む散気機構と紫外線照射とを併用するものなども
提案されている。
[0004] As a device for performing aeration treatment, a tower-type aeration treatment device using a packed tower or a multi-stage shelf tower, and an air blowing-type aeration treatment device for blowing air into a tank are used in chemical plants and exhaust gas treatment. There are many uses. Further, as disclosed in Japanese Patent Application Laid-Open No. 2-75391, there has been proposed a device that uses both an air blowing mechanism for blowing air and ultraviolet irradiation.

【0005】[0005]

【発明が解決しようとする課題】ところで、従来公知の
曝気処理法ないし処理装置は、いずれも液境膜をフラッ
ティングやバブリングさせ、汚染物質の気化を高めて曝
気処理をするものであるが、高効率で処理をするために
は塔式の場合、高充填層や多段にする必要があり、また
空気吹込式の場合、多重槽構造とする必要があり、その
ため、塔高が高くなったり、設置面積が広くなったりす
るという問題があった。この問題を解決するために、特
開平5−92181号公報では、塔を複数塔に分割し、
曝気処理を工夫して塔高を低減させることが開示されて
いるが、この提案のものでは、設置面積が逆に増大する
ことになり、装置の小型化を図ることはできない。
By the way, any of the conventionally known aeration methods or apparatuses perform the aeration process by flooding or bubbling a liquid film to increase the vaporization of contaminants. In order to treat with high efficiency, in the case of a tower type, it is necessary to have a high packed bed or multiple stages, and in the case of an air blowing type, it is necessary to have a multi-tank structure, so that the tower height becomes high, There was a problem that the installation area became large. To solve this problem, JP-A-5-92181 discloses that a tower is divided into a plurality of towers,
It is disclosed that the height of the tower is reduced by devising aeration treatment. However, with this proposal, the installation area increases, and the size of the apparatus cannot be reduced.

【0006】また、揚水地下水などは、揚水場所や深度
により硬度成分、濁度及び汚染濃度が変動するため、曝
気処理が不安定になり、場合によっては揚水に含まれる
汚泥や砂によって閉塞状態になることがあり、前工程に
排砂汚泥処理を必要とするなどの問題もある。
In addition, pumped groundwater and the like vary in hardness component, turbidity, and pollutant concentration depending on the pumping location and depth, so that aeration treatment becomes unstable, and in some cases, is blocked by sludge or sand contained in the pumped water. There is also a problem that the wastewater sludge treatment is required in the previous process.

【0007】さらに、曝気処理装置は居住地域に設置さ
れることも多く、その場合、例えば特開平9−9456
7号公報に開示されるように騒音対策を講じる必要があ
る。また、敷地面積に制限がある場合が多く、装置の小
型化が求められており、曝気処理装置を簡単に移動ある
いは車載可能にすることも求められている。しかるに、
従来公知の曝気処理装置では、上述の如く塔高や設置面
積が大きいことから、騒音対策費、据付費、移動費及び
メンテナンス費等が嵩むなどの問題もある。
Further, the aeration processing apparatus is often installed in a residential area, in which case, for example, Japanese Patent Application Laid-Open No. 9-9456.
It is necessary to take noise countermeasures as disclosed in Japanese Patent No. In addition, the area of the site is often limited, and the size of the device is required to be reduced, and it is also required that the aeration processing device can be easily moved or mounted on a vehicle. However,
Conventionally known aeration apparatuses have large tower heights and installation areas as described above, and thus have problems such as increased noise control costs, installation costs, moving costs, maintenance costs, and the like.

【0008】本発明はかかる諸点に鑑みてなされたもの
であり、その課題とするところは、揮発性有機化合物を
含有する揚水等の硬度成分、濁度及び濃度などに影響さ
れずに高効率で曝気処理ができる曝気処理方法を提供
し、また同時に、この方法の実施に適しかつ装置の小型
化を図り得る曝気処理装置を提供するものである。
[0008] The present invention has been made in view of the above-mentioned points, and it is an object of the present invention to provide a highly efficient method without being affected by hardness components such as pumped water containing volatile organic compounds, turbidity and concentration. It is an object of the present invention to provide an aeration treatment method capable of performing aeration treatment, and at the same time, to provide an aeration treatment device suitable for carrying out this method and capable of reducing the size of the device.

【0009】[0009]

【課題を解決するための手段】上記の課題を解決するた
め、請求項1に係る発明は、揮発性有機化合物を含有す
る水を曝気処理する曝気処理方法として、予め曝気室内
の中心部に複数の翼を有する遠心回転盤を配置する。そ
して、この遠心回転盤を回転させるとともに、遠心回転
盤の中心部に向けて上記水を注入して遠心回転盤の回転
による遠心力で微粒子化し、吸引した空気と接触させて
曝気処理をする。この曝気処理方法では、揮発性有機化
合物を含有する揚水などの水が遠心力で微粒子化されて
吸引空気で曝気されるため、揚水等の硬度成分、濁度及
び濃度などに影響されることなく、高効率で曝気処理が
行われることになる。
Means for Solving the Problems To solve the above-mentioned problems, the invention according to claim 1 is an aeration treatment method for aerating water containing a volatile organic compound. A centrifugal wheel with wings is arranged. Then, while rotating the centrifugal rotating disk, the water is injected toward the center of the centrifugal rotating disk, and fine particles are formed by centrifugal force generated by the rotation of the centrifugal rotating disk. In this aeration treatment method, since water such as pumped water containing volatile organic compounds is atomized by centrifugal force and aerated with suction air, it is not affected by hardness components such as pumped water, turbidity and concentration. Thus, the aeration process is performed with high efficiency.

【0010】請求項2に係る発明は、揮発性有機化合物
を含有する水を曝気処理する曝気処理装置として、少な
くとも1つの曝気室を有しかつこの曝気室の側壁の中心
部に開口部を設けたケーシングと、上記ケーシングの曝
気室内の中心部に上記開口部に対向して配置された複数
の翼を有する遠心回転盤と、この遠心回転盤を回転軸を
介して回転駆動する駆動手段と、上記開口部を通してケ
ーシングの曝気室内に挿入され、上記水を遠心回転盤の
中心部に向けて注入する注入管とを備え、上記注入管に
より注入した水を遠心回転盤の回転による遠心力で微粒
子化し、上記開口部から吸引した空気と接触させて曝気
処理をするように構成する。この構成では、注入管によ
り注入した水が遠心回転盤の回転による遠心力で確実に
微粒子化されて吸引空気に曝気されるため、高効率の曝
気処理を比較的簡単な構成で確実に確保することができ
る。
According to a second aspect of the present invention, as an aeration apparatus for aerating water containing a volatile organic compound, at least one aeration chamber is provided, and an opening is provided at the center of the side wall of the aeration chamber. A casing, a centrifugal rotating disk having a plurality of blades disposed at the center of the casing in the aeration chamber so as to face the opening, and driving means for rotating the centrifugal rotating disk via a rotating shaft; An injection pipe that is inserted into the aeration chamber of the casing through the opening and injects the water toward the center of the centrifugal wheel; Then, the aeration process is performed by bringing the air into contact with the air sucked from the opening. In this configuration, since the water injected by the injection pipe is surely atomized by the centrifugal force generated by the rotation of the centrifugal rotating disk and is aerated with the suction air, high-efficiency aeration processing is ensured with a relatively simple configuration. be able to.

【0011】請求項3及び4に係る発明は、いずれも請
求項2記載の曝気処理装置の遠心回転盤による水の微粒
子化を高める上で好ましい具体的構成を提供する。すな
わち、請求項3に係る発明の場合、上記遠心回転盤は、
回転軸に固定された主板と、上記開口部に対応した中心
開口部を有する副板と、上記主板と副板との間にこれら
と平行に配置されかつ副板と同様な中心開口部を有する
1枚又は複数枚の分散板とを備え、この分散板と主板又
は副板との間並びに隣接する分散板同士の間にそれぞれ
複数の翼が円周方向に所定間隔毎にかつ半径方向に湾曲
して延びて設けられてなる構成とする。この構成では、
注入管により注入した水が遠心回転盤の回転による遠心
力で微粒子化されるに際し、主板と副板と分散板と翼と
で細分化して構成された多数の通路を通って注入水が遠
心回転盤の幅方向(軸方向)全周に亘って略均一に分散
して微粒子化されることになり、微粒子化が高められ
る。
Each of the inventions according to claims 3 and 4 provides a preferable specific structure for enhancing the atomization of water by the centrifugal rotating disk of the aeration treatment apparatus according to claim 2. That is, in the case of the invention according to claim 3, the centrifugal wheel is
A main plate fixed to the rotating shaft, a sub-plate having a central opening corresponding to the opening, and a central opening disposed between and parallel to the main plate and the sub-plate and similar to the sub-plate; One or more dispersing plates are provided, and a plurality of blades are respectively curved at predetermined intervals in the circumferential direction and radially between the dispersing plates and the main plate or the auxiliary plate and between adjacent dispersing plates. And is provided so as to extend. In this configuration,
As the water injected by the injection pipe is atomized by the centrifugal force generated by the rotation of the centrifugal rotating disk, the injected water is centrifugally rotated through a number of passages that are subdivided into a main plate, sub-plates, dispersion plates, and blades. The particles are dispersed substantially uniformly over the entire circumference in the width direction (axial direction) of the board and are atomized, whereby the atomization is enhanced.

【0012】また、請求項4に係る発明の場合、上記遠
心回転盤は、回転軸に固定された主板と、上記開口部に
対応した中心開口部を有する副板とを備え、上記主板と
副板との間に複数の翼が円周方向に所定間隔毎にかつ半
径方向に湾曲して延びて設けられてなり、上記各翼の表
面には翼長方向に延びる凸条部が翼幅方向に所定間隔毎
に複数形成されている構成とする。この構成では、注入
管により注入した水が遠心回転盤の回転による遠心力で
微粒子化されるに際し、その注入水は、主板と副板と翼
とで構成された通路を翼表面の凸条部により遠心回転盤
の幅方向(軸方向)に整流されながら通ることによっ
て、その軸方向全周に亘って略均一に分散して微粒子化
されることになる。
Further, in the case of the invention according to claim 4, the centrifugal rotating disk includes a main plate fixed to a rotating shaft, and a sub-plate having a central opening corresponding to the opening, and the main plate and the sub-plate. A plurality of wings are provided at predetermined intervals in the circumferential direction and curved in the radial direction between the wings, and a ridge extending in the wing length direction is provided on the surface of each wing in the wing width direction. Are formed at predetermined intervals. With this configuration, when the water injected by the injection pipe is atomized by centrifugal force due to the rotation of the centrifugal rotating disk, the injected water passes through the passage formed by the main plate, the sub plate, and the wings on the wing surface of the wing surface. As a result, the fluid passes while being rectified in the width direction (axial direction) of the centrifugal rotary disk, and is thus dispersed substantially uniformly over the entire circumference in the axial direction to become fine particles.

【0013】請求項5に係る発明は、請求項3又は4記
載の曝気処理装置において、上記注入管の先端部を上記
副板の中心開口部より遠心回転盤内に挿入するととも
に、その挿入部分に遠心回転盤の軸方向に沿って複数の
注入穴を設ける構成とする。この構成では、遠心回転盤
内に挿入された注入管先端部の複数の注入穴より水が遠
心回転盤の幅方向全体に略均一に分散して注入されるこ
とになり、遠心回転盤の構成と相俟って注入水の微粒子
化が一層高められる。
According to a fifth aspect of the present invention, in the aeration processing apparatus according to the third or fourth aspect, the distal end of the injection pipe is inserted into the centrifugal rotary disc through the central opening of the sub-plate, and the insertion portion is provided. Is provided with a plurality of injection holes along the axial direction of the centrifugal turntable. In this configuration, water is substantially uniformly dispersed and injected over the entire width direction of the centrifugal rotary disk from a plurality of injection holes at the tip of the injection pipe inserted into the centrifugal rotary disk. In addition, the atomization of the injection water can be further reduced.

【0014】請求項6に係る発明は、上記駆動手段にお
いて、液中に含まれる揮発性有機化合物の濃度に応じ
て、遠心回転盤の周速を変更調整可能に設ける構成とす
る。この構成では、液中に含まれる揮発性有機化合物の
濃度に応じて、遠心回転盤の周速が変更調整され、それ
に伴い気液比が変えられることによって経済的な曝気処
理が可能になる。
According to a sixth aspect of the present invention, in the driving means, the peripheral speed of the centrifugal rotary disc is provided so as to be adjustable in accordance with the concentration of the volatile organic compound contained in the liquid. In this configuration, the peripheral speed of the centrifugal wheel is changed and adjusted according to the concentration of the volatile organic compound contained in the liquid, and the gas-liquid ratio is changed accordingly, thereby enabling economical aeration.

【0015】[0015]

【発明の実施の形態】以下、本発明の実施の形態を図面
に基づいて説明する。図1は本発明の第1の実施形態に
係る曝気処理装置Aを示し、この曝気処理装置Aは、揮
発性有機化合物を含有する地下水等を揚水した後に曝気
処理するためのものであり、略円筒状のケーシング1を
備えている。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 shows an aeration treatment apparatus A according to a first embodiment of the present invention. The aeration treatment apparatus A is for performing aeration treatment after pumping groundwater or the like containing a volatile organic compound. A cylindrical casing 1 is provided.

【0016】上記ケーシング1は、中心軸を通る水平面
で分離可能な2つの部分からなり、その内部は、2枚の
隔壁2,3により軸方向に吸入室4と曝気室5と吐出室
6とに仕切られいている。曝気室5の入口側側壁である
隔壁2の中心部には吸入室4と曝気室5とを連通する吸
入開口部7が設けられているとともに、曝気室5の出口
側側壁である隔壁3の中心部には曝気室5と吐出室6と
を連通する吐出開口部8が設けられている。
The casing 1 is composed of two parts which can be separated on a horizontal plane passing through the central axis, and the interior thereof is axially divided by two partition walls 2 and 3 into a suction chamber 4, an aeration chamber 5 and a discharge chamber 6. It is divided into. A suction opening 7 communicating the suction chamber 4 and the aeration chamber 5 is provided at a central portion of the partition 2 which is an inlet side wall of the aeration chamber 5, and a partition 3 which is an outlet side wall of the aeration chamber 5 is provided. A discharge opening 8 communicating the aeration chamber 5 and the discharge chamber 6 is provided at the center.

【0017】上記曝気室5内の中心部には吸入開口部7
に対向して遠心回転盤11が配置されており、この遠心
回転盤11は回転軸12と一体的に回転するようになっ
ている。遠心回転盤11は、図2及び図3に拡大詳示す
るように、回転軸12に固定された主板13と、上記吸
入開口部7に対応した中心開口部14を有する副板15
と、上記主板13と副板15との間にこれらと平行に配
置されかつ副板15と同様な中心開口部16を有する複
数枚(図では3枚)の分散板17,17,…とを備え、
この分散板17と主板13又は副板15との間並びに隣
接する分散板17,17同士の間にはそれぞれ半径方向
に円弧状に湾曲して延びる複数の平板状の翼18,1
8,…が円周方向に所定間隔毎に設けられており、これ
らの翼18,18,…は、回転軸12の方向に隣接する
もの同士では円周方向の位相がずれて遠心回転盤11の
外側から平面的に見て千鳥状に配列されている。
In the center of the aeration chamber 5, a suction opening 7 is provided.
A centrifugal rotating disk 11 is disposed opposite to the rotating shaft 12, and the centrifugal rotating disk 11 rotates integrally with the rotating shaft 12. As shown in detail in FIGS. 2 and 3, the centrifugal rotating disk 11 includes a main plate 13 fixed to a rotating shaft 12 and a sub-plate 15 having a center opening 14 corresponding to the suction opening 7.
And a plurality (three in the figure) of dispersing plates 17, 17,... Disposed between the main plate 13 and the sub-plate 15 in parallel with them and having the same central opening 16 as the sub-plate 15. Prepared,
Between the dispersing plate 17 and the main plate 13 or the sub plate 15 and between the adjacent dispersing plates 17, 17, a plurality of flat blades 18, 1 each extending in a radially arcuately curved shape.
Are provided at predetermined intervals in the circumferential direction, and the blades 18, 18,... Adjacent to each other in the direction of the rotary shaft 12 are out of phase in the circumferential direction and Are arranged in a zigzag pattern when viewed two-dimensionally from the outside.

【0018】上記副板15の中心開口部14の周囲には
リング状のカラー19が設けられており、このカラー1
9は、隔壁2の吸入開口部7に装着した円筒状部材20
の外周面上に回転自在に嵌合されている。
A ring-shaped collar 19 is provided around the center opening 14 of the sub-plate 15.
9 is a cylindrical member 20 attached to the suction opening 7 of the partition 2
Is rotatably fitted on the outer peripheral surface of the.

【0019】上記遠心回転盤11の材質については、特
に制限があるわけではないが、駆動エネルギーの消費を
少なくするためには、比強度が大きい材質が好適であ
り、耐食性や耐磨耗性を考慮すれば軽合金や強化プラス
チックが好ましい。
The material of the centrifugal rotary disk 11 is not particularly limited, but a material having a large specific strength is suitable for reducing the consumption of driving energy, and a material having high corrosion resistance and abrasion resistance is preferred. Considering this, light alloys and reinforced plastics are preferred.

【0020】上記回転軸12は、ケーシング1の中心軸
に沿ってケーシング1内を貫通して延びているととも
に、ケーシング1の左右の側壁部1a,1bにそれぞれ
パッキンシール21を介して回転自在に支持されてい
る。この回転軸12の一端には駆動手段22が動力伝達
可能に連結されている。この駆動手段22は、図で詳示
していないが、電動モータ等のアクチュエータと多段変
速又は連続変速可能な減速機構とを備え、曝気処理をす
る揚水に含まれる揮発性有機化合物の濃度に応じて、遠
心回転盤11の回転速度ないし周速を変更調整可能に設
けられている。
The rotary shaft 12 extends through the inside of the casing 1 along the central axis of the casing 1, and is rotatably mounted on the left and right side walls 1a, 1b of the casing 1 via packing seals 21, respectively. Supported. A driving means 22 is connected to one end of the rotating shaft 12 so as to transmit power. Although not shown in detail in the figure, the driving unit 22 includes an actuator such as an electric motor and a speed-reduction mechanism capable of multi-speed or continuous speed change, and according to the concentration of the volatile organic compound contained in the water to be aerated. The rotational speed or the peripheral speed of the centrifugal rotating disk 11 is provided so as to be changeable and adjustable.

【0021】一方、上記ケーシング1の側壁部1aには
吸入室4内に空気を導き入れるための空気吸引口26が
設けられているとともに、揮発性有機化合物を含有する
揚水を注入するための注入管27がケーシング1の吸入
室4内を通って隔壁2の吸入開口部7より曝気室5内に
挿入されている。この注入管27の先端部は、遠心回転
盤11の副板15の中心開口部14より遠心回転盤11
の内部にまで挿入されており、その挿入部分には遠心回
転盤11の軸方向に沿って複数(図では分散板17の枚
数より一つ多い四つ)の注入穴28,28,…が設けら
れている。
On the other hand, an air suction port 26 for introducing air into the suction chamber 4 is provided in the side wall 1a of the casing 1, and an injection port for injecting pumped water containing a volatile organic compound. A pipe 27 passes through the suction chamber 4 of the casing 1 and is inserted into the aeration chamber 5 through the suction opening 7 of the partition wall 2. The distal end of the injection pipe 27 is moved from the center opening 14 of the sub-plate 15 of the centrifugal
Are provided in the inserted portion along the axial direction of the centrifugal rotating disk 11 (in the figure, four injection holes 28, one more than the number of the dispersion plates 17). Have been.

【0022】また、ケーシング1の周壁部1cには曝気
室5内の下部より曝気された浄化水を排出するための浄
化水排出口31が設けられているとともに、ケーシング
1の側壁部1bには吐出室6から曝気ガスを排出するた
めの曝気ガス吐出口32が設けられている。上記曝気ガ
ス吐出口32は、図示していないが、活性炭吸着塔など
の公知の排ガス処理装置にガス管を介して連通されてい
て、排出される曝気ガスを浄化して大気に放出するよう
になっている。
The peripheral wall 1c of the casing 1 is provided with a purified water discharge port 31 for discharging purified water aerated from a lower portion in the aeration chamber 5, and the side wall 1b of the casing 1 is provided with a purified water discharge port 31. An aeration gas discharge port 32 for discharging the aeration gas from the discharge chamber 6 is provided. Although not shown, the aeration gas discharge port 32 is connected to a known exhaust gas treatment device such as an activated carbon adsorption tower via a gas pipe so that the discharged aeration gas is purified and released to the atmosphere. Has become.

【0023】尚、36はケーシング1の据付部材、37
は吐出室6内の曝気ガス吐出口32寄りに設けられたミ
ストエリネータであって、吐出室6内を通過する曝気ガ
ス中の同伴ミストを捕捉するためのものである。
Reference numeral 36 denotes an installation member for the casing 1;
Reference numeral denotes a mist eliminator provided in the discharge chamber 6 near the aeration gas discharge port 32, for capturing accompanying mist in the aeration gas passing through the discharge chamber 6.

【0024】次に、上記曝気処理装置Aの作動について
説明するに、この装置Aで曝気処理をするときには、駆
動手段22により回転軸12を介して遠心回転盤11を
回転させるとともに、揮発性有機化合物を含有する揚水
を注入管27を通して遠心回転盤11の中心部に向けて
注入する。すると、その水は、遠心回転盤11の回転に
よる遠心力により曝気室5内の遠心回転盤11周囲に放
射状に飛散して霧状に微粒子化され、吸入室4側より吸
入開口部7を通して曝気室5内に吸引された空気と接触
することにより、液中に含有する揮発性有機化合物が曝
気される。そして、曝気された浄化水は浄化水排出口3
1からケーシング1外に排出される一方、空気と混合し
た曝気ガスは、吐出開口部8を通って吐出室6に流入
し、吐出室6内のミストエリネータ37により同伴ミス
トが捕捉された後、曝気ガス吐出口32から排ガス処理
装置に導かれる。
Next, the operation of the aeration processing apparatus A will be described. When performing the aeration processing using the apparatus A, the centrifugal rotating disk 11 is rotated by the driving means 22 via the rotary shaft 12 while the volatile organic compound is used. The pumped water containing the compound is injected through the injection pipe 27 toward the center of the centrifugal wheel 11. Then, the water is scattered radially around the centrifugal rotating disk 11 in the aeration chamber 5 by the centrifugal force generated by the rotation of the centrifugal rotating disk 11 to be atomized into fine particles, and is aerated through the suction opening 7 from the suction chamber 4 side. By contacting the air sucked into the chamber 5, the volatile organic compound contained in the liquid is aerated. And the purified water that has been aerated is purified water outlet 3
While the aerated gas mixed with the air is discharged from the casing 1 to the outside of the casing 1, the aerated gas flows into the discharge chamber 6 through the discharge opening 8, and the entrained mist is captured by the mist eliminator 37 in the discharge chamber 6. , From the aeration gas discharge port 32 to the exhaust gas treatment device.

【0025】このような曝気処理によれば、揮発性有機
化合物を含有する揚水が遠心力で微粒子化されて吸引空
気で曝気されるため、揚水の硬度成分、濁度及び濃度な
どに影響されることなく、高効率で曝気処理を行うこと
ができる。また、遠心力で曝気処理の高効率化を図るも
のであることから、装置の小型・軽量化を図ることがで
き、その結果、据付面積を減少させることができるとと
も、移動及び車載を簡単に行うことができ、更に騒音対
策費、据付費及びメンテナンス費等の低減化をも図るこ
とができる。同時に、注入管27からの注水による洗浄
効果も加わり、液中に含まれている汚泥や砂などによる
閉塞も起こらず、前工程で排砂汚泥処理を必要とせず安
定した曝気処理を行うことができる。
According to such aeration treatment, since the pumped water containing the volatile organic compound is atomized by centrifugal force and aerated with the suction air, it is affected by the hardness component, turbidity and concentration of the pumped water. Thus, the aeration process can be performed with high efficiency. In addition, the centrifugal force increases the efficiency of the aeration process, so the size and weight of the device can be reduced. As a result, the installation area can be reduced, and moving and mounting on a vehicle can be simplified. In addition, noise reduction costs, installation costs, maintenance costs, and the like can be reduced. At the same time, the washing effect by the water injection from the injection pipe 27 is added, the clogging by the sludge or sand contained in the liquid does not occur, and the stable aeration treatment can be performed without the necessity of the sand discharge sludge treatment in the previous process. it can.

【0026】その上、上記遠心回転盤11は、主板13
と副板15と分散板17と翼18とによって細分化され
た多数の遠心通路を有する構成になっているため、注入
管27により注入した水が遠心回転盤11の幅方向(軸
方向)全周に亘って略均一に分散して微粒子化されるこ
とになり、微粒子化ひいては曝気処理の高効率化を高め
ることができる。また、注入管27の先端部は、副板1
5の中心開口部14より遠心回転盤11内に挿入されて
いるとともに、その挿入部分に遠心回転盤11の軸方向
に沿って複数の注入穴28,28,…を有しているた
め、この注入管27の各注入穴28から注入する水を遠
心回転盤11の幅方向全体に略均一に分散させることが
できるので、曝気処理の高効率化を一層高めることがで
きる。
In addition, the centrifugal turntable 11 has a main plate 13
, The sub-plate 15, the dispersion plate 17, and the blades 18, so that water is injected through the injection pipe 27 in the width direction (axial direction) of the centrifugal rotating disk 11. The particles are substantially uniformly dispersed over the circumference to be finely divided, and the fineness of the fine particles, and hence the efficiency of the aeration treatment, can be improved. In addition, the tip of the injection tube 27 is
5 is inserted into the centrifugal rotating disk 11 through the central opening 14 of the centrifugal rotating disk 11 and has a plurality of injection holes 28, 28,. Since the water injected from each injection hole 28 of the injection pipe 27 can be dispersed substantially uniformly throughout the width of the centrifugal rotary plate 11, the efficiency of the aeration process can be further enhanced.

【0027】さらに、遠心回転盤11を回転駆動する駆
動手段22は、遠心回転盤11の回転速度ないし周速を
変更調整可能に設けられているため、注入水に含まれる
揮発性有機化合物の濃度に応じて周速を変更して気液比
を変えることができ、経済的な曝気処理を確保すること
ができる。この場合、遠心回転盤11の周速は、20m
/s以下では液の微粒子化が十分でなく、曝気効率の低
下を招く一方、50m/s以上では駆動エネルギーの消
費が過大となるため、20〜50m/sの範囲が好まし
い。より好ましくは液の微粒子化が50〜100ミクロ
ンとなる、30〜40m/sである。
Further, since the driving means 22 for rotating the centrifugal rotating disk 11 is provided so as to be able to change and adjust the rotation speed or the peripheral speed of the centrifugal rotating disk 11, the concentration of the volatile organic compound contained in the injection water is adjusted. , The gas-liquid ratio can be changed by changing the peripheral speed, and economical aeration can be ensured. In this case, the peripheral speed of the centrifugal rotary disc 11 is 20 m
If it is less than / m, the liquid is not sufficiently atomized and the aeration efficiency is lowered. On the other hand, if it is more than 50 m / s, the drive energy is excessively consumed, so that the range of 20 to 50 m / s is preferable. More preferably, it is 30 to 40 m / s, which makes the liquid fine particles 50 to 100 microns.

【0028】ここで、上記曝気処理装置Aを用いて曝気
処理を行った実験の濃度測定結果を下記の表1に示す。
この実験では、トリクロロエチレンを0.455mg/
l平均で含む原水を直径900mm、幅700mmのケ
ーシング1に内蔵された直径450mmの遠心回転盤1
1に向けて注水し、900Nm/hrの空気を吸引
し、気液比G/L=100,150,200にて曝気処
理を行った。水温は20℃、気温は17℃であった。
Table 1 below shows the results of concentration measurement in experiments in which aeration was performed using the aeration apparatus A.
In this experiment, trichlorethylene was added at 0.455 mg /
l A centrifugal rotary plate 1 with a diameter of 450 mm incorporated in a casing 1 with a diameter of 900 mm and a width of 700 mm containing raw water
Water was injected toward 1, air at 900 Nm 3 / hr was suctioned, and aeration was performed at a gas-liquid ratio of G / L = 100, 150, 200. The water temperature was 20 ° C and the air temperature was 17 ° C.

【0029】[0029]

【表1】 表1の実験結果からは、本発明の第1の実施形態に係る
曝気処理装置Aによれば、揮発性有機化合物であるトリ
クロロエチレンの浄化水での濃度が、原水でのそれと比
べて約10分の1以下にまで減少でき、またその減少率
は気液比が大きい程大きくなることが分かる。
[Table 1] From the experimental results in Table 1, according to the aeration apparatus A according to the first embodiment of the present invention, the concentration of trichloroethylene, which is a volatile organic compound, in purified water is about 10 minutes longer than that in raw water. It can be seen that the ratio can be reduced to 1 or less, and the reduction rate increases as the gas-liquid ratio increases.

【0030】尚、上記第1の実施形態では、遠心回転盤
11の翼18を、回転軸12の方向に隣接するもの同士
では円周方向の位相をずらして遠心回転盤11の外側か
ら平面的に見て千鳥状に配列したが、翼18の配列形態
としては、これに特に限定されるものではなく、気液が
遠心回転盤11内を同時に通過するとき、遠心力による
気液の重力差偏流を防ぎ、気液の遠心飛散を妨げない形
態であればよい。また、分散板17の枚数は、枚数の増
加に比例して曝気効率が向上するため、設計風量及び静
圧によって決定された翼数、並びに主板13と副板15
との間隔に応じて1〜4枚の範囲にすればよい。
In the first embodiment, the blades 18 of the centrifugal rotary disk 11 are arranged such that the blades 18 adjacent to each other in the direction of the rotary shaft 12 are shifted in phase in the circumferential direction so as to be flat from the outside of the centrifugal rotary disk 11. However, the arrangement of the wings 18 is not particularly limited to this. When the gas and liquid simultaneously pass through the centrifugal rotating disk 11, the gravitational difference between the gas and liquid due to the centrifugal force is generated. Any form may be used as long as it prevents drifting and does not hinder gas-liquid centrifugal scattering. In addition, the number of the dispersion plates 17 is increased in proportion to the increase in the number of the distribution plates, so that the aeration efficiency is improved.
May be set in the range of 1 to 4 sheets depending on the interval between them.

【0031】図4は本発明の第2の実施形態に係る曝気
処理装置Bを示し、この曝気処理装置Bは円筒状のケー
シング41を備えており、このケーシング41の内部
は、4つの隔壁42,43,44,45により軸方向に
一次吐出室46と一次曝気室47と吸気室48と二次曝
気室49と二次吐出室50とに仕切られている。
FIG. 4 shows an aeration processing apparatus B according to a second embodiment of the present invention. The aeration processing apparatus B includes a cylindrical casing 41, and the inside of the casing 41 includes four partition walls 42. , 43, 44, 45 are axially partitioned into a primary discharge chamber 46, a primary aeration chamber 47, an intake chamber 48, a secondary aeration chamber 49, and a secondary discharge chamber 50.

【0032】上記一次曝気室47の入口側側壁である隔
壁43の中心部には吸入室48と一次曝気室47とを連
通する一次吸入開口部51が設けられているとともに、
一次曝気室47の出口側側壁である隔壁42の中心部に
は一次曝気室47と一次吐出室46とを連通する一次吐
出開口部52が設けられている。また同様に、二次曝気
室49の入口側側壁である隔壁44の中心部には吸入室
48と二次曝気室49とを連通する二次吸入開口部53
が設けられているとともに、二次曝気室49の出口側側
壁である隔壁45の中心部には二次曝気室49と二次吐
出室50とを連通する二次吐出開口部54が設けられて
いる。
At the center of the partition 43, which is the inlet side wall of the primary aeration chamber 47, there is provided a primary suction opening 51 communicating the suction chamber 48 and the primary aeration chamber 47.
A primary discharge opening 52 that connects the primary aeration chamber 47 and the primary discharge chamber 46 is provided at the center of the partition 42 that is the outlet side wall of the primary aeration chamber 47. Similarly, a secondary suction opening 53 communicating the suction chamber 48 and the secondary aeration chamber 49 is provided at the center of the partition wall 44, which is an inlet side wall of the secondary aeration chamber 49.
Is provided, and a secondary discharge opening 54 that connects the secondary aeration chamber 49 and the secondary discharge chamber 50 is provided at the center of the partition wall 45 that is the outlet side wall of the secondary aeration chamber 49. I have.

【0033】上記一次及び二次曝気室47,49内の中
心部にはそれぞれ吸入開口部51,53に対向して遠心
回転盤55,55が配置されており、この両遠心回転盤
55,55は共に回転軸56廻りに一体的に回転するよ
うになっている。各遠心回転盤55は、第1の実施形態
における遠心回転盤11と同じく、回転軸56に固定さ
れた主板61と、吸入開口部51又は53に対応した中
心開口部62を有する副板63と、上記主板61と副板
63との間にこれらと平行に配置されかつ副板63と同
様な中心開口部64を有する複数枚の分散板65,6
5,…とを備え、この分散板65と主板61又は副板6
3との間並びに隣接する分散板65,65同士の間にそ
れぞれ複数の翼(図示せず)が円周方向に所定間隔毎に
かつ半径方向に湾曲して延びて設けられてなる。
Centrifugal rotating disks 55, 55 are disposed at the center portions of the primary and secondary aeration chambers 47, 49 so as to face the suction openings 51, 53, respectively. Are integrally rotated about a rotation shaft 56. Each centrifugal rotating disk 55 has a main plate 61 fixed to a rotating shaft 56 and a sub-plate 63 having a central opening 62 corresponding to the suction opening 51 or 53, similarly to the centrifugal rotating disk 11 in the first embodiment. A plurality of dispersion plates 65 and 6 disposed between the main plate 61 and the sub-plate 63 in parallel with them and having the same central opening 64 as the sub-plate 63.
, And the dispersion plate 65 and the main plate 61 or the sub plate 6
A plurality of wings (not shown) are provided at predetermined intervals in the circumferential direction and curved in the radial direction, and are provided between the dispersion plates 65 and 65 adjacent to each other.

【0034】また、上記回転軸56は、ケーシング41
の中心軸に沿ってケーシング41内を貫通して延びてい
るとともに、ケーシング41の左右の側壁部41a,4
1bにそれぞれパッキンシール71を介して回転自在に
支持されている。この回転軸12の一端には、図示して
いないが、電動モータ等のアクチュエータと多段変速又
は連続変速可能な減速機構とからなる駆動手段が動力伝
達可能に連結されている。
The rotating shaft 56 is connected to the casing 41.
Extend through the inside of the casing 41 along the central axis of the casing 41, and the left and right side walls 41a, 41 of the casing 41.
1b are rotatably supported via packing seals 71, respectively. Although not shown, a drive means including an actuator such as an electric motor and a deceleration mechanism capable of multi-speed or continuous speed change is connected to one end of the rotary shaft 12 so as to transmit power.

【0035】一方、上記ケーシング41の周壁部41c
には吸入室48内に空気を導き入れるための空気吸引口
76が設けられているとともに、揮発性有機化合物を含
有する揚水を注入するための注入管77がケーシング4
1の吸入室48内を通って隔壁43の一次吸入開口部5
1より一次曝気室47内に挿入されており、また一次浄
化水を注入するための注入管78が同じくケーシング4
1の吸入室48内を通って隔壁44の二次吸入開口部5
3より二次曝気室49内に挿入されている。上記各注入
管77,78の先端部は、それぞれ遠心回転盤55の副
板63の中心開口部62より遠心回転盤55の内部にま
で挿入されているとともに、その挿入部分に遠心回転盤
55の軸方向に沿って複数の注入穴(図示せず)を有し
ている。
On the other hand, the peripheral wall portion 41c of the casing 41
Is provided with an air suction port 76 for introducing air into the suction chamber 48, and an injection pipe 77 for injecting pumped water containing a volatile organic compound is provided in the casing 4.
, The primary suction opening 5 of the partition wall 43
1 is inserted into the primary aeration chamber 47, and an injection pipe 78 for injecting the primary purified water is also provided in the casing 4.
1 through the suction chamber 48, and the secondary suction opening 5 of the partition wall 44.
3 is inserted into the secondary aeration chamber 49. The tip of each of the injection pipes 77 and 78 is inserted from the center opening 62 of the sub-plate 63 of the centrifugal rotary disk 55 to the inside of the centrifugal rotary disk 55, and the centrifugal rotary disk 55 is inserted into the inserted portion. It has a plurality of injection holes (not shown) along the axial direction.

【0036】また、ケーシング41の周壁部41cに
は、一次曝気室47内の下部より一次曝気された一次浄
化水を排出するための一次浄化水排出口81と、二次曝
気室49内の下部より二次曝気された二次浄化水を排出
するための二次浄化水排出口82とが設けられている。
一次浄化水排出口81から排出される一次浄化水は、図
示していないが、一次浄化水槽に貯えられ、その後ポン
プにより注入管78を通して二次曝気室49内に注入さ
れるようになっている。
The primary wall of the casing 41 has a primary purified water discharge port 81 for discharging primary purified water from the lower part of the primary aeration chamber 47 and a lower part of the secondary aeration chamber 49. A secondary purified water discharge port 82 for discharging the secondary purified water that has been more secondary aerated is provided.
The primary purified water discharged from the primary purified water discharge port 81 is stored in a primary purified water tank (not shown), and is then injected into the secondary aeration chamber 49 through the injection pipe 78 by a pump. .

【0037】さらに、ケーシング41の左右両側壁部4
1a,41bにはそれぞれ一次又は二次吐出室46,5
0から曝気ガスを排出するための曝気ガス吐出口83,
84が設けられている。この各曝気ガス吐出口83,8
4は、図示していないが、活性炭吸着塔などの公知の排
ガス処理装置にガス管を介して連通されていて、排出さ
れる曝気ガスを浄化して大気に放出するようになってい
る。尚、86及び87はそれぞれ一次又は二次吐出室4
6,50内の曝気ガス吐出口83,84寄りに設けられ
たミストエリネータである。
Furthermore, the left and right side walls 4 of the casing 41
1a and 41b have primary or secondary discharge chambers 46 and 5, respectively.
Aeration gas discharge port 83 for discharging aeration gas from 0,
84 are provided. These aeration gas discharge ports 83, 8
Although not shown, 4 is connected to a known exhaust gas treatment device such as an activated carbon adsorption tower via a gas pipe, and purifies exhausted aerated gas and discharges it to the atmosphere. 86 and 87 are primary or secondary discharge chambers 4 respectively.
The mist eliminator is provided near the aeration gas discharge ports 83 and 84 in the insides 6 and 50.

【0038】そして、上記第2の実施形態の曝気処理装
置Bにおいても、第1の実施形態の曝気処理装置Aと同
じく、揮発性有機化合物を含有する揚水を遠心回転盤5
5の回転による遠心力で微粒子化し、吸引空気と接触さ
れて曝気処理をするため、揚水の硬度成分、濁度及び濃
度などに影響されることなく、高効率で曝気処理を行う
ことができる。特に、第2の実施形態の曝気処理装置B
の場合、揚水を一次曝気室47内で一次曝気処理をし、
その一次浄化水を一次浄化水排出口81から一旦排出し
て一次浄化水槽に貯えた後、それを更に二次曝気室49
内で二次曝気処理をするようにしているため、曝気効率
を一層向上させることができる。
In the aeration treatment apparatus B of the second embodiment, similarly to the aeration treatment apparatus A of the first embodiment, the pumping water containing the volatile organic compound is supplied to the centrifugal rotary disk 5.
Since the particles are atomized by the centrifugal force generated by the rotation of No. 5 and aerated by being brought into contact with the suction air, the aerated process can be performed with high efficiency without being affected by the hardness component, turbidity, concentration, etc. of the pumped water. In particular, the aeration apparatus B of the second embodiment
In the case of, the pumped water is subjected to primary aeration treatment in the primary aeration chamber 47,
After the primary purified water is once discharged from the primary purified water discharge port 81 and stored in the primary purified water tank, it is further discharged to the secondary aeration chamber 49.
Since the secondary aeration process is performed in the inside, the aeration efficiency can be further improved.

【0039】ここで、上記曝気処理装置Bを用いて曝気
処理を行った実験の濃度測定結果を下記の表2に示す。
この実験では、1,1,1−トリクロロエタンを0.1
8mg/l、トリクロロエチレンを0.24mg/l、
テトラクロロエチレンを0.44mg/l含む原水を直
径1200mm、幅1100mmのケーシング41の一
次曝気室47内に注入して一次曝気処理を行い、次いで
その一次浄化水を二次曝気室49内に注入して二次曝気
処理を行った。水温は16℃、気温は12℃であった。
Table 2 below shows the results of concentration measurement in experiments in which aeration was performed using the aeration apparatus B.
In this experiment, 1,1,1-trichloroethane was added at 0.1%.
8 mg / l, 0.24 mg / l of trichlorethylene,
Raw water containing 0.44 mg / l of tetrachloroethylene is injected into the primary aeration chamber 47 of the casing 41 having a diameter of 1200 mm and a width of 1100 mm to perform primary aeration, and then the primary purified water is injected into the secondary aeration chamber 49. Secondary aeration was performed. The water temperature was 16 ° C and the air temperature was 12 ° C.

【0040】[0040]

【表2】 表2の実験結果からは、本発明の第2の実施形態に係る
曝気処理装置Bによれば、揮発性有機化合物である1,
1,1−トリクロロエタン、トリクロロエチレン及びテ
トラクロロエチレンの一次浄化水での濃度は、いずれも
原水でのそれと比べて10分の1程度に減少でき、また
二次浄化水での濃度は、一次浄化水でのそれと比べて更
に10分の1程度に減少できることが分かる。
[Table 2] From the experimental results in Table 2, according to the aeration apparatus B according to the second embodiment of the present invention, the volatile organic compound 1,
The concentration of 1,1-trichloroethane, trichloroethylene and tetrachloroethylene in the primary purified water can be reduced to about 1/10 compared to that in the raw water, and the concentration in the secondary purified water can be reduced in the primary purified water. It can be seen that this can be further reduced to about one tenth.

【0041】尚、本発明の曝気処理装置は上記第1及び
第2の実施形態に限定されるものではなく、その他種々
の形態を包含するものである。例えば、上記各実施形態
では、遠心回転盤11,55として、主板13,61と
副板15,63と分散板17,65と複数の翼18とで
構成したが、分散板を省いた構成としてもよい。
The aeration apparatus of the present invention is not limited to the first and second embodiments, but includes various other forms. For example, in each of the above-described embodiments, the centrifugal rotating disks 11 and 55 are configured by the main plates 13 and 61, the auxiliary plates 15 and 63, the dispersion plates 17 and 65, and the plurality of blades 18. Is also good.

【0042】すなわち、図5及び図6に示すように、主
板91と副板92と間に複数の幅広の翼93を円周方向
に所定間隔毎にかつ半径方向に湾曲させて延ばして設け
る構成とする。そして、上記各翼93の表面に、翼長方
向に延びる複数(図では4つの)の断面矩形状の凸条部
96,96,…を幅方向両側と中間の所定間隔位置毎に
形成する。
That is, as shown in FIGS. 5 and 6, a plurality of wide wings 93 are provided between the main plate 91 and the sub-plate 92 at predetermined intervals in the circumferential direction and curved in the radial direction to extend. And A plurality of (four in the figure) rectangular ridges 96, 96,... Extending in the wing length direction are formed on the surface of each of the wings 93 at predetermined intervals between both sides in the width direction and an intermediate position.

【0043】この構成の場合、遠心回転盤の中心部に向
けて注入した揚水が遠心回転盤の回転による遠心力で微
粒子化されるに際し、その注入水は、主板91と副板9
2と翼93とで構成された通路を翼93表面の凸条部9
6により遠心回転盤の幅方向(軸方向)に整流されなが
ら通ることによって、その軸方向全周に亘って略均一に
分散して微粒子化されるため、その微粒子化を高めるこ
とができる。尚、翼93の表面に形成する凸条部として
は、図7に示すような断面三角形状の凸条部97とした
り、図8に示すような波形形状の凸条部98としたりし
てもよい。
In the case of this configuration, when the pumped water injected toward the center of the centrifugal rotary disk is atomized by the centrifugal force generated by the rotation of the centrifugal rotary disk, the injected water uses the main plate 91 and the sub-plate 9
The passage constituted by the wings 93 and the wings 93 is formed into a ridge 9 on the surface of the wings 93.
By being rectified and passed in the width direction (axial direction) of the centrifugal rotary disk by 6, the particles are substantially uniformly dispersed and atomized over the entire circumference in the axial direction, so that the atomization can be increased. The ridge formed on the surface of the wing 93 may be a ridge 97 having a triangular cross section as shown in FIG. 7 or a ridge 98 having a corrugated shape as shown in FIG. Good.

【0044】また、上記第1の実施形態に係る曝気処理
装置Aでは、ケーシング1内に1つの曝気室5を形成
し、その両側に吸入室4と吐出室6とを形成し、また第
2の実施形態に係る曝気処理装置Bでは、ケーシング4
1内に2つの曝気室47,49及び吐出室46,50と
1つの吸入室48とを形成したが、本発明の曝気処理装
置におけるケーシングの形態としては、これらに限定さ
れるものではなく、種々の組み合わせを採ることができ
るが、ケーシング内に少なくとも1つの曝気室を有すれ
ばよい。また、遠心回転軸を回転させる回転軸は、水平
方向に配置するだけでなく垂直方向に配置してもよい。
Further, in the aeration processing apparatus A according to the first embodiment, one aeration chamber 5 is formed in the casing 1, and the suction chamber 4 and the discharge chamber 6 are formed on both sides thereof. In the aeration processing apparatus B according to the embodiment, the casing 4
Although two aeration chambers 47 and 49, discharge chambers 46 and 50, and one suction chamber 48 are formed in 1, the form of the casing in the aeration processing apparatus of the present invention is not limited to these. Although various combinations can be adopted, it is sufficient that at least one aeration chamber is provided in the casing. Further, the rotating shaft for rotating the centrifugal rotating shaft may be arranged not only horizontally but also vertically.

【0045】さらに、上記各実施形態では、曝気処理装
置A,Bにおいて、揮発性有機化合物を含有する地下水
などの揚水を曝気処理する場合について述べたが、本発
明は、揚水に限らず、化学工場なでの各種水溶液の曝気
処理や酸化処理工程などの分野にも適用することができ
るのは言うまでもない。
Further, in each of the above-described embodiments, a case has been described in which aeration treatment is performed on pumped water such as groundwater containing a volatile organic compound in the aeration treatment devices A and B. However, the present invention is not limited to pumping and is not limited to pumping. Needless to say, the present invention can be applied to fields such as aeration treatment of various aqueous solutions and oxidation treatment steps in factories.

【0046】[0046]

【発明の効果】以上のように、本発明の曝気処理方法に
よれば、揮発性有機化合物を含有する揚水などの水を遠
心回転盤の回転による遠心力で微粒子化して吸引空気で
曝気することができるので、揚水等の硬度成分、濁度及
び濃度などに影響されることなく、高効率で曝気処理を
行うことができる。
As described above, according to the aeration method of the present invention, water such as pumped water containing a volatile organic compound is atomized by centrifugal force generated by rotation of a centrifugal rotating disk and aerated with suction air. Therefore, the aeration process can be performed with high efficiency without being affected by hardness components such as water pumping, turbidity and concentration.

【0047】また、本発明の曝気処理装置によれば、比
較的簡単な構成で高効率な曝気処理を確保して、装置を
小型で軽量とすることができるので、据付面積を減少さ
せることができるととも、移動及び車載を簡単に行うこ
とができる。同時に多重操作やユニット化もでき、自由
度に優れており、更に騒音対策費、据付費及びメンテナ
ンス費等の軽減化を図ることができるなどの効果をも併
有する。
Further, according to the aeration apparatus of the present invention, it is possible to secure high-efficiency aeration processing with a relatively simple configuration and to reduce the size and weight of the apparatus, thereby reducing the installation area. If possible, it can be easily moved and mounted. At the same time, multiple operations and unitization can be performed, and the degree of freedom is excellent, and further, there is an effect that noise reduction costs, installation costs, maintenance costs, and the like can be reduced.

【0048】特に、請求項3及び4記載の発明では、注
入水を遠心回転盤の幅方向全周に亘って略均一に分散し
て微粒子化することにより、その微粒子化を高めること
ができるので、曝気処理の高効率化をより図ることがで
きる。
In particular, according to the third and fourth aspects of the present invention, since the injected water is dispersed substantially uniformly over the entire circumference in the width direction of the centrifugal rotating disk to form fine particles, the fine particles can be enhanced. In addition, the efficiency of the aeration process can be further improved.

【0049】請求項5に係る発明では、遠心回転盤内に
挿入された注入管先端部の複数の注入穴より水を遠心回
転盤の幅方向全体に略均一に分散して注入することによ
り、遠心回転盤の構成と相俟って注入水の微粒子化を一
層高めることができ、曝気処理の高効率化をより一層図
ることができる。
According to the fifth aspect of the present invention, water is substantially uniformly dispersed and injected over the entire width direction of the centrifugal rotating disk from the plurality of injection holes at the tip of the injection pipe inserted into the centrifugal rotating disk. Combined with the configuration of the centrifugal rotary disc, the atomization of the injection water can be further reduced, and the efficiency of the aeration process can be further improved.

【0050】さらに、請求項6に係る発明では、液中に
含まれる揮発性有機化合物の濃度に応じて、遠心回転盤
の周速を変更調整して気液比を変えることができるの
で、経済的な曝気処理を行うことができるという効果を
も奏する。
Further, in the invention according to the sixth aspect, the gas-liquid ratio can be changed by changing and adjusting the peripheral speed of the centrifugal rotary disk in accordance with the concentration of the volatile organic compound contained in the liquid. Also, it is possible to perform an effective aeration process.

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

【図1】本発明の第1の実施形態に係る曝気処理装置の
縦断側面図である。
FIG. 1 is a vertical sectional side view of an aeration processing apparatus according to a first embodiment of the present invention.

【図2】上記曝気処理装置の遠心回転盤の斜視図であ
る。
FIG. 2 is a perspective view of a centrifugal wheel of the aeration apparatus.

【図3】図2のX−Xにおける拡大断面図である。FIG. 3 is an enlarged sectional view taken along line XX of FIG. 2;

【図4】第2の実施形態を示す図1相当図である。FIG. 4 is a view corresponding to FIG. 1 showing a second embodiment.

【図5】別の実施形態に係る遠心回転盤の一部分の縦断
面図である。
FIG. 5 is a longitudinal sectional view of a part of a centrifugal wheel according to another embodiment.

【図6】上記遠心回転盤の翼の斜視図である。FIG. 6 is a perspective view of a wing of the centrifugal wheel.

【図7】上記翼の他の形態を示す斜視図である。FIG. 7 is a perspective view showing another embodiment of the wing.

【図8】同じく翼の他の形態を示す斜視図である。FIG. 8 is a perspective view showing another form of the wing.

【符号の説明】[Explanation of symbols]

A,B 曝気処理装置 1,41 ケーシング 5 曝気室 7 吸入開口部 11,55 遠心回転盤 12,56 回転軸 13,61,91 主板 14,16,62,64 中心開口部 15,63,92 副板 17,65 分散板 18,93 翼 22 駆動手段 27,77,78 注入管 28 注入穴 47 一次曝気室 49 二次曝気室 51 一次吸入開口部 53 二次吸入開口部 96,97,98 凸条部 A, B Aeration treatment device 1, 41 Casing 5 Aeration chamber 7 Suction opening 11, 55 Centrifugal rotary plate 12, 56 Rotating shaft 13, 61, 91 Main plate 14, 16, 62, 64 Central opening 15, 63, 92 Sub Plate 17, 65 Dispersion plate 18, 93 Blade 22 Drive means 27, 77, 78 Injection tube 28 Injection hole 47 Primary aeration chamber 49 Secondary aeration chamber 51 Primary suction opening 53 Secondary suction opening 96, 97, 98 Ridge Department

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 揮発性有機化合物を含有する水を曝気処
理する曝気処理方法であって、 曝気室内の中心部に複数の翼を有する遠心回転盤を配置
し、この遠心回転盤を回転させるとともに、遠心回転盤
の中心部に向けて上記水を注入して遠心回転盤の回転に
よる遠心力で微粒子化し、吸引した空気と接触させて曝
気処理をすることを特徴とする曝気処理方法。
An aeration treatment method for aeration treatment of water containing a volatile organic compound, wherein a centrifugal rotating disk having a plurality of blades is arranged at a central portion in an aeration chamber, and the centrifugal rotating disk is rotated. An aeration treatment method comprising: injecting the water toward a central portion of a centrifugal rotating disk; forming fine particles by centrifugal force generated by the rotation of the centrifugal rotating disk;
【請求項2】 揮発性有機化合物を含有する水を曝気処
理する曝気処理装置であって、 少なくとも1つの曝気室を有しかつこの曝気室の側壁の
中心部に開口部を設けたケーシングと、 上記ケーシングの曝気室内の中心部に上記開口部に対向
して配置された複数の翼を有する遠心回転盤と、 この遠心回転盤を回転軸を介して回転駆動する駆動手段
と、 上記開口部を通してケーシングの曝気室内に挿入され、
上記水を遠心回転盤の中心部に向けて注入する注入管と
を備え、 上記注入管により注入した水を遠心回転盤の回転による
遠心力で微粒子化し、上記開口部から吸引した空気と接
触させて曝気処理をするように構成されていることを特
徴とする曝気処理装置。
2. An aeration treatment apparatus for aeration treatment of water containing a volatile organic compound, comprising: a casing having at least one aeration chamber and having an opening in a center of a side wall of the aeration chamber; A centrifugal rotating disk having a plurality of blades arranged in the center of the casing in the aeration chamber so as to face the opening; driving means for rotating the centrifugal rotating disk via a rotating shaft; Inserted into the aeration chamber of the casing,
An injection pipe for injecting the water toward the center of the centrifugal rotary disk, wherein the water injected by the injection pipe is atomized by centrifugal force generated by rotation of the centrifugal rotary disk, and brought into contact with air sucked from the opening. An aeration treatment apparatus characterized in that it is configured to perform an aeration treatment by using an aeration method.
【請求項3】 上記遠心回転盤は、回転軸に固定された
主板と、上記開口部に対応した中心開口部を有する副板
と、上記主板と副板との間にこれらと平行に配置されか
つ副板と同様な中心開口部を有する1枚又は複数枚の分
散板とを備え、この分散板と主板又は副板との間並びに
隣接する分散板同士の間にそれぞれ複数の翼が円周方向
に所定間隔毎にかつ半径方向に湾曲して延びて設けられ
てなる請求項2記載の曝気処理装置。
3. The centrifugal rotating disk is disposed in parallel with a main plate fixed to a rotating shaft, a sub-plate having a central opening corresponding to the opening, and between the main plate and the sub-plate. And one or more dispersing plates having a central opening similar to that of the sub-distributing plate, and a plurality of blades are formed between the dispersing plate and the main plate or the sub-distributing plate and between adjacent dispersing plates. The aeration processing apparatus according to claim 2, wherein the aeration processing apparatus is provided so as to extend at predetermined intervals in the direction and curved in the radial direction.
【請求項4】 上記遠心回転盤は、回転軸に固定された
主板と、上記開口部に対応した中心開口部を有する副板
とを備え、上記主板と副板との間に複数の翼が円周方向
に所定間隔毎にかつ半径方向に湾曲して延びて設けられ
てなり、上記各翼の表面には翼長方向に延びる凸条部が
翼幅方向に所定間隔毎に複数形成されている請求項2記
載の曝気処理装置。
4. The centrifugal rotating disk includes a main plate fixed to a rotating shaft and a sub plate having a central opening corresponding to the opening, and a plurality of blades are provided between the main plate and the sub plate. A plurality of ridges extending in the blade length direction are formed at predetermined intervals in the blade width direction on the surface of each of the wings. The aeration apparatus according to claim 2.
【請求項5】 上記注入管の先端部は、上記副板の中心
開口部より遠心回転盤内に挿入されているとともに、そ
の挿入部分に遠心回転盤の軸方向に沿って複数の注入穴
を有している請求項3又は4記載の曝気処理装置。
5. The distal end of the injection tube is inserted into the centrifugal rotating disk through the central opening of the sub-plate, and a plurality of injection holes are formed in the inserted portion along the axial direction of the centrifugal rotating disk. The aeration apparatus according to claim 3, wherein the apparatus comprises:
【請求項6】 上記駆動手段は、液中に含まれる揮発性
有機化合物の濃度に応じて、遠心回転盤の周速を変更調
整可能に設けられている請求項2〜5のいずれか一つに
記載の曝気処理装置。
6. The method according to claim 2, wherein the driving means is provided so as to be able to change and adjust the peripheral speed of the centrifugal rotating disk in accordance with the concentration of the volatile organic compound contained in the liquid. The aeration treatment device according to claim 1.
JP11142254A 1999-05-21 1999-05-21 Aeration treatment method and apparatus Withdrawn JP2000325984A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11142254A JP2000325984A (en) 1999-05-21 1999-05-21 Aeration treatment method and apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11142254A JP2000325984A (en) 1999-05-21 1999-05-21 Aeration treatment method and apparatus

Publications (1)

Publication Number Publication Date
JP2000325984A true JP2000325984A (en) 2000-11-28

Family

ID=15311052

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2000325984A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101208855B1 (en) 2012-10-15 2012-12-05 주식회사 한국건설관리공사 Water treating apparatus of reservoir water in the river
KR101208816B1 (en) 2012-10-15 2012-12-06 주식회사 한국건설관리공사 Water purification apparatus in river using the micro bubble
CN105645612A (en) * 2014-10-04 2016-06-08 沈智丰 Multistage centrifugal-atomization aerator
JP2016187772A (en) * 2015-03-30 2016-11-04 株式会社住化分析センター Gas-liquid treatment apparatus

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101208855B1 (en) 2012-10-15 2012-12-05 주식회사 한국건설관리공사 Water treating apparatus of reservoir water in the river
KR101208816B1 (en) 2012-10-15 2012-12-06 주식회사 한국건설관리공사 Water purification apparatus in river using the micro bubble
CN105645612A (en) * 2014-10-04 2016-06-08 沈智丰 Multistage centrifugal-atomization aerator
JP2016187772A (en) * 2015-03-30 2016-11-04 株式会社住化分析センター Gas-liquid treatment apparatus

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Free format text: JAPANESE INTERMEDIATE CODE: A300

Effective date: 20060801