JPH08150304A - Device for removing floating particulate - Google Patents

Device for removing floating particulate

Info

Publication number
JPH08150304A
JPH08150304A JP29653194A JP29653194A JPH08150304A JP H08150304 A JPH08150304 A JP H08150304A JP 29653194 A JP29653194 A JP 29653194A JP 29653194 A JP29653194 A JP 29653194A JP H08150304 A JPH08150304 A JP H08150304A
Authority
JP
Japan
Prior art keywords
water
trapping
fine particles
box
parallel plates
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
JP29653194A
Other languages
Japanese (ja)
Other versions
JP2908257B2 (en
Inventor
Susumu Maruyama
將 丸山
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.)
EEZEE GOMME YOKO KK
Original Assignee
EEZEE GOMME YOKO 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 EEZEE GOMME YOKO KK filed Critical EEZEE GOMME YOKO KK
Priority to JP29653194A priority Critical patent/JP2908257B2/en
Publication of JPH08150304A publication Critical patent/JPH08150304A/en
Application granted granted Critical
Publication of JP2908257B2 publication Critical patent/JP2908257B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Abstract

PURPOSE: To provide a device for removing floating particulate in which the whole equipment is directly immersed in water such as lakes and marshes, rivers and an inland sea and which is of low cost. CONSTITUTION: When dirty water is caused to flow in a removal box 2 by using a natural flow of lakes and marshes, rivers or the like and is passed between parallel plates 7 of an inclined plate group 3, particulate is precipitated by gravity and removed from the dirty water. The dirty water is caused to flow and is circulated from a fine flow hole 12, and the removed particulate is collected in a collecting space 9 below the parallel plates 7 and is properly discharged. In this way, since the natural flow is used, power for flowing in the removal box is not required. Since the influence of the water flow is restrained by the removal box, particulate precipitated on the parallel plates is prevented from stirring up.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、水や空気等の流体の
流れを利用して水中あるいは空気中の微粒子を捕捉箱の
内部で捕捉除去する浮遊微粒子捕捉除去装置に関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a floating particle trapping / removing apparatus for trapping and removing particles in water or air in a trapping box by utilizing the flow of a fluid such as water or air.

【0002】[0002]

【従来の技術】観賞魚用水槽、あるいは養殖池などにお
いては、魚の***物あるいは投餌後の残渣などにより、
水中に浮遊微粒子が発生し汚濁する。また、湖沼、河
川、内海などでは、供給される栄養塩類に起因して植物
プランクトン等の微粒子が発生浮遊し、一定の環境条件
下での大量発生により赤潮等の公害問題に発展してい
る。さらに、ビルやマンション等の高架水槽内部におい
ては、配管を通して水槽内部に鉄錆等の浮遊粒子が持ち
込まれ、沈殿集積することによる水質汚染の問題が発生
している。これらの浮遊微粒子による問題を解決するた
め、水中に浮遊する微粒子の捕捉除去技術の開発が望ま
れている。
2. Description of the Related Art In aquariums for aquariums, aquaculture ponds, etc., due to excretions of fish or residues after feeding,
Floating particles are generated in water and become polluted. Further, in lakes, rivers, inland seas, etc., fine particles such as phytoplankton are generated and suspended due to the supplied nutrient salts, and due to a large amount generated under a certain environmental condition, pollution problems such as red tide have been developed. Further, in an elevated water tank such as a building or a condominium, floating particles such as iron rust are brought into the water tank through a pipe, and there is a problem of water pollution due to sedimentation and accumulation. In order to solve the problems caused by these suspended particles, it is desired to develop a technique for capturing and removing particles suspended in water.

【0003】従来、これらの水中に浮遊する微粒子を捕
捉除去し水を浄化させる技術として、フィルターを用い
て微粒子を除去する技術や、数mm間隔の何枚かの平行
板を設置することによって、浮遊する微粒子を速く沈降
させる技術等が存在する。フィルターによる場合、捕捉
した微粒子によりフィルターが目詰まりし、その清掃や
取換えが必要となり面倒である上、フィルターの消耗に
伴うコストが発生していた。
Conventionally, as a technique for purifying water by capturing and removing fine particles floating in water, a technique of removing fine particles by using a filter or installing several parallel plates with an interval of several mm is used. There are techniques for rapidly setting floating particles. In the case of using a filter, the trapped fine particles clog the filter, which necessitates cleaning and replacement, which is troublesome, and the cost associated with the exhaustion of the filter occurs.

【0004】一方、フィルターに代って平行板を使用す
る技術としては、特開昭49−13761号公報、特公
昭56−52605号公報、特公昭61−51958号
公報、特公昭57−58206号公報、特公昭61−4
7562号公報、特開昭61−187906号公報、実
開昭59−135106号公報、実開昭61−1320
09号公報に記載されているものがある。
On the other hand, as a technique of using a parallel plate in place of a filter, Japanese Patent Laid-Open No. 49-13761, Japanese Patent Publication No. 56-52605, Japanese Patent Publication No. 61-51958, and Japanese Patent Publication No. 57-58206. Gazette, Japanese Patent Publication Sho 61-4
7562, JP-A-61-187906, JP-A-59-135106, JP-A-61-1320.
There is one described in Japanese Patent Publication No. 09.

【0005】[0005]

【発明が解決しようとする課題】ところで、平行板を使
用する浮遊微粒子の捕捉除去装置の場合は、水の流れの
無い使用環境下でのみ有効であり、一般の場合、一旦沈
降した微粒子が様々な原因によって引き起こされる水流
によって再び舞い上がるので実用的でない。すなわち、
観賞魚用水槽内で使用する場合、エアレーションによる
対流が起こり、また、湖沼、河川、海で使用する場合、
温度差、風圧等による対流、落差による流れによって水
は常に動いている。水中に微粒子が浮遊する場合、微粒
子の比重が水よりも若干ながら重いので、重力によって
沈降しようとするが、水中の流れによって舞い上がり沈
降させることが困難である。特に、浮遊する粒子が微細
であればあるほど、僅かな流れによって舞い上がり、微
粒子は浮遊し続けることになる。
By the way, in the case of a device for capturing and removing suspended particulates using a parallel plate, it is effective only in a use environment where there is no flow of water. It is not practical because it rises again due to water flow caused by various causes. That is,
When used in an ornamental fish tank, convection due to aeration occurs, and when used in lakes, rivers, or the sea,
Water is constantly moving due to convection due to temperature difference, wind pressure, etc., and flow due to drop. When the fine particles are suspended in water, the specific gravity of the fine particles is slightly heavier than that of water, so that the fine particles tend to settle by gravity, but it is difficult to fly up and settle due to the flow of water. In particular, the finer the suspended particles are, the smaller the particles flow up, and the fine particles continue to float.

【0006】そのため、上記公報記載の技術は、いずれ
も、多数の微粒子が浮遊する水(以下、汚濁水という)
を一旦、水槽内に引き入れ、自然条件による沈降微粒子
の舞い上がりを極力抑え、汚濁水の浄化を迅速に行い、
この水槽内で汚濁水を処理して浄化した後、元に戻す構
成を採用しており、装置全体を水中に沈めて汚濁処理を
行う技術ではない。
Therefore, in all of the techniques described in the above publications, water in which a large number of fine particles are suspended (hereinafter referred to as polluted water)
Once into the water tank, suppress the rising of settling particles due to natural conditions as much as possible, and quickly purify polluted water,
It employs a configuration in which polluted water is treated and purified in this water tank and then returned to its original state, and it is not a technique of submerging the entire device in water to perform the pollutant treatment.

【0007】従って、このような公報記載の技術では、
湖沼、河川、内海等の岸辺に装置設置場所を確保しなけ
ればならず、設置スペースの問題が発生し、また、汚濁
水を装置側に引き入れる動力エネルギーも必要とする
等、全体にコストが高くなるといった難点がある。
Therefore, in the technique described in such a publication,
The cost is high as a whole because the equipment installation site must be secured on the shores of lakes, rivers, inland seas, etc., and there is a problem of installation space, and power energy to draw polluted water to the equipment side is required. There is a drawback that

【0008】なお、特開昭53−95372号公報に
は、FBR用コールドトラップに適用される不純物沈降
分離装置が開示されているが、これはFBRプラントの
一構成要素として適用されるものであり、上記と同様に
浄化液を移動させる動力エネルギーを必要とする点で他
の公報記載の技術と何ら変わりなく、湖沼、河川、内海
等の汚濁水処理用としてそのまま単独で使用できる構成
となっていない。
[0008] Incidentally, Japanese Patent Laid-Open No. 53-95372 discloses an impurity sedimentation separation device applied to a cold trap for FBR, which is applied as one component of the FBR plant. In the same way as the above, it requires kinetic energy to move the purification liquid, and is no different from the technology described in other publications, and is configured to be used as it is for treating polluted water such as lakes, rivers, and inland seas. Absent.

【0009】そこで、この発明の目的とするところは、
装置全体を湖沼、河川、内海等に直接沈設できる低コス
トの浮遊微粒子の捕捉除去装置を提供するところにあ
る。
Therefore, the object of the present invention is to
An object of the present invention is to provide a low-cost trapping / removing device for suspended particles that can directly deposit the entire device in lakes, rivers, inland seas, etc.

【0010】[0010]

【課題を解決するための手段】上記目的達成のために
は、汚濁水を動力エネルギーを使用しなくても装置内部
に引き入れることができる構成、すなわち、汚濁水の処
理のためのエネルギーは自然の流れを利用できること
と、装置全体を水中に沈設しても捕捉除去機能があるこ
とが必要である。
In order to achieve the above-mentioned object, a structure in which polluted water can be drawn into the apparatus without using power energy, that is, the energy for treating the polluted water is natural. It must be able to utilize the flow and have the ability to capture and remove even if the entire device is submerged in water.

【0011】本発明者は、傾斜板群を使用した捕捉除去
手段を箱の内部に設け、箱自体を水中等の流体中に設置
できる構成とするとともに、箱の側壁に微細な穴を設け
る構成により、自然の流れによって箱の内部に汚濁水が
流入し、平行板の間を通過する際に微粒子を捕捉除去し
つつ水を箱の内外で循環させれば、箱の内部で沈降させ
た微粒子が水流によって再び舞い上がるのを防止でき、
水中の透明度を向上させ得ることを発見した。
The present inventor has a structure in which the trapping and removing means using the inclined plate group is provided inside the box so that the box itself can be installed in a fluid such as water, and a fine hole is provided in the side wall of the box. As a result, polluted water flows into the inside of the box by a natural flow, and when water is circulated inside and outside the box while capturing and removing particles when passing between parallel plates, the particles settled inside the box will flow. Prevents you from soaring again,
It has been discovered that it can improve transparency in water.

【0012】すなわち、この発明における微粒子の捕捉
除去装置として、上部に水流入口を有し水中に設置可能
な捕捉箱を設け、この捕捉箱の内部上側に平行板を所定
間隔で多数斜めに並べ、この平行板の下端部において捕
捉箱の側壁に微細な水流出穴を設けて、捕捉箱の水流入
口及び水流出穴と外部とを結ぶ循環路を形成し、この捕
捉箱内の循環路に流入した水が平行板の隙間を通過する
間に浮遊する微粒子を平行板上に沈殿させ、更に、重力
によって平行板の上面に沿って捕捉箱の底部に沈降して
いくような構成を採用した。
That is, as the device for trapping and removing fine particles in the present invention, a trap box having a water inlet at the top and which can be installed in water is provided, and a large number of parallel plates are obliquely arranged at predetermined intervals inside the trap box. A fine water outflow hole is provided on the side wall of the trap box at the lower end of this parallel plate to form a circulation path connecting the water inflow port and the water outflow hole of the trap box to the outside, and flow into the circulation path inside this trap box. The fine particles floating while the water passing through the gaps between the parallel plates were settled on the parallel plates, and were further settled by the gravity along the upper surface of the parallel plates to the bottom of the trap box.

【0013】また、この捕捉した微粒子を捕捉箱に集積
しておく空間が必要であり、さらに集積微粒子が再び捕
捉箱外部に流出するのを防ぐ必要がある。また、捕捉箱
に流入した水は再利用のため、再び捕捉箱外部に流出さ
せ循環させる必要がある。そこで、これらの条件を満足
させるために、捕捉箱の底部と傾斜板群の下端との間
に、平行板上を重力により落下してきた微粒子を集積さ
せるための微粒子集積空間を設け、捕捉箱の側壁におい
て、傾斜板群の平行板の間隔に合わせて微粒子集積空間
の最上位置に微細な流出穴を形成し、集積微粒子の外部
への流出防止と、流入した水等の再利用を可能とする構
成を採用した。
Further, a space for accumulating the trapped particles in the trap box is required, and it is necessary to prevent the accumulated particles from flowing out of the trap box again. Further, since the water that has flowed into the trap box is reused, it is necessary to flow it out of the trap box again and circulate it. Therefore, in order to satisfy these conditions, a fine particle accumulation space for accumulating fine particles that have fallen by gravity on the parallel plate is provided between the bottom of the trap box and the lower end of the inclined plate group, and On the side wall, a fine outflow hole is formed at the uppermost position of the fine particle accumulation space in accordance with the distance between the parallel plates of the inclined plate group, so that the accumulated fine particles can be prevented from flowing out and the inflowing water can be reused. Adopted the configuration.

【0014】なお、本装置を水中等の流体中に沈設する
構成を採用しているため、捕捉箱に汚濁水を流入させる
手段としては、自然のエネルギーを利用することができ
る。例えば、観賞魚用の水槽内に本装置を設置するとき
はエアレーションに伴う対流があり、ビル・マンション
等の高架水槽内部に設置するときにはヘッド圧により水
道の使用時に発生する渦流があり、さらには、河川の場
合は落差による自然の流れ、湖沼の場合には風や太陽光
の熱による温度差で起こる対流、内海の場合は潮流等が
あり、これらの流れを利用すれば汚濁水を捕捉箱の上部
流入口に容易に取り込むことができる。
Since this apparatus is so constructed as to be submerged in a fluid such as water, natural energy can be used as a means for causing polluted water to flow into the trap box. For example, when installing this device in an aquarium for ornamental fish, there is convection due to aeration, and when installing this device inside an elevated aquarium such as in a building or condominium, there is a vortex that occurs when water is used due to head pressure. In the case of rivers, there is a natural flow due to the head, in the case of lakes and convections that occur due to temperature differences due to the heat of wind and sunlight, and in the case of the inland sea there are tidal currents, etc. Can be easily taken into the upper inlet.

【0015】これらの捕捉除去原理を考慮すれば、本装
置を、水中に浮遊する微粒子の捕捉除去装置ばかりでな
く、空気中に浮遊する微粒子の捕捉除去装置としても適
用できることになる。すなわち、本発明に係る微粒子捕
捉除去装置は、その材質、大きさ、流出穴径等を適宜選
択することで、クリーンルームにおける空気清浄装置、
ジィーゼルエンジンの煤煙除去装置、火力発電所、工場
のボイラー煙突の煤煙除去装置、砕石プラント、セメン
トプラント等の煤煙除去装置、製材所のおがくず回収装
置等、各種装置に応用できる。
Considering these trapping and removing principles, the present apparatus can be applied not only as a trapping and removing apparatus for fine particles floating in water but also as a trapping and removing apparatus for fine particles floating in air. That is, the fine particle capture and removal apparatus according to the present invention is an air cleaning apparatus in a clean room, by appropriately selecting the material, size, outflow hole diameter, and the like.
It can be applied to various devices such as soot removing device of diesel engine, thermal power plant, soot removing device of boiler chimney of factory, soot removing device of crushed stone plant, cement plant, etc., sawdust recovery device of sawmill.

【0016】なお、捕捉箱に流入する水流は、外乱エネ
ルギーの大小により異なることから、流入口部で渦流等
が発生し、平行板間に流入した際にその外乱エネルギー
により、平行板上に集積した微粒子が舞い上がる可能性
もある。そこで、捕捉箱内には、斜め方向の渦を伴うよ
うな強い流れを緩衝して滑らかに傾斜板群に導くため
に、上側の流体流入口と傾斜板群との間に整流板を設け
る構成を採用することが望ましい。
Since the water flow flowing into the trap box differs depending on the magnitude of the disturbance energy, a vortex flow etc. is generated at the inlet, and when the water flows between the parallel plates, the disturbance energy accumulates on the parallel plates. There is a possibility that the fine particles that have sprung up. Therefore, in the trapping box, a rectifying plate is provided between the fluid inlet on the upper side and the inclined plate group in order to buffer a strong flow accompanied by an oblique vortex and guide it smoothly to the inclined plate group. It is desirable to adopt.

【0017】また、傾斜板群の平行板間隔について言及
すると、沈降速度の大きな浮遊物、すなわち、比重の大
きなもの又は粒子径の大きなものは、多少平行板を通過
する水流が速くても捕捉されるので、このような場合、
流出穴を大きくしてより多くの水量の処理が可能とな
る。一方、粒子径の大きな粒子が間隔の密な平行板間を
通過しようとすると、平行板間につかえて流れの邪魔に
なることがあり、所期の捕捉除去機能を発揮できない場
合がある。そのため、比重あるいは粒子径の大きなもの
から小さなものまで、水中における様々な微粒子に合わ
せて捕捉し、浄化ができるように、平行板の間隔を、粗
いものから密なものまでを複合状態で積層した傾斜板群
の構成も採用可能である。
Further, referring to the parallel plate spacing of the inclined plate group, a suspended matter having a large sedimentation velocity, that is, one having a large specific gravity or one having a large particle diameter is captured even if the water flow passing through the parallel plates is somewhat fast. So in this case,
Larger outflow holes allow for treatment of larger amounts of water. On the other hand, when particles having a large particle diameter try to pass between closely-spaced parallel plates, they may be caught between the parallel plates and obstruct the flow, and the desired trapping and removing function may not be exhibited. Therefore, in order to capture and purify various fine particles in water from large to small particles with specific gravity or particle size, parallel plates are laminated in a composite state from coarse to dense ones. The configuration of the inclined plate group can also be adopted.

【0018】また、傾斜板群を通過する微粒子の内、微
粒子集積空間に捕捉されないで流出穴を通じて外部に流
れ出る微粒子の捕捉率は、上記のごとく、微粒子の沈降
速度が大きいとき、すなわち微粒子の外径が大きいと
き、平行板の長さを長くしたとき、平行板の幅を大きく
したとき、平行板の鉛直線からの傾き角度を大きくとっ
たとき、平行板の入り口付近の流速を下げたとき、捕捉
箱の側壁の流出穴径を小さくしたときに、上げることが
できる。つまり、捕捉率は、主に平行板の面積と水の通
過速度に依存する。従って、捕捉率を改善するために、
平行板の面積を変更できない場合、流出穴を小さくして
流速を小さくすることで対応できる。そのため、処理水
量に応じて流出穴の穴径を調節できる機構、すなわち、
流出穴の穴径を調節可能とするシャッターを設ける構成
を採用することで、捕捉率を適宜選定することができ
る。また、このシャッターを全閉することにより、捕捉
箱の引上げ清掃時に流出穴から微粒子がこぼれ落ちるの
を防止することができる。
Further, among the fine particles passing through the inclined plate group, the capture rate of the fine particles which are not captured in the fine particle accumulating space and flow out to the outside through the outflow hole is as described above when the sedimentation velocity of the fine particles is high, that is, outside the fine particles. When the diameter is large, when the length of the parallel plate is increased, when the width of the parallel plate is increased, when the inclination angle of the parallel plate from the vertical line is increased, and when the flow velocity near the entrance of the parallel plate is decreased. , It can be raised when the diameter of the outflow hole on the side wall of the trap box is reduced. That is, the capture rate mainly depends on the area of the parallel plates and the water passage speed. Therefore, in order to improve the capture rate,
If the area of the parallel plate cannot be changed, it can be dealt with by reducing the outflow hole to reduce the flow velocity. Therefore, a mechanism that can adjust the hole diameter of the outflow hole according to the amount of treated water, that is,
The capture rate can be appropriately selected by adopting a configuration in which a shutter that can adjust the hole diameter of the outflow hole is provided. Further, by completely closing this shutter, it is possible to prevent fine particles from spilling out from the outflow hole when pulling up and cleaning the trap box.

【0019】次に、傾斜板群の平行板の傾斜角度につい
て言及すると、これらの平行板を傾斜させるのは以下の
理由による。すなわち、平行板を水平にすると、浮遊す
る微粒子が重力により沈下堆積するが、これらを一箇所
に集積させることができない。逆に平行板を鉛直方向に
立てると、集積空間に微粒子を落下させることができる
が、微粒子を平行板に沈殿させることができない。従っ
て、平行板を傾斜させることにより、微粒子を沈殿さ
せ、かつ沈殿させた微粒子を平行板に沿って落下させ、
集積空間に集積させることができる。この傾斜角度は、
平行板の鉛直線からの角度が大きくなるほど捕捉率が向
上するが、平行板によって捕捉された微粒子が下に滑り
落ちにくくなり、平行板上に堆積するおそれがあること
から、傾斜板群の傾斜角度は鉛直線から30°〜45°
に設定されることが望ましい。
Next, referring to the inclination angle of the parallel plates of the inclined plate group, the reason why these parallel plates are inclined is as follows. That is, when the parallel plates are made horizontal, the floating fine particles sink and accumulate due to gravity, but they cannot be accumulated in one place. On the contrary, when the parallel plate is set up in the vertical direction, the fine particles can be dropped into the accumulation space, but the fine particles cannot be precipitated on the parallel plate. Therefore, by inclining the parallel plate, the fine particles are precipitated, and the precipitated fine particles are dropped along the parallel plate,
It can be accumulated in the accumulation space. This tilt angle is
The capture rate improves as the angle of the parallel plates from the vertical line increases, but the particles trapped by the parallel plates are less likely to slide down and may be deposited on the parallel plates. The angle is 30 ° to 45 ° from the vertical line
It is desirable to be set to.

【0020】なお、微粒子集積空間に堆積した微粒子は
集積するに従ってそのレベルを上げ、捕捉箱の側面の流
出穴のレベルを越えると、微粒子はこの流出穴から外部
に流出し、その機能を失うことになる。従って、集積さ
れた微粒子を清掃により除去する必要がある。金魚鉢等
のように水深の浅いものは、この内部に沈設された装置
自体を水面に引き上げ、微粒子集積空間に溜まった微粒
子を傾斜板群を外して底部の集積微粒子を水とともに廃
棄すればよい。また、手が直接届かない水深の深い場所
等に設置した装置は、紐等をゆっくり引き上げて装置を
水面から引上げ、上記と同様に集積微粒子の除去を行え
ばよい。
The fine particles accumulated in the fine particle accumulation space increase in level as they are accumulated, and if the level exceeds the level of the outflow hole on the side surface of the trap box, the fine particles flow out to the outside through this outflow hole and lose their function. become. Therefore, it is necessary to remove the accumulated fine particles by cleaning. For a shallow water such as a fishbowl, the device itself submerged in the fishbowl may be pulled up to the surface of the water, the fine particles accumulated in the fine particle accumulation space may be removed from the inclined plate group, and the fine particles at the bottom may be discarded together with water. In addition, for an apparatus installed in a place where the depth of water is out of reach of the hands, a string or the like may be slowly pulled up to pull up the apparatus from the water surface, and the accumulated fine particles may be removed in the same manner as above.

【0021】また、高架水槽内に本装置を設置した場合
には、これを取り出して微粒子を廃棄することは非常に
手間暇がかかる。集積された微粒子を高架水槽の外部か
ら簡単に取り出すことができれば、清掃に要する時間の
短縮も可能となる。本発明者は、上記の点を考慮して、
捕捉箱の底部又は下部に微粒子集積空間に集積した微粒
子を排出するための排出口を設ける構成を採用すること
により、清掃に要する時間の短縮を図った。高架水槽の
場合、排出口に連結された細管の管端は通常バルブによ
って閉塞されており、微粒子が満杯になったとき、バル
ブを開くことにより高架水槽のヘッド圧によって細管か
ら流れだし、微粒子を外に排出することができる。
Further, when this device is installed in an elevated water tank, it takes a lot of time and effort to take out this device and dispose of fine particles. If the accumulated particles can be easily taken out from the outside of the elevated water tank, the time required for cleaning can be shortened. The present inventor, in consideration of the above points,
The time required for cleaning was shortened by adopting a structure in which a discharge port for discharging fine particles accumulated in the fine particle accumulation space is provided at the bottom or lower part of the trap box. In the case of an elevated water tank, the pipe end of the thin tube connected to the discharge port is usually closed by a valve.When the particles are full, the valve is opened to flow from the thin tube by the head pressure of the elevated water tank, and the particles are discharged. Can be discharged outside.

【0022】同様に、湖沼、河川、内海等においても、
上記排出口にパイプを連結し、別置き型のポンプで微粒
子を水とともに吸引して回収する構成も採用できる。淡
水で金属腐食の問題がなければ水中ポンプを設置しても
よい。回収した微粒子は下水の汚泥と同じ成分と考えら
れるので、そのままごみ焼却炉内部に噴霧して焼却する
か、フィルターによって水分を除去して汚泥ケーキの形
で焼却することも考えられる。なお、排出口に代わり、
捕捉箱の底部に引出しを設け、この引出し内に微粒子集
積空間を設ける構成も採用できる。
Similarly, in lakes, rivers, inland seas, etc.
It is also possible to employ a configuration in which a pipe is connected to the discharge port and fine particles are sucked and collected together with water by a separately installed pump. A submersible pump may be installed if there is no problem of metal corrosion in fresh water. Since the recovered fine particles are considered to have the same components as the sewage sludge, it is possible to spray them directly into the waste incinerator and incinerate them, or to remove the water with a filter and incinerate them in the form of sludge cake. In addition, instead of the outlet,
It is also possible to adopt a configuration in which a drawer is provided at the bottom of the trap box and a fine particle accumulation space is provided in the drawer.

【0023】[0023]

【作用】上記のように、本装置を観賞魚用水槽、高架水
槽、あるいは湖沼、河川、内海等に沈設すると、観賞魚
用水槽ではエアレーションによる対流、高架水槽ではヘ
ッド圧による渦流、あるいは湖沼、河川、内海等では太
陽光等による対流等により、自然の水流が発生し、水流
入口から微粒子を含んだ水が捕捉箱内に導かれる。捕捉
箱内に導かれた水は、平行板の間を通って箱の側壁に設
けられた微細な流出穴から外部に流出する。平行板を通
過する水流の流速は、平行板の開口面積と側壁の流出穴
の面積比に従って低減される。平行板の間を通過する水
流は層流を形成し、平行板に近い部分は流速が遅く平行
板の中間部の流速は速い。この平行板に近い部分ではそ
の流速が遅いため、微粒子は沈降を開始し、沈降した微
粒子はさらに平行板に接近し、さらに流速の遅い部分に
入るため、ついには平行板面に沈降していく。平行板の
極近傍の流速はほとんど零に近いので、平行板上に到達
した微粒子は平行板に沿って沈降し、捕捉箱の底部に集
積される。平行板を通過する水流は、平行板の間を通過
する度に一定の割合で微粒子を失いながら循環し水中の
透明度を向上させることになる。
As described above, when the device is submerged in an ornamental fish tank, an elevated water tank, a lake, a river, an inland sea, etc., convection by aeration in the ornamental fish tank, a swirl due to head pressure in the elevated water tank, or a lake, In rivers, inland seas, etc., natural water flows are generated by convection due to sunlight, etc., and water containing fine particles is guided into the trap box from the water inlet. The water introduced into the trap box flows between the parallel plates and flows out to the outside from the fine outflow holes provided in the side wall of the box. The flow velocity of the water flow passing through the parallel plates is reduced according to the ratio of the opening area of the parallel plates and the area of the outflow holes of the side walls. The water flow passing between the parallel plates forms a laminar flow, and the flow velocity is low in the part close to the parallel plates and fast in the middle part of the parallel plates. Since the flow velocity is slow in the part close to the parallel plate, the fine particles start to settle, and the settled fine particles further approach the parallel plate and enter the part with the slower flow velocity, and finally settle on the parallel plate surface. . Since the flow velocity near the parallel plate is almost zero, the fine particles that have reached the parallel plate settle along the parallel plate and are accumulated at the bottom of the trap box. The water flow passing through the parallel plates circulates while losing fine particles at a constant rate every time the water flows between the parallel plates, thereby improving the transparency in water.

【0024】集積された微粒子は、微粒子集積空間に堆
積するので、堆積レベルが微細な流出穴のレベルに達す
るまでの間に清掃除去する必要がある。観賞魚用水槽な
どでは水深が浅いので、装置をそのまま取り出し、また
水深の深い場所に設置する場合には、装置に予め紐を連
結しておき、適宜水面まで取り出して、傾斜板群を取り
出した後に、集積微粒子を水ごと廃棄する。捕捉箱の底
面に残った微粒子は水道水などで洗い落とす。また、排
出口から細管を通して微粒子を排出することもでき、こ
の場合、わざわざ捕捉箱を水中から取り出さなくとも簡
単に廃棄することができる。
Since the accumulated fine particles are deposited in the fine particle accumulation space, it is necessary to clean and remove them until the deposition level reaches the level of the fine outflow holes. Since the water is shallow in ornamental fish tanks, etc., if you take out the device as it is, or if you want to install it in a deep water place, connect the string to the device beforehand, take it out to the water surface appropriately, and take out the inclined plate group. After that, the accumulated fine particles are discarded together with water. Fine particles remaining on the bottom of the trap box should be washed off with tap water. Further, it is also possible to discharge the fine particles from the discharge port through a thin tube, and in this case, it is possible to simply dispose of the trapping box without taking it out of the water.

【0025】[0025]

【実施例】以下、添附図面に示した実施例について説明
する。図1ないし図6はこの発明に係る微粒子捕捉除去
装置を示すものであり、図1はその斜視図、図2はその
側面断面図、図3は水流出穴部分の拡大図、図4は整流
板を付設した場合の斜視図、図5はその側面断面図であ
る。
Embodiments Embodiments shown in the accompanying drawings will be described below. 1 to 6 show a fine particle capturing / removing device according to the present invention. FIG. 1 is a perspective view thereof, FIG. 2 is a side sectional view thereof, FIG. 3 is an enlarged view of a water outlet hole portion, and FIG. FIG. 5 is a side cross-sectional view of a case where a plate is attached, and FIG.

【0026】この微粒子捕捉除去装置1は、上方が開放
した直方体状の捕捉箱2と、この捕捉箱2の内部に収容
される傾斜板群3とを備えている。捕捉箱2は、上面に
流体流入口4を有し、水底等に設置可能なように平面状
の底面部5を有している。流体流入口4は、捕捉箱2の
上面を閉塞して、その一部から水を流入するために、パ
イプを接続した構造のものであってもよいが、汚濁水を
迅速に処理する上からは図1のごとく、傾斜板群3の上
面の開口面積に合わせて、捕捉箱2の上面のほとんどを
開放した矩形状であることが望ましい。捕捉箱2の上面
には、傾斜板群3の上面開口部に対応する部分を除いて
蓋6が施され、水流の影響を極力抑える構成としてい
る。
The particulate trapping / removing apparatus 1 is provided with a rectangular parallelepiped trapping box 2 having an open top, and an inclined plate group 3 housed inside the trapping box 2. The trap box 2 has a fluid inlet 4 on its upper surface, and has a flat bottom portion 5 so that it can be installed on a water bottom or the like. The fluid inlet 4 may have a structure in which a pipe is connected in order to close the upper surface of the trap box 2 and allow water to flow in from a part thereof, but in order to quickly treat polluted water. As shown in FIG. 1, it is preferable that most of the upper surface of the trapping box 2 is a rectangular shape in accordance with the opening area of the upper surface of the inclined plate group 3. A lid 6 is provided on the upper surface of the trap box 2 except for the portion corresponding to the upper opening of the inclined plate group 3 so that the influence of water flow is suppressed as much as possible.

【0027】傾斜板群3は、多数の平行板7を平行に傾
斜させて連結片(図示せず)等により一体化させたもの
で、捕捉箱2の側壁2aに形成された載置片8により、
捕捉箱2の底部に微粒子集積空間9を残した状態で載置
される。この傾斜板群3は、微粒子集積空間9に集積し
た微粒子を取り除く時に取り外し可能とするために、ビ
ス等により捕捉箱2に着脱自在に固定されている。
The inclined plate group 3 is formed by inclining a large number of parallel plates 7 in parallel and integrating them by a connecting piece (not shown) or the like, and a placing piece 8 formed on the side wall 2a of the trap box 2. Due to
The trapping box 2 is placed with the particulate accumulation space 9 left on the bottom. The inclined plate group 3 is detachably fixed to the trapping box 2 with screws or the like so as to be removable when removing the particles accumulated in the particle accumulation space 9.

【0028】この傾斜板群3は、長さ200mm、幅15
0mm、高さ100mmの捕捉箱2に、長さ約113mm、幅
150mmよりもやや短く、45°に傾斜した各平行板7
を間隔4〜5mmピッチで多数配列してなるものであり、
傾斜板群3の上面を捕捉箱2の上面に位置させると、そ
の下側の微粒子集積空間9の高さが約20mmとなる。こ
の平行板7の配列ピッチは上記の4〜5mmに限らず、水
流速度あるいは汚濁度に応じて種々選択でき、おおよそ
3〜10mmの範囲で選択することができる。この範囲に
限ったのは、3mmよりも小さいと目詰まりを起こし易
く、10mmよりも大きいと捕捉率が低下するからであ
る。また、当然のことながら、傾斜板群の大きさは、捕
捉箱の大きさに合わせて自由に設定できる。
This inclined plate group 3 has a length of 200 mm and a width of 15
Each parallel plate 7 which is slightly shorter than about 113 mm in length and 150 mm in width and is tilted at 45 ° is attached to the trap box 2 of 0 mm and height 100 mm.
Are arranged at intervals of 4 to 5 mm,
When the upper surface of the inclined plate group 3 is positioned on the upper surface of the trapping box 2, the height of the fine particle accumulation space 9 therebelow is about 20 mm. The arrangement pitch of the parallel plates 7 is not limited to the above 4 to 5 mm, but can be variously selected according to the water flow velocity or the degree of pollution, and can be selected within the range of about 3 to 10 mm. The reason for limiting this range is that if it is smaller than 3 mm, clogging is likely to occur, and if it is larger than 10 mm, the capture rate is lowered. Further, as a matter of course, the size of the inclined plate group can be freely set according to the size of the trap box.

【0029】なお、傾斜板群3の別の実施例として、水
流速度あるいは汚濁度のいずれにも対応できるように、
平行板間隔を粗いものから密なものにまで複合した複合
平行板からなる傾斜板群3としてもよい。この場合の平
行板7の配列ピッチは、粗いもので10mm程度、中程度
のもので6mm程度、密なもので3mm程度のものをランダ
ム状あるいは順次組み合わせて構成するようにすればよ
い。
As another embodiment of the inclined plate group 3, in order to be able to cope with either the water flow velocity or the degree of pollution,
The inclined plate group 3 may be composed of a composite parallel plate in which the parallel plate intervals are compounded from coarse to dense. In this case, the arrangement pitch of the parallel plates 7 may be about 10 mm for a coarse plate, about 6 mm for a medium plate, and about 3 mm for a dense plate in a random or sequential combination.

【0030】また、捕捉率を上げるために、図4及び図
5のごとく、上側の流体流入口4と傾斜板群3との間に
升目状の整流板11を設け、平行板7に沿った斜め方向
からの強い流れが発生したとしても、これを緩衝して滑
らかに傾斜板群3に導くように構成してもよい。
Further, in order to increase the capture rate, as shown in FIGS. 4 and 5, a grid-shaped straightening plate 11 is provided between the upper fluid inflow port 4 and the inclined plate group 3 and is arranged along the parallel plate 7. Even if a strong flow from an oblique direction occurs, it may be configured so as to buffer this and smoothly guide it to the inclined plate group 3.

【0031】捕捉箱2の微粒子集積空間9の最上側面部
には、約2mmである微細な流体流出穴12が、平行板7
の下端部において各平行板間に形成されている。この流
体流出穴12の穴径は捕捉率と関係するため、その流出
量を調節可能とするのが望ましい。
A fine fluid outflow hole 12 of about 2 mm is formed in the parallel plate 7 on the uppermost side surface of the fine particle accumulation space 9 of the trap box 2.
Is formed between the parallel plates at the lower end of the. Since the hole diameter of the fluid outflow hole 12 is related to the capture rate, it is desirable that the outflow amount can be adjusted.

【0032】図6は流体の流出穴部の流量調節機構を示
す図で、(a)は捕捉箱2の側壁に形成された横一列に
形成された三角形の穴13に対応して、三角形の穴14
が横一列に形成されたシャッター板15を上下の案内レ
ール16に沿ってスライド可能に係合した状態を示して
いる。同図(b)は両者の穴13、14が組み合わされ
た状態を示し、図中の斜線部が流出穴径である。両者の
重合度合いにより捕捉箱2からの水の流出量が決定さ
れ、捕捉率が決定されることになる。
FIG. 6 is a view showing a flow rate adjusting mechanism of a fluid outflow hole portion. FIG. 6A shows a triangular hole 13 formed in a lateral row formed on a side wall of the trap box 2 in a triangular shape. Hole 14
Shows a state in which the shutter plates 15 formed in a horizontal row are slidably engaged along the upper and lower guide rails 16. The same figure (b) shows the state where both holes 13 and 14 were combined, and the shaded part in the figure is the outflow hole diameter. The outflow amount of water from the trapping box 2 is determined by the degree of polymerization of the both, and the trapping rate is determined.

【0033】また、図2において、捕捉箱2の側面下部
には、微粒子集積空間9に集積した微粒子を排出させる
ための排出口18が形成されており、この排出口18
は、通常閉塞されており、必要に応じて細管19(図1
0、図12参照)を連結可能な構造とされている。
Further, in FIG. 2, a discharge port 18 for discharging the particles accumulated in the particle accumulation space 9 is formed in the lower portion of the side surface of the trap box 2. This discharge port 18
Are normally occluded and, if necessary, the tubule 19 (Fig. 1).
0, see FIG. 12).

【0034】次に、上記構成の微粒子捕捉除去装置1の
使用方法を説明する。図7は観賞魚用水槽20の水の浄
化目的で微粒子捕捉除去装置1を使用した状態を示すも
のである。この場合、エアレーションによって水槽20
内に水の対流が起こっており、この対流を利用して捕捉
箱2の開口4から水槽内の水を流入する。流入した水
は、傾斜板群3の平行板7間を通過する間に水よりも比
重の大きい微粒子は重力により沈降し、平行板7に沈殿
捕捉されることになる。平行板7に捕捉された微粒子
は、平行板7の傾斜に沿って落下し、傾斜板群3の下側
に確保された微粒子集積空間9に落下堆積する。
Next, a method of using the particulate trapping / removing apparatus 1 having the above-mentioned configuration will be described. FIG. 7 shows a state in which the fine particle capturing / removing device 1 is used for the purpose of purifying the water in the ornamental fish tank 20. In this case, the aquarium 20 is aerated.
Convection of water occurs inside, and the water in the water tank flows in through the opening 4 of the trap box 2 by utilizing this convection. While the inflowing water passes between the parallel plates 7 of the inclined plate group 3, the fine particles having a larger specific gravity than the water settle due to gravity, and are trapped by the parallel plates 7. The fine particles captured by the parallel plate 7 fall along the inclination of the parallel plate 7 and fall and accumulate in the fine particle accumulation space 9 secured below the inclined plate group 3.

【0035】捕捉されなかった微粒子を含む水は、平行
板7の下端部位置に形成された流出穴12から外部へ流
出するが、これらの作用が連続的に繰り返され、水が循
環することにより、水槽20内の水はその透明度を増す
ことになる。透明度の最終到達点は水槽20の中で新た
に発生する微粒子の生成速度と捕捉速度の比によって決
められる。
The water containing the untrapped fine particles flows out through the outflow hole 12 formed at the lower end portion of the parallel plate 7, and these actions are continuously repeated to circulate the water. The water in the water tank 20 will increase its transparency. The final reaching point of the transparency is determined by the ratio of the generation rate and the trapping rate of fine particles newly generated in the water tank 20.

【0036】一般に水質が悪化するのは、浮遊する微粒
子が腐敗し、硫化水素やメタンガス等のガスを発生させ
るからであり、本装置1を使用した場合、微粒子が生成
されてからあまり時間を経過しない内に捕捉除去される
ので、本装置1の微粒子集積空間9に堆積した微粒子を
定期的に除去すれば腐敗も起こらない。
Generally, the water quality is deteriorated because the suspended fine particles are decomposed to generate a gas such as hydrogen sulfide or methane gas. When the present apparatus 1 is used, it takes a long time after the fine particles are generated. Since the particles are captured and removed before they are removed, if the particles accumulated in the particle accumulation space 9 of the present apparatus 1 are removed regularly, spoilage does not occur.

【0037】集積された微粒子の除去は、流出穴12の
レベルに達するまでの間に行う。観賞魚用水槽などでは
水深が浅いので、そのまま捕捉箱2を取り出し、捕捉箱
2から傾斜板群3を取出した後に、集積微粒子を水ごと
廃棄する。捕捉箱2の底面に残った微粒子は水道水等で
洗い落とす。実験では冬季の低温期で4週間、夏場の高
温期で2週間程度で清掃し好成績を保っている。
The removal of the accumulated fine particles is performed until the level of the outflow hole 12 is reached. Since the water is shallow in an aquarium for aquarium fish, the trapping box 2 is taken out as it is, and the inclined plate group 3 is taken out from the trapping box 2, and then the accumulated fine particles are discarded together with the water. Fine particles remaining on the bottom surface of the trap box 2 are washed off with tap water or the like. In the experiment, cleaning was carried out in low temperature in winter for 4 weeks and in high temperature in summer in about 2 weeks, and good results are maintained.

【0038】また、水槽20内でエアレーションを行っ
ている場合には、傾斜板群3の平行板7には、常に酸素
を含んだ水が流れることになる。そのため、平行板7上
に沈降する微粒子は集積空間9に沈降するまでの間に好
気性のバクテリアの分解作用を受けることになる。実験
結果によると、幅350mm、奥行180mm、深さ200
mm程度の水槽20に大型の金魚3びきを飼育し、10か
月間水換えなしで、pH7.5という値を得ている。
When aeration is performed in the water tank 20, water containing oxygen always flows through the parallel plates 7 of the inclined plate group 3. Therefore, the fine particles settled on the parallel plate 7 are subjected to the decomposition action of aerobic bacteria before settling in the accumulation space 9. According to the experimental results, width 350mm, depth 180mm, depth 200
A large goldfish 3 is bred in a water tank 20 of about mm, and a value of 7.5 is obtained without changing water for 10 months.

【0039】図8は湖沼、河川、内海等の水底に設置し
た載置台22上に本装置1を2台載置した例を示してい
る。この湖沼等の場合は、太陽光による水面と水底との
間の温度差により対流が起こり、河川の場合は傾斜面に
よる落差により流れが起こり、さらに、内海の場合には
潮流等により夫々水流が発生し、これら自然の流れによ
り捕捉箱2の内部に水が流入し、浄化作用が行われる。
特に、大量に微粒子が浮遊し、腐敗しているような河川
等の場合、腐敗した微粒子はさらに粒子径が小さくなる
ため浮遊し続けるが、本装置1に流入すると、腐敗微粒
子の比重が水よりも重いため、上記観賞魚用と同様な浄
化作用が行われ、その効果も大きい。
FIG. 8 shows an example in which two apparatus 1 are mounted on a mounting table 22 installed on the bottom of a water such as a lake, a river or an inland sea. In the case of lakes and marshes, convection occurs due to the temperature difference between the water surface and the bottom of the water due to sunlight, and in the case of rivers the flow occurs due to the head difference due to the inclined surface. Water is generated, and water flows into the trap box 2 due to these natural flows, and the purifying action is performed.
In particular, in the case of a river or the like in which a large amount of fine particles are suspended and is spoiled, the spoiled fine particles continue to float because the particle diameter becomes smaller, but when they flow into the device 1, the specific gravity of the spoiled fine particles is larger than that of water. Since it is also heavy, the same purifying action as that for the above ornamental fish is performed and its effect is great.

【0040】河川等に設置された捕捉除去装置1に集積
した微粒子の排出清掃作業は、図9のごとく、予め本装
置1に紐23を付け、水上の構造物又は浮き24に固定
しておく。本装置1を清掃する場合は紐23をゆっくり
と引き上げることによって観賞魚用水槽の場合と同じよ
うに清掃する。
As shown in FIG. 9, a string 23 is attached to the present device 1 in advance and fixed to a floating structure or float 24 in the discharge cleaning work of the fine particles accumulated in the trapping and removing device 1 installed in a river or the like. . When cleaning the present device 1, the string 23 is slowly pulled up to perform cleaning in the same manner as in the aquarium for fish tank.

【0041】なお、海、河川、湖沼が大型で大量の微粒
子を排出する必要がある場合には、図10のごとく、微
粒子集積空間の低部の排出口18(図2参照)に細管1
9を連結し、この細管19を通して岸辺等に別置したポ
ンプ25で微粒子を水とともに吸引して回収する。湖沼
や河川のように淡水で金属腐食の問題がなければ、水中
ポンプを設置してもよい。回収した微粒子は下水の汚泥
と同じ成分と考えられるので、そのままごみ焼却炉内部
に噴霧して焼却するか、フィルターによって水分を除去
して汚泥ケーキの形で焼却することも考えられる。
When the sea, rivers and lakes are large and need to discharge a large amount of fine particles, as shown in FIG. 10, the thin tube 1 is attached to the discharge port 18 (see FIG. 2) at the lower part of the fine particle accumulation space.
9 are connected, and the fine particles are sucked and collected together with water by the pump 25 separately placed on the shore or the like through the thin tube 19. Submersible pumps may be installed if there is no problem of metal corrosion in fresh water such as lakes and rivers. Since the collected fine particles are considered to have the same components as the sludge of the sewage, it is possible to spray them as they are inside the refuse incinerator and incinerate them, or to remove them with a filter to incinerate them in the form of sludge cake.

【0042】図11は高架水槽26内に本装置11を設
置した図、図12はこの高架水槽26の内部に設置され
た本装置1に細管19を連結した状態を示す断面図であ
る。高架水槽26内に本装置1を設置した場合、水槽内
のヘッド圧により渦流などが発生し、これにより水流に
より捕捉箱2内部に水を取り入れ、鉄錆等の微粒子等を
沈殿捕捉する。また、微粒子集積空間9に集積した微粒
子は細管19の先端のバルブ27を開くことにより外部
に排出することができる。
FIG. 11 is a view showing the apparatus 11 installed in the elevated water tank 26, and FIG. 12 is a sectional view showing a state in which a thin tube 19 is connected to the apparatus 1 installed in the elevated water tank 26. When the apparatus 1 is installed in the elevated water tank 26, a head pressure in the water tank causes a swirl or the like, which causes water to be taken into the trap box 2 and the fine particles such as iron rust are trapped and trapped. Further, the fine particles accumulated in the fine particle accumulation space 9 can be discharged to the outside by opening the valve 27 at the tip of the thin tube 19.

【0043】[0043]

【発明の効果】以上詳述したところから明らかな通り、
本発明に係る微粒子捕捉除去装置によると、流体中に沈
設可能な捕捉箱の多数の傾斜した平行板によって微粒子
を捕捉除去できるので、捕捉箱に水を流入循環させる動
力が不要で低コスト化が図れ、また、捕捉箱により外部
水流の影響を抑えることができるので、効率よく微粒子
を捕捉除去できる。
As is clear from the above description,
According to the particulate trapping / removing device of the present invention, particulates can be trapped and removed by the large number of inclined parallel plates of the trapping box that can be submerged in the fluid, so that the power for circulating the water in the trapping box is unnecessary and the cost can be reduced. Moreover, since the influence of the external water flow can be suppressed by the trap box, the fine particles can be trapped and removed efficiently.

【0044】また、捕捉箱の流体流入口と傾斜板群との
間に整流板を設けると、外部水流の影響を極力抑えて効
率のよい浄化が可能となる。さらに、捕捉箱の側壁に形
成された流体流出穴の穴径を調節可能とするシャッター
を設けたから流出穴径の調節により適宜の捕捉率に設定
できる。
Further, if a flow straightening plate is provided between the fluid inlet of the trap box and the inclined plate group, the effect of the external water flow can be suppressed as much as possible, and efficient purification can be performed. Further, since the shutter for adjusting the hole diameter of the fluid outflow hole formed on the side wall of the trap box is provided, it is possible to set an appropriate trapping rate by adjusting the outflow hole diameter.

【0045】また、傾斜板群の平行板の傾斜角度を鉛直
線に対して30°〜45°に設定すれば、微粒子の沈降
捕捉及び集積が極めて良好に行い得る。さらに、捕捉箱
の底部又は下部に微粒子集積空間に集積した微粒子を排
出するための排出口を設ければ、集積微粒子を簡単に外
部に排出することができる。
If the inclination angle of the parallel plates of the inclined plate group is set to 30 ° to 45 ° with respect to the vertical line, the fine particles can be trapped and collected very well. Further, if a discharge port for discharging fine particles accumulated in the fine particle accumulation space is provided at the bottom or lower part of the trap box, the accumulated fine particles can be easily discharged to the outside.

【0046】なお、平行板の間隔を粗いものから密なも
のまでを複合状態で積層した傾斜板群を使用すれば、比
重あるいは粒子径の大きなものから小さなものまで、水
中における様々な微粒子に応じて捕捉し浄化することが
できるといった利点も有している。
By using a group of inclined plates in which parallel plates are arranged in a composite state from coarse to dense ones, it is possible to respond to various fine particles in water from large to small specific gravity or particle diameter. It also has the advantage that it can be captured and purified.

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

【図1】この発明に係る微粒子捕捉除去装置の一実施例
を示す斜視図
FIG. 1 is a perspective view showing an embodiment of a particulate trapping / removing device according to the present invention.

【図2】同じくその断面図、FIG. 2 is a sectional view of the same,

【図3】同じく流出穴部の拡大図[FIG. 3] Similarly, an enlarged view of the outflow hole portion.

【図4】傾斜板群の上側に整流板を設けた例を示す斜視
FIG. 4 is a perspective view showing an example in which a current plate is provided on the upper side of a group of inclined plates.

【図5】同じく整流板を設けた場合の捕捉箱の断面図FIG. 5 is a cross-sectional view of the trapping box when a straightening vane is also provided.

【図6】流体流出穴の流量調節機構を示す図であり、
(a)はシャッター板を開放した状態の図、(b)はシ
ャッター板の穴と捕捉箱の側壁の穴との組合わせ状態を
示す図
FIG. 6 is a view showing a flow rate adjusting mechanism of a fluid outflow hole,
(A) is a diagram showing a state where the shutter plate is opened, and (b) is a diagram showing a combination state of the hole of the shutter plate and the hole of the side wall of the capturing box.

【図7】本装置を観賞魚用水槽の浄化用に使用した例を
示す斜視図
FIG. 7 is a perspective view showing an example in which the device is used for cleaning an aquarium for ornamental fish.

【図8】本装置を河川、湖沼等の浄化用として使用した
例を示す斜視図
FIG. 8 is a perspective view showing an example in which this device is used for purification of rivers, lakes and marshes.

【図9】本装置の清掃を考慮して本装置を浮きなどに紐
で連結した状態を示す図
FIG. 9 is a diagram showing a state in which the device is connected to a float or the like with a string in consideration of cleaning of the device.

【図10】大量の集積微粒子を排出する場合の概略構成
FIG. 10 is a schematic configuration diagram in the case of discharging a large amount of accumulated fine particles.

【図11】高架水槽の内部に本装置を設置した場合の概
略図
FIG. 11 is a schematic diagram when this device is installed inside an elevated water tank.

【図12】同じく高架水槽から集積微粒子を排出する場
合の概略図
FIG. 12 is a schematic view of the case of discharging accumulated fine particles from the elevated water tank.

【符号の説明】[Explanation of symbols]

1 微粒子捕捉除去装置 2 捕捉箱 3 傾斜板群 4 流入口 5 底面 7 平行板 9 微粒子集積空間 11 整流板 12 流出穴 15 シャッター板 18 排出口 20 観賞魚用水槽 24 浮き 25 ポンプ 1 Particle capture and removal device 2 Capture box 3 Slanted plate group 4 Inlet 5 Bottom surface 7 Parallel plate 9 Fine particle accumulation space 11 Rectification plate 12 Outflow hole 15 Shutter plate 18 Discharge port 20 Ornamental fish tank 24 Float 25 Pump

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 上部に流体流入口を有し流体中に設置可
能な捕捉箱と、この捕捉箱の内部上側に平行板を多数並
べて斜めに固定してなる傾斜板群と、捕捉箱の底部と傾
斜板群の下端との間に形成された微粒子集積空間と、捕
捉箱の側壁において、傾斜板群の平行板の間隔に合わせ
て微粒子集積空間の最上位置に形成された微細な流体流
出穴とを備えた浮遊微粒子の捕捉除去装置。
1. A trapping box having a fluid inlet in the upper part, which can be installed in a fluid, a group of inclined plates in which a plurality of parallel plates are arranged diagonally and fixed obliquely inside the trapping box, and a bottom part of the trapping box. And a lower end of the slant plate group, and a fine fluid outflow hole formed at the uppermost position of the fine particle stack space on the side wall of the trapping box in accordance with the distance between the parallel plates of the slant plate group. And a device for trapping and removing suspended particles.
【請求項2】 前記捕捉箱の流体流入口と傾斜板群との
間に整流板を設けた請求項1記載の浮遊微粒子捕捉除去
装置。
2. The suspended particulate trapping / removing device according to claim 1, further comprising a current plate provided between the fluid inlet of the trap box and the inclined plate group.
【請求項3】 前記流体流出穴にその穴径を調節可能と
するシャッターを設けた請求項1又は2記載の浮遊微粒
子捕捉除去装置。
3. The suspended particulate capture / removal device according to claim 1, wherein the fluid outflow hole is provided with a shutter capable of adjusting the hole diameter.
【請求項4】 前記傾斜板群の平行板の傾斜角度を鉛直
線に対して30°〜45°に設定した請求項1、2又は
3記載の浮遊微粒子捕捉除去装置。
4. The suspended particulate capture / removal device according to claim 1, 2 or 3, wherein the inclination angle of the parallel plates of the inclined plate group is set to 30 ° to 45 ° with respect to the vertical line.
【請求項5】 前記捕捉箱の底部又は下部に微粒子集積
空間に集積した微粒子を排出するための排出口を設けた
請求項1、2、3又は4記載の浮遊微粒子捕捉除去装
置。
5. The suspended particulate trapping / removing apparatus according to claim 1, wherein a discharge port for discharging the particulates accumulated in the particulate accumulation space is provided at the bottom or lower part of the trap box.
【請求項6】 前記平行板の間隔を、粗いものから密な
ものまでを複合状態で積層した請求項1、2、3、4又
は5記載の浮遊微粒子捕捉除去装置。
6. The suspended particulate trapping / removing device according to claim 1, wherein the parallel plates are stacked in a composite state from a coarse one to a dense one.
JP29653194A 1994-11-30 1994-11-30 Device for trapping and removing suspended particulates Expired - Lifetime JP2908257B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP29653194A JP2908257B2 (en) 1994-11-30 1994-11-30 Device for trapping and removing suspended particulates

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29653194A JP2908257B2 (en) 1994-11-30 1994-11-30 Device for trapping and removing suspended particulates

Publications (2)

Publication Number Publication Date
JPH08150304A true JPH08150304A (en) 1996-06-11
JP2908257B2 JP2908257B2 (en) 1999-06-21

Family

ID=17834741

Family Applications (1)

Application Number Title Priority Date Filing Date
JP29653194A Expired - Lifetime JP2908257B2 (en) 1994-11-30 1994-11-30 Device for trapping and removing suspended particulates

Country Status (1)

Country Link
JP (1) JP2908257B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106215469A (en) * 2016-09-21 2016-12-14 武汉兴天宇环境股份有限公司 A kind of immersion settler and settling system

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106215469A (en) * 2016-09-21 2016-12-14 武汉兴天宇环境股份有限公司 A kind of immersion settler and settling system
CN106215469B (en) * 2016-09-21 2019-08-02 武汉兴天宇环境股份有限公司 A kind of immersion settler and settling system

Also Published As

Publication number Publication date
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