JPH04166293A - Filtering device - Google Patents

Filtering device

Info

Publication number
JPH04166293A
JPH04166293A JP2291023A JP29102390A JPH04166293A JP H04166293 A JPH04166293 A JP H04166293A JP 2291023 A JP2291023 A JP 2291023A JP 29102390 A JP29102390 A JP 29102390A JP H04166293 A JPH04166293 A JP H04166293A
Authority
JP
Japan
Prior art keywords
layer
space
filter
stream
flow
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.)
Pending
Application number
JP2291023A
Other languages
Japanese (ja)
Inventor
Yukio Kato
幸男 加藤
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP2291023A priority Critical patent/JPH04166293A/en
Publication of JPH04166293A publication Critical patent/JPH04166293A/en
Pending legal-status Critical Current

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Classifications

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

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  • Biological Treatment Of Waste Water (AREA)

Abstract

PURPOSE:To remarkably reduce the generation of sludge by providing passage space between a bottom plate and the lower part of the filter medium layer and interrupting relevant passage with partitioning plate to the lower part of at least one or more the filter medium layers, thereby prohibiting proliferating configuration of bacteria to be as a filter film type. CONSTITUTION:Flowing-in water(x) from flowing-in pipe 4 is abutted on a bottom plate 9 to be made in stirring condition and direction of stream is chaged and the stream (y) is formed along the bottom plate 9 in lower passage 10. On the other hands, the stream (z) is formed along the filter member layer 7 and the stream (y) goes to the rising flow (z) in space layer 6-6'' and it is in a push-backed condition by the interrupting plate 14 and the rising stream (z) is assisted to a space layer. Since stream is stirred and buffered in the lower passage space 10 to be no up-and-down flow on the filter member surface of space layer, proliferating configuration of bacteria is concentrated to the internal part of the filter member and not form filter film shaped on the surface of the filter member. Based on these phenomenons, increase and accumulation of sludge are very small compared with proliferation in the film shape member after the lapse of time and especially in the bottom passage space the accumulation of sludge hardly occurrs by buffered stream and buffering action is not interrupted by the increase of bacteria.

Description

【発明の詳細な説明】 僧内金流れ方向に窒間層?介して炉適材層金立役して仕
切り、横方向に通水させ、接触酸化を計る濾過装置でに
空間層の上下緩衝作用により浄化機能が得られる。とこ
ろが空間層の上下流は菌の繁殖の形態がP膜状になる重
大な欠点がある。又流入する原水による流れは戸適材表
面或いは壁面に沿って流下し、底板に沿って流れが出来
る。この強い流れは上記緩衝作用を阻害するばかりでな
く、濾過材層を次々通水する構成の為、その勤王によっ
て底面に接する濾過社内の菌が流される為の弊害を生じ
、更に之が波及し、菌体が外部に大量に流出する直接の
弊害と菌を向復の困難性など間接的な弊害?さけられな
い。加えて濾過材層の菌相差により初めに通水する濾過
材層及び空間層に易分解成分の処理が集中し、大量の汚
泥が蓄積する上、上述の底面で生ずる菌体の剥離或いは
枯死も次々と下流のろ過材層に波及し大量枯死に発展し
やすい不都合がある。Fill状になる菌の繁殖増加の
形態は、空間層の上下流による接触と走化性によって栄
養源と#l素の最も豊な濾過材表面に上に上にと厚みを
増し続け、下になる層は環境条件の変化によって絶えず
死滅と発生金繰シ返す事になり、その中心部程酸素が少
なく活性が低くなる。従って浄化に有効な部分は塊の表
面に限られる事になシ、その大部分は効率の悪い余剰汚
泥となシ、さらにP膜に囲1れる濾過材内部は酸欠状態
になり浄化機能について全く無意味な空間となる。以上
は空間層の上下緩衝作用が原因であるので、たとえ通水
空間の大きい濾過材を便用しても、通水とは別にP嗅状
になる菌が増加蓄積する不都合をさけられなり0 本発明は上記に鑑みなされたもので槽内を長手方向に空
間層全おいてF適材層金立設して仕切り一痛の空間層に
流入口、他gs空間層に流出口を設け、貯水式にして便
用するf′pf過按貧に於いて底面に沿って本体底板と
ろ過材層底部との間に流路空間を設は少なくとも一ケ所
以上ろ過材層の下で仕切板により該流l!!I空関會遁
断する構成により従来の不都合全除去する様にしたろ過
製電に関するものである。
[Detailed Description of the Invention] Nitrogen layer in the flow direction of gold inside the monastery? Through the filtration device, which uses a layer of metal suitable for the furnace as a partition and allows water to flow in the lateral direction, a purifying function is obtained by the vertical buffering effect of the space layer. However, there is a serious drawback that bacteria propagate in the form of a P film upstream and downstream of the spatial layer. In addition, the flow of incoming raw water flows down along the door fitting surface or wall surface, and a flow is created along the bottom plate. This strong current not only obstructs the above-mentioned buffering effect, but also causes harmful effects as bacteria in the filtration chamber that is in contact with the bottom surface is washed away due to the structure in which water is passed through the filtration material layer one after another. Are there direct harms such as a large amount of bacterial cells leaking out to the outside, and indirect harms such as difficulty in recovering the bacteria? I can't avoid it. In addition, due to the bacterial phase difference in the filter media layer, the treatment of easily decomposed components is concentrated in the filter media layer and the space layer through which water first passes, resulting in the accumulation of a large amount of sludge, and the above-mentioned detachment or death of bacterial cells that occur on the bottom surface. This has the disadvantage that it spreads to the downstream filter media layer one after another and tends to lead to mass dieback. The form of increased bacterial growth, which forms a fill, is due to contact and chemotaxis between the upstream and downstream of the spatial layer, which continues to increase in thickness on the surface of the filter medium, which is richest in nutrients and #1 elements, and then downwards. This layer is constantly dying and growing due to changes in environmental conditions, and the center of the layer has less oxygen and is less active. Therefore, the effective part for purification is limited to the surface of the lump, and most of it becomes inefficient surplus sludge, and furthermore, the inside of the filter material surrounded by the P membrane becomes oxygen-deficient, and the purification function is impaired. It becomes a completely meaningless space. The above is caused by the vertical buffering effect of the spatial layer, so even if you use a filter material with a large water passage space, you can avoid the inconvenience of increasing and accumulating bacteria that cause P-smelt, apart from water passage. The present invention has been made in view of the above, and is a water storage type in which all the space layers in the longitudinal direction are installed in the tank with F appropriate layer metal upright, an inlet is provided in one space layer of the partition, and an outlet is provided in the other gs space layer. When adjusting f'pf for convenience, a flow path space is provided between the bottom plate of the main body and the bottom of the filter layer along the bottom surface, and a partition plate is used at least one place under the filter layer to prevent the flow. l! ! This invention relates to a filtration power production system that eliminates all of the disadvantages of the conventional technology through a configuration in which the air barrier is disconnected.

以上実施例に石って説明する。第一図は旭川のν過装置
であり本体1の内部金部れ方向に仕切板2.2金立設し
、流入室Aと吐出室Ci区分しその間を濾過材層Bとし
、PA材室Bとは仕切板下部3.3でそれぞれ連通し、
濾過材層Bに空間層6〜6′t−介して濾過材層7〜?
’t−立設して仕切り濾過材層下部8〜8と底板9との
間に流路空間10を設は濾過材層7の下を遮断板14で
連断しである。11.11fl汚泥排出口でキャップ1
2.12をかぶせである。流入バイブ4より原水が流入
すると吐出口5の高さテで水面りが上昇し流入室A1濾
過材室B1吐出室CとIliに流れ吐出口5より外部に
吐出循環する。濾過材層はTに示す様に多孔板13の間
にF適材11″fc収納して濾過材層を形成し炉材支持
多孔板13の下に遮断板14を設けている。
The above will be explained based on the embodiments. Figure 1 shows Asahikawa's ν filtration device, in which a partition plate 2.2 is installed vertically in the direction of the internal metal part of the main body 1, dividing the inlet chamber A and the discharge chamber Ci, with a filter material layer B between them, and a PA material chamber B. They communicate with each other at the bottom of the partition plate 3.3,
Filtering material layer B is provided with filtering material layer 7 through space layer 6-6't-?
A channel space 10 is provided between the lower parts 8 to 8 of the partition filtration material layers and the bottom plate 9, and the bottom of the filtration material layer 7 is continuous with a blocking plate 14. 11. Cap 1 at the 11fl sludge discharge port
2.12 is covered. When raw water flows in from the inflow vibrator 4, the water level rises at the height of the discharge port 5, flows into the inflow chamber A1, the filter medium chamber B1, the discharge chamber C and Ili, and is discharged and circulated from the discharge port 5 to the outside. As shown in T, the filter material layer is formed by storing F suitable material 11''fc between the perforated plates 13, and a blocking plate 14 is provided below the furnace material support perforated plate 13.

作用効果について税関する。Customs regarding the effect.

流入バイブ4から流入水(イ)は底板9にぶつかって攪
拌状態になり流れ方向をかえ下部流路10を底板9に沿
って(ロ)の流れが出来る。一方濾過材層Tに沿って(
ハ)の流れ力;出来、(ロ)の流れは空間層6及び6で
は上昇流ヒ→を生じ更に遮断板14によシ押し戻される
状態になり空間層へ上昇流(ハ)が助勢される。流れ扛
下部流路空間10で攪拌緩衝され空間層のろ過材面で上
下流にならないので菌の繁殖の形態は炉適材内部に集中
し濾過材表面でFvX状にならない。
The inflow water (a) from the inflow vibrator 4 collides with the bottom plate 9, becomes agitated, changes the flow direction, and forms the flow (b) along the bottom flow path 10 along the bottom plate 9. On the other hand, along the filter material layer T (
Flow force of c): done, the flow of (b) generates an upward flow H → in the space layers 6 and 6, and is further pushed back by the blocking plate 14, and the upward flow (c) is assisted in the space layer. . Since the flow is agitated and buffered in the flow path space 10 and does not flow upstream or downstream on the surface of the filter material in the space layer, the form of bacterial propagation is concentrated inside the furnace material and does not become FvX-like on the surface of the filter material.

以上の事から使用時間がたってもF嘆状の繁殖に比して
、汚泥の増加蓄積は極く少なくなり、特に底面流路空間
は緩衝流によシ蓄積し[(いので、緩衝作用は菌の増加
によって阻害される事はない。
From the above, even after usage time has passed, the increase and accumulation of sludge is extremely small compared to the proliferation of F-shaped sludge, and especially in the bottom flow passage space, it accumulates due to the buffer flow. It is not inhibited by an increase in bacteria.

更に底面に沿う流れによる弊害がなくなり、槽内全体で
水と菌との効率のよい接触酸化が行われ、易分解成分の
処理は複数のFA材層T〜Tで発掘する事が出来る1、
又この実施例では濾過材内部に水の浸入移動しやすく園
の蓄積に有利な通水空間の大きい人工或いは天然のQi
!碓質音質全不規則1せた木毛状物17(商品名、ビニ
ロック)にしてckJ流路にかえた早によ#)空間層で
上下流が出来ないので部分通水による弊害が発生しなり
好@5@が得られる。掃除再生はその1\の状態で空間
層を利用して濾過材に水を噴射し、底面流路に落した汚
泥全汚泥排出バイブ11より容易に除去出来る。
Furthermore, the harmful effects of flow along the bottom surface are eliminated, and efficient contact oxidation between water and bacteria is performed throughout the tank, and easily decomposable components can be excavated in multiple FA material layers T to T1.
In addition, in this embodiment, artificial or natural Qi filters with large water passage spaces, which are advantageous for water accumulation, are used.
! As soon as I changed to the ckJ flow path by changing the sound quality to the ckJ flow path with completely irregular wood fibers 17 (product name, Vinylock), problems caused by partial water flow occurred because upstream and downstream flow cannot be done in the spatial layer. You can get Nariko@5@. For cleaning and regeneration, water is injected onto the filter medium using the space layer in the state 1\, and the sludge dropped into the bottom channel can be easily removed by the sludge discharge vibrator 11.

遮断板14の高さについては、低い場合には底面の流れ
の勤王によって流れが遮断板のはずれに集中し、菌が流
され剥離する墨があるので流路空間より制クシている。
Regarding the height of the blocking plate 14, if it is low, the flow will concentrate at the edge of the blocking plate due to the flow on the bottom surface, and bacteria will be washed away and there will be ink to be peeled off, so it will be more difficult to control than the flow path space.

又P2m材層の底板に多孔板又1グ平板15を設ければ
動圧防止作用と同時に骨材などの粒材の収納に利用出来
る。
Furthermore, if a perforated plate or a 1G flat plate 15 is provided on the bottom plate of the P2m material layer, it can be used to prevent dynamic pressure and at the same time to store granular materials such as aggregate.

第二図は菌の繁殖の形態が、その走化性により濾過材表
面に洲膜状になシやすい通水空間の小さい濾過材18で
濾過材層を形成し、三層目7の下に遮断板14を設ける
様にしている。作用効果については底面流路10で循環
水は充分緩衝されたのち空間層6〜6を上昇し、菌の繁
殖の形態は涙膜状にならないで濾過材内部に集中し、侵
透或いは通水によシ浄化される。尚この実施例では仕切
板2を省略している。又濾過材層7の底面流路10に段
差をつけ充分な緩衝空間と同時に空間層の上昇流(ハ)
を強化する様にしている。
Figure 2 shows that the mode of bacterial propagation is that due to their chemotaxis, they tend to form a film on the surface of the filter medium, forming a filter medium layer in the filter medium 18 with a small water passage space, and forming a layer under the third layer 7. A blocking plate 14 is provided. Regarding the action and effect, the circulating water is sufficiently buffered in the bottom flow path 10 and then rises through the space layers 6 to 6, and the form of bacterial growth does not become a tear film, but concentrates inside the filter medium, causing penetration or water passage. It is purified by the process. In this embodiment, the partition plate 2 is omitted. In addition, a step is provided in the bottom channel 10 of the filter material layer 7 to create a sufficient buffer space and at the same time create an upward flow in the space layer (c).
I am trying to strengthen it.

第三図作用効果は流入水は底面にそった流れ(ロ)にな
るが、遮断板14によシ底面流路10で攪拌緩衝され上
昇流(ハ)になる。ふき上る水は炉適材内部に分散平均
化し吐出口に向い移動すム濾過材層7を通水LA空間層
6に出た循環水は濾過材層γの通水抵抗を受け、濾過材
層Tを通水する事になるが、この際空間層6では菌の繁
殖の形態が涙膜状にならない事から底面流路10が緩衝
空間となシ、空間層を介して濾過材層を通水移動するも
のと考えられる。この実施例では各濾過材層で菌相差を
生じ難分解成分の処理に適するので、処理の目的により
有効に利用する幕が出来る。尚この実施例では仕切板2
の下部を多孔板16にし多孔板の通水孔で濾過材層Bと
連通し、吐出口5及び−過材室Bの通水抵抗となり流れ
を分散平均化し、部分通水を防止する様にしている。
The effect shown in Figure 3 is that the inflowing water flows along the bottom surface (b), but is agitated and buffered in the bottom channel 10 by the blocking plate 14 and becomes an upward flow (c). The rising water is dispersed and averaged inside the furnace suitable material and moves toward the discharge port.The circulating water that flows through the filtration material layer 7 and exits to the LA space layer 6 is subjected to the water flow resistance of the filtration material layer γ, and is transferred to the filtration material layer T. Water will be allowed to pass through the filter material layer through the space layer 6, and the bottom flow path 10 will serve as a buffer space since bacteria will not propagate in a tear film-like manner in the space layer 6. It is considered to be moving. In this embodiment, a bacterial phase difference occurs in each filter layer and is suitable for processing difficult-to-decompose components, so that a curtain can be used more effectively for the purpose of processing. In this embodiment, the partition plate 2
A perforated plate 16 is used at the bottom of the perforated plate to communicate with the filtration material layer B through the water passage holes of the perforated plate, thereby creating water flow resistance at the discharge port 5 and the filtration material chamber B, dispersing and averaging the flow, and preventing partial water flow. ing.

[遮断板14を設け、第一、第ニア、7のF通層で易分
解成分の大量処理に適する通水空間の大きい濾過材1T
にし、第三層Tは漉す作用のある目の詰んだ砕石、小砂
利、或いにプラスチックの繊維を不規則に絡1せた木毛
状物18にL2、最終層の通水抵抗で、第一。第二層の
部分通水を防止し、同時に擾拌緩衝状態全強化する様に
している。尚この実施例では吐出室Cとの仕切板2の上
部通水口3を多孔板16にしている。多孔板16による
作用効果は使用期間がたって菌の蓄積が進み、濾過材層
γが通水不能の状態になり、水面りが上昇オーバーフロ
ー刀シクノ望間I曽6でθ不り狛汁V(よるー流下作用
(ホ)を助勢し、更に空間層6の上部を素通りしないで
空間716に流下(へ)し、水交換が持続し濾過材層T
裏面の菌体が好気状態を保つことが出来る。
[Filtering material 1T equipped with a blocking plate 14 and having a large water passage space suitable for large-scale treatment of easily decomposed components with the first, near, and seventh F passage layers.
The third layer T is made of dense crushed stone, small gravel, or a wooden wool material 18 with plastic fibers irregularly intertwined with it, which has a filtering effect, L2, and the final layer has water resistance. first. Partial water passage through the second layer is prevented, and at the same time, the agitation buffer state is fully strengthened. In this embodiment, the upper water passage port 3 of the partition plate 2 with respect to the discharge chamber C is made into a perforated plate 16. The effect of the perforated plate 16 is that as the period of use progresses, bacteria accumulate, the filter layer γ becomes unable to pass water, and the water level rises. It supports the flow-down action (e), and furthermore, it flows down into the space 716 without passing through the upper part of the space layer 6, and the water exchange continues and the filter material layer T
The bacterial cells on the back side can maintain an aerobic state.

第五図は通路のろ過材の巾を大きくとり目の細い漉す作
用のある天然又は人工の繊維質?不規則に絡1せた木毛
状噂、或いは小砂利18にし吐出口5を底面近くに下げ
た実施例で、その作用効果は底面10を設けない場合は
上記飛す作用によって空間層6〜6で上下に緩衝する為
、濾過活流入面でP#が形成する!11になる。この実
施例によれば緩衝作用は底面流路10.10で行われる
為、菌の繁殖の形態はP襖状にならない。浄化は通水に
よる接触酸化になシ通水抵抗と共に水面りが上昇し、吐
出口5に向って落差による通水と充分な空気に接する等
効率のよい浄化力が得らnる。汚泥の発生はごく少なく
てすむので上記作用は極めて長期に持続する好都合が傅
られる。
In Figure 5, the width of the filter material in the passage is widened, and is it a natural or artificial fiber that has a narrow-mesh straining effect? This is an embodiment in which the discharge port 5 is lowered near the bottom surface using irregularly entwined wood fibers or small gravel 18, and its effect is that when the bottom surface 10 is not provided, the space layer 6 to 6 to buffer vertically, P# is formed on the filtration active inflow surface! Becomes 11. According to this embodiment, since the buffering effect is performed in the bottom channel 10.10, the form of bacterial growth does not become P-sliding. Purification is carried out by catalytic oxidation due to water flow, and the water level rises with water flow resistance, and efficient purification power such as water flow due to the head and contact with sufficient air toward the discharge port 5 is obtained. Since only a small amount of sludge is generated, the above effect can be advantageously maintained for an extremely long period of time.

以上の説明で明らかな様に本発明は炉適材室Bヶ流n方
向に窒闇46會介して濾過材層1全立設して仕切り、濾
過材層7’f(次々と通水或いは接触移動させ酸化を計
る濾過装置1に於いて濾過材下部8と底面9との間に底
面9に沿って流路空間1゜を設は濾過材Tの下で仕切板
14で該流路1oを遮断する事により、底面に沿って生
ずる流れによる弊害発生を除去し、菌の繁殖形態’tP
K状にしない事で汚泥の発生tを大巾に減らし、極めて
長期に菌の増加によって浄化機能を阻害しない等従来の
不都合をことごとく解決した。
As is clear from the above explanation, the present invention is constructed by partitioning the furnace suitable material chamber B by arranging the entire filtration material layer 1 upright in the direction of flow n, and by arranging the filtration material layer 1 entirely upright in the direction of flow n of the furnace suitable material chamber B, and In the filtration device 1 that measures oxidation by moving the filter material, a flow path space 1° is provided along the bottom surface 9 between the lower part 8 of the filter material T and the bottom surface 9. By blocking it, the harmful effects caused by the flow that occurs along the bottom surface are removed, and the breeding form of bacteria is prevented.
By not forming the sludge in a K-shape, the amount of sludge generated is greatly reduced, and all the disadvantages of the conventional method have been solved, such as preventing the purification function from being inhibited by the increase in bacteria over a very long period of time.

尚、遮断板の位置や、便い方、濾過材の性質、その組合
せ等によって異なる作用効果が得られるので本発明は広
範囲に旭川、生活廃水、原振処理などその目的によって
適応させる事が出来る。
In addition, different effects can be obtained depending on the position of the blocking plate, the method of use, the properties of the filter medium, the combination thereof, etc., so the present invention can be applied to a wide range of purposes, such as Asahikawa, domestic wastewater, and original vibration treatment. .

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

第一図乃至第五図は本発明の実施例と示す断面図である
。 囚に於いて、1は本体、2は仕切板、3は仕切板通水口
、4は流入口、5は吐出口、6は空間層、Tは濾過材層
、8は炉通材層底部、9は本体底板、10は底面流路、
11は汚泥排出パイプ、12はキャップ、13はFJI
材支持多孔板、14は遮断板、15は濾過材層底板、1
6は仕切板の多孔板、17.18は濾過材、19は濾過
材層天端、A1流入室、B、濾過材室、C1吐出室、D
、水面、(イ)、(ロ)、(ハ)、に)、(ホ)、(へ
)は流れの記号である。 ヤ1 図
FIGS. 1 to 5 are cross-sectional views showing embodiments of the present invention. In the container, 1 is the main body, 2 is the partition plate, 3 is the partition plate water inlet, 4 is the inlet, 5 is the discharge port, 6 is the space layer, T is the filter material layer, 8 is the bottom of the furnace material layer, 9 is the main body bottom plate, 10 is the bottom flow path,
11 is sludge discharge pipe, 12 is cap, 13 is FJI
material supporting porous plate, 14 is a blocking plate, 15 is a filtering material layer bottom plate, 1
6 is a perforated plate of a partition plate, 17.18 is a filtering material, 19 is the top of the filtering material layer, A1 inflow chamber, B, filtering material chamber, C1 discharge chamber, D
, water surface, (a), (b), (c), ni), (ho), (he) are symbols of flow. Figure 1

Claims (4)

【特許請求の範囲】[Claims] (1)槽内を流れ方向に空間層を介して少なくとも1個
以上のろ過材層を立設して仕切り、一端の空間層に流入
口、他端に吐出口を設け、貯水式になるろ過装置に於い
て、底板とろ過材層下部との間に底板に沿つて流路空間
を設け、少なくとも一ケ所以上ろ過材層の下を仕切板で
該流路を遮断し、ろ過材層を横方向に通水或いは接触酸
化により浄化機能が得られる様にしたろ過装置。
(1) The inside of the tank is partitioned by erecting at least one filter layer with a space layer in the flow direction, an inlet is provided in the space layer at one end, and an outlet is provided at the other end, resulting in water storage type filtration. In the device, a flow path space is provided along the bottom plate between the bottom plate and the lower part of the filtration layer, the flow path is blocked at least one place under the filtration layer with a partition plate, and the filtration layer is placed horizontally. A filtration device that achieves purification function through directional water flow or catalytic oxidation.
(2)ろ過材層で底面流路に段差を設け空間層の上昇流
の強化と、充分な緩衝空間が得られる様にする事を特徴
とした特許請求の範囲第一項記載のろ過装置。
(2) The filtration device according to claim 1, characterized in that a step is provided in the bottom channel of the filter material layer to strengthen the upward flow of the space layer and to provide a sufficient buffer space.
(3)吐出側空間層に仕切板を立設して吐出室を区分し
、仕切板の一部を多孔板にし、ろ過材室と連通し、通水
抵抗により部分通水防止作用が得られる様にする事を特
徴とした特許請求の範囲第一項記載のろ過装置。
(3) A partition plate is installed upright in the discharge side space layer to divide the discharge chamber, and a part of the partition plate is made into a perforated plate to communicate with the filter media chamber, so that partial water flow prevention effect can be obtained due to water flow resistance. A filtration device according to claim 1, characterized in that the filtration device has the following features:
(4)最終のろ過材層のろ過材を漉す作用のある人工或
いは天然の繊維質を不規則に絡ませた木毛状物或いは小
砂利などにし、吐出口を底面近くに設けることを特徴と
した特許請求の範囲第一項記載のろ過装置。
(4) The final filter layer is made of artificial or natural fibers that have the effect of straining the filter material, such as wood wool or small gravel, which are irregularly entangled, and the discharge port is provided near the bottom. A filtration device according to claim 1.
JP2291023A 1990-10-29 1990-10-29 Filtering device Pending JPH04166293A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2291023A JPH04166293A (en) 1990-10-29 1990-10-29 Filtering device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2291023A JPH04166293A (en) 1990-10-29 1990-10-29 Filtering device

Publications (1)

Publication Number Publication Date
JPH04166293A true JPH04166293A (en) 1992-06-12

Family

ID=17763455

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2291023A Pending JPH04166293A (en) 1990-10-29 1990-10-29 Filtering device

Country Status (1)

Country Link
JP (1) JPH04166293A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008104999A (en) * 2006-10-27 2008-05-08 Samutekku:Kk Apparatus for treating water to be treated

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008104999A (en) * 2006-10-27 2008-05-08 Samutekku:Kk Apparatus for treating water to be treated

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