JPS60150811A - Continuous filter - Google Patents
Continuous filterInfo
- Publication number
- JPS60150811A JPS60150811A JP59006734A JP673484A JPS60150811A JP S60150811 A JPS60150811 A JP S60150811A JP 59006734 A JP59006734 A JP 59006734A JP 673484 A JP673484 A JP 673484A JP S60150811 A JPS60150811 A JP S60150811A
- Authority
- JP
- Japan
- Prior art keywords
- water
- flow path
- suspended
- channel
- filtered
- 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
Links
Landscapes
- Filtration Of Liquid (AREA)
Abstract
Description
【発明の詳細な説明】
〔技術分野〕
本発明は土砂その他の微粒子を懸濁した大量の水例えば
雨水、掘削水、産業廃水、下水等から懸濁物質を除去し
、懸濁物の少ない水質のものを連続且つ動力を用いずに
得る懸濁水連続f過装置に関する。[Detailed Description of the Invention] [Technical Field] The present invention removes suspended solids from a large amount of water in which earth and sand and other fine particles are suspended, such as rainwater, drilling water, industrial wastewater, sewage, etc., and improves water quality with less suspended solids. This invention relates to a continuous filtration device for suspended water that continuously and without using power.
トンネル、ダム等の土木工事に於いては湧出、流出する
地下水等は土砂を多量に懸濁し、そのま1河川に放流す
ると白濁して種々の公害を引き起す。選鉱、窯業寺の多
量の懸濁物を有する排水も同様に種々の公害の原因とな
る。このため雨水、掘削水、下水や上記の排水の処理と
しては沈砂池全役けである程度の懸濁物全除去した後河
川に放流する方法がとられているが、大量の水を所定時
間滞留させるために沈砂池は大型となり広大な面積を必
要とするという不便がある。このような面積を必要とし
ない処理方法として7f:I過が考えられるが、これは
減圧や加圧を利用するものであり、動力を必要とし、高
価な処理方法となる欠点がある。During civil engineering works such as tunnels and dams, groundwater that gushes out or flows out has a large amount of suspended earth and sand, and if it is discharged directly into a river, it becomes cloudy and causes various types of pollution. Drainage from ore processing and ceramics, which contains a large amount of suspended solids, also causes various types of pollution. For this reason, rainwater, excavation water, sewage, and the above-mentioned wastewater are treated by using a settling basin to remove a certain amount of all suspended matter and then discharging it into rivers. In order to do this, the settling basin becomes large and requires a vast area, which is inconvenient. A possible treatment method that does not require such an area is 7f:I filtration, but this method uses reduced pressure or increased pressure, and has the drawback of requiring power and being an expensive treatment method.
本発明の目的はこの様な状況に鑑み、U字溝や排水管等
の流路金利用してそこで懸濁水をf遇することにより広
大な面積の沈砂池や動力を必要としない懸濁水連続F1
過装置を提供することにある。In view of this situation, the purpose of the present invention is to utilize flow channels such as U-shaped grooves and drainage pipes to collect suspended water there, thereby creating a continuous stream of suspended water that does not require a vast area of settling ponds or power. F1
The objective is to provide a
即ち本発明の要旨は水路中に複数の側面とこれをつなぐ
面とで仕切られた水路と平行な1つ以上の濾過水流路を
有し、少なくとも側面の一部が多孔質板及び/又はf布
で構成されている連続濾過装置にある。That is, the gist of the present invention is to have one or more filtrate water flow paths parallel to the waterway partitioned by a plurality of side surfaces and a surface connecting them, and at least a part of the side surfaces is made of a porous plate and/or f. It is in a continuous filtration device made up of cloth.
本発明の連続濾過装置を図mk用いて説明する。The continuous filtration device of the present invention will be explained using Figure mk.
第1図及び第2図は本発明の連続濾過装置の実施形態を
示す断面斜視模式図でろる。第3図は1過水流路の1例
であり、第4図は側面又はさらに底面、上面の流れ方向
の接続のしかたの1例である。1 and 2 are schematic cross-sectional perspective views showing embodiments of the continuous filtration device of the present invention. FIG. 3 shows an example of one permeable flow path, and FIG. 4 shows an example of how to connect the side, bottom, and top surfaces in the flow direction.
図面において1は水路の壁であり、2は濾過水流路を示
す。第1図では濾過水流路2は2つの側面3と底面4と
上面5の2つの水平面でかこまれており、濾過水流路2
が3本設置された例が示されている。これらの1過水流
路は適当な支柱あるいは梁等(図示せず)で水路内に浮
んだ形で設置されており、水路内のe過水流路以外の空
間が懸濁水流路6となる。第2図では水路内を複数組の
側面3群と隣りあう側面の下部と上部全交互に水平な仕
切ジでつないで懸濁水流路6と1過水流路2にわけたも
のである。In the drawings, 1 is the wall of the water channel, and 2 is the filtrate flow path. In FIG. 1, the filtrate flow path 2 is surrounded by two horizontal planes, ie, two side surfaces 3, a bottom surface 4, and a top surface 5.
An example in which three are installed is shown. These 1 overwater flow passages are installed in a floating manner within the water channel using suitable supports or beams (not shown), and the space other than the e overflow flow passages within the waterway becomes the suspended water flow path 6. In FIG. 2, the inside of the water channel is divided into a suspended water flow path 6 and a superfluous water flow path 2 by connecting the three groups of side surfaces and the lower and upper portions of the adjacent side surfaces alternately with horizontal partitions.
第2図では側面と底面で口字を形成しているが底面をな
くしてV字型にしてもよい。水路壁と水平な仕切りは密
指しており、懸濁水と濾過水が混合しないようになって
いる。両端の水平な仕切りと水路壁は水平な仕切りを水
路壁の上にまで出してそこで固定してもよい。この濾過
水流路は水路中で水路に平行に設置されており、濾過水
流路の長さは長い方がe過面積を大きくとれる点で好ま
しく、処理すべき懸濁水の水量、流速、懸濁物濃度にも
よるが、一般的には30毒以上あることが好ましく、処
理効率と費用の −かねあいから507)z乃至2 k
mであることがより好ましい。長さの上限は該連続濾過
装置を設置する水路の長さにより制限されることは言う
までもない。In FIG. 2, the sides and bottom form a mouthpiece, but the bottom may be omitted to form a V-shape. The channel walls and horizontal partitions are closely spaced to prevent the suspended water and filtered water from mixing. The horizontal partitions and channel walls at both ends may extend above the channel walls and be fixed there. This filtrate flow path is installed parallel to the waterway in the waterway, and the longer the length of the filtrate water flow path is, the more preferable it is because it can increase the filtration area. Although it depends on the concentration, it is generally preferable to have 30 toxins or more, and from the viewpoint of treatment efficiency and cost, 507)z to 2k.
More preferably, it is m. Needless to say, the upper limit of the length is limited by the length of the waterway in which the continuous filtration device is installed.
懸濁水流路6は1過面で濾過されない懸濁物が丁におち
てたまったり、懸濁水流に押し流されて排除されること
全考慮すれば、第1図、第2図のように水路底に接する
側であることが好ましいが、懸濁水の水質によ゛ろては
その逆の配置であってもよい。The suspension water flow channel 6 is a waterway as shown in Figs. 1 and 2, taking into account that unfiltered suspended matter may fall on the filter surface and accumulate, or be swept away by the suspension water flow and removed. Although it is preferable that the side be in contact with the bottom, the opposite arrangement may be possible depending on the quality of the suspension water.
1過水流路2には懸濁水流路6を流れる水の一部が流路
6に接する側面3、又はさらに底面4、上面5で懸濁物
を1別されてきれいになった水が入ってくる。1. In the superhydrous flow path 2, part of the water flowing through the suspended water flow path 6 enters the side surface 3 in contact with the flow path 6, or water that has been purified by separating suspended substances at the bottom surface 4 and top surface 5. come.
以下、このp別を行う面を一過面と言うが、少なくとも
側面6の一部が濾過面である必要があり、側面全体が一
過面であることが好ましく、さらVC底面4、存在すれ
ば上面5も1過面であることが好ましい。Hereinafter, the surface that performs this P separation will be referred to as a transient surface, but at least a part of the side surface 6 needs to be a filtering surface, and it is preferable that the entire side surface is a transient surface. For example, it is preferable that the upper surface 5 is also a polygonal surface.
一過面は多孔質あるいは網目状の金属ちるいは樹脂製の
薄板(以下多孔質板という)で形成されているかあるい
はC布支持板で支持されたe布で形成されている。The temporary surface is formed of a porous or mesh-like metal or resin thin plate (hereinafter referred to as a porous plate), or is formed of e-cloth supported by a C-cloth support plate.
多孔質板の孔の大きさ網目の大きさP布の濾過%注は処
理すべき懸濁水の水質、必要とする1過蚕、14過水質
により異なり、これらの要求に応じて適宜選択すればよ
い。f布としては市販されているどのよりな1布も用い
ることができるがポリエステル、ポリオレフィン糸ナイ
ロ/、ポリ塩化ビニル寺の合成繊維フィラメント1布が
好ましく用いられる。さらにP布の一方の面に毛羽分有
するフィラメントj4布が好ましく用いられる。The pore size of the porous plate, the mesh size, P, and the filtration percentage of the cloth vary depending on the quality of the suspended water to be treated and the required quality of 1- or 14-filtered water, and should be selected appropriately according to these requirements. good. As the fabric, any commercially available strand fabric can be used, but synthetic fiber filament fabrics such as polyester, polyolefin thread nylon/polyvinyl chloride, etc. are preferably used. Further, a filament J4 cloth having fluff on one side of the P cloth is preferably used.
νIJちFl−過面土砂等の忽′FA物の大半を阻止し
て1過水爺か適当量得られるものであればどのようなも
のも用いることが出来るが、上述の多孔質板又I′iP
布であることが好ましい。Any material can be used as long as it can block most of the FA substances such as νIJ, Fl-surface sediment, etc., and obtain a suitable amount of 1% water, but the above-mentioned porous plate or I 'iP
Preferably, it is cloth.
このような連続濾過装置の一例を示すと第3図に示すよ
うな側面と底面が多孔質板で形成された側面の長い凹状
の断面を有するものであシ、側面の上部はおたがいには
めおいが可能な凹部と凸部が形成されている。この多孔
質板をそのまままたはその上にさらにf布をはってP布
の端と一諸に右上の四部8に他の同様なセットの左上の
凸部9をはめこんで連結して多数の凹状部を有する濾過
水流路を形成することができる。An example of such a continuous filtration device is as shown in Fig. 3, which has a long concave cross-section with side and bottom sides formed of porous plates, and the tops of the sides are fitted with each other. Possible recesses and protrusions are formed. This porous plate can be used as it is, or by further placing F cloth on top of it and connecting it with the edge of P cloth by inserting the convex part 9 in the upper left of another similar set into the four parts 8 in the upper right. A filtrate water flow path having a concave portion can be formed.
このような凹凸はめこみの代参に側面上部に平板をつけ
てボルト止め等の方法で遅結してもよい。A flat plate may be attached to the upper part of the side surface as a substitute for fitting into such irregularities, and the connection may be delayed by bolting or the like.
連続f過装置は1本の箱屋あるいは断面U字型の1通水
派路で形成されていてもよいがf過能力号?勘来すると
第1図あるいは第2図に示すように箱型やU字型の流路
が水路中に複数個設置されていることが好ましい。The continuous f-passage device may be formed by a single box or one water branch with a U-shaped cross section, but is the f-overcapacity number? In view of this, it is preferable that a plurality of box-shaped or U-shaped channels are installed in the water channel as shown in FIG. 1 or 2.
これらのC適宜めるいはその他f過水流路を形成する壁
は濾過水流路の端から端まで一枚の多孔質板やP布で形
成キれていてもよいが実用面からみると例えば第4図に
示すように流れ方向に沿って何枚かの多孔質板やf布及
びその支持体が例えばはめあい10で結合されて1過水
流路壁を構成していることが好ましい。結合方法は濾過
水と懸濁水の著しい混合がおこらなければどのような方
法であってもよい。結合する単位1つの長きは50備乃
至6常であることが設置VCあたって便利である。The wall forming the filtrate channel may be made of a single porous plate or P cloth from one end of the filtrate channel to the other, but from a practical point of view, for example, As shown in FIG. 4, it is preferable that several porous plates, fabrics, and their supports are connected along the flow direction, for example, with fittings 10, to constitute one permeable flow channel wall. Any method of combining may be used as long as significant mixing of the filtered water and suspended water does not occur. It is convenient for the installed VC that the length of one unit to be combined is 50 to 6.
この濾過水流路の上流側末端は例えば水路上流側末端に
つないで封鎖するあるいは別に端面をふさぐ仕切板等を
用いる。端面部分で両側面をくつつける等懸濁水が濾過
されないまま濾過水流路2に入らない工夫がされておれ
ばどのような方式でおってもよい。The upstream end of the filtrate flow path may be connected to the upstream end of the waterway to be closed off, or a partition plate or the like may be used to separately block the end surface. Any method may be used as long as the suspended water does not enter the filtrate flow path 2 without being filtered, such as by attaching both sides at the end portions.
1iti水流路の下流側末端は濾過水が懸濁水ヤ念11
A物と混合しないで放流あるいは回収、利用できるよう
になっていればよい。At the downstream end of the water flow path, the filtered water is suspended.
It is sufficient as long as it can be discharged, collected, and used without mixing with substance A.
本発明の連続f過装置全設置する水路は各種形状の管状
水路、上部の開いた溝型水路等どのよう′な形状でも適
用できるが、U字溝であれば設置、保守が容易であるこ
と、ふた會すればその上を道路等に使用でき実質上水路
用のそれ以外に用い得ない空間が生じないことからU字
溝が好ましい。The waterways in which the entire continuous filtration device of the present invention is installed can be of any shape, such as tubular waterways of various shapes, groove-type waterways with an open top, etc., but installation and maintenance are easy if they are U-shaped grooves. A U-shaped groove is preferable because if the lids are assembled, the top can be used for roads, etc., and there is virtually no space left that cannot be used for anything other than waterways.
水路の本発明の連続f過装置の下流には懸濁水流路に流
量せきや沈砂池全段けてもよい。この沈砂池は設けると
しても比較的小さい容量のものでよい。A flow rate weir or a settling basin may be installed in the suspended water flow path downstream of the continuous filtering device of the present invention in the waterway. Even if this settling basin is provided, it may have a relatively small capacity.
懸濁水流路6に入った懸濁水はf過量で土砂等がC別さ
れて1過水が1過水流路2f通って流Fし、下流で集め
られて目的に応じて利用されたり、回収されたり河川に
放流されたりする。The suspended water that has entered the suspended water flow path 6 is separated by F excess and sediment, etc., and flows through the 1 over water flow path 2 F, and is collected downstream and used or recovered. or discharged into rivers.
f別された土砂寺はe退部に一部残留するが大部分は懸
濁水とともに懸濁水流路6を流下する。f過量に残留し
た土砂等f′i懸濁水流賃が低下あるいはなくなった時
に乾燥してf過量から自然に懸濁水流路内に脱落する。A part of the separated Dosunaji (f) remains in the e-retirement section, but most of it flows down the suspension water channel 6 along with the suspended water. When the flow rate of the suspension water f'i decreases or disappears, the soil and sand remaining in the excess quantity f dries and naturally falls from the excess quantity f into the suspension water channel.
この脱落した土砂類は次回の流水時に下流に流され沈降
する。This fallen sediment will be washed downstream and settle during the next flush.
またf過面に土砂類が口塞りした場合は濾過水、井戸水
、河川水等の土砂の少ない水を必要に応じて濾過水流路
側に流してI濾過面から懸濁水流路側に濾過するように
する逆洗を行ってもよい。In addition, if the F filtration surface is clogged with sediment, water with less sediment such as filtered water, well water, river water, etc. can be flowed to the filtrate water flow path side as necessary, and filtered from the I filtration surface to the suspended water flow path side. You may also perform backwashing.
f別された土砂類は集めて埋立地等に利用できる。Sediment that has been sorted can be collected and used as a landfill.
本発明の特徴はe過設備あるいは沈砂池に大きな面積を
必要とすることなく、本来必要な導水溝(水路)をその
ままあるいは若干断面積を大さくすることによって土砂
のP別が可能である点にあり、水路にふたをするあるい
は水路を地中に埋めこむことによって実質上の土地を必
要としないことにあり、経済効果、土地利用効果を優れ
たものである。The feature of the present invention is that it is possible to separate P by using the originally necessary water guide channel (channel) or by slightly increasing the cross-sectional area, without requiring a large area for e-filtration equipment or a settling basin. It has excellent economic and land use effects because it virtually does not require land by covering the waterway or burying the waterway underground.
以下実施例を用い本発明をさらに詳しく説明する。 The present invention will be explained in more detail below using Examples.
実施例1
第2図における側面の高さ750、底面の巾4cmの多
孔鋼板製の支持体からなるU字型みぞが5個均等な間隔
でならぷ様に側面上部を平板でつなぎ、その外側にポリ
エステルフィラメントよりなるf布を支持体に密層させ
てはって、これを断面中1常、深さ1mのU字溝に底か
ら約25mの位置に下部が位置する様に設置して作った
長さ15mのユニットヲ多数製作し、このユニットを上
流ダム工事現場から約1 km下流の沈砂北進つなげて
設置し、白濁したダム工事湧出水k 10 m”/分の
童で流したところ、湧出水はf布で懸濁物が除去された
後濾過水流路を通り、下流に設けた集水ビートに集めら
れた。Example 1 Five U-shaped grooves made of a perforated steel plate support with a side height of 750 mm and a bottom width of 4 cm in Fig. 2 are connected at the upper part of the side surface with a flat plate in a row arranged at equal intervals, and the outside thereof is F fabric made of polyester filament was densely layered on a support and placed in a U-shaped groove with a depth of 1 m throughout the cross section so that the lower part was located approximately 25 m from the bottom. A number of 15 m long units were manufactured, and these units were installed by connecting them to a sand basin about 1 km downstream from the upstream dam construction site, and the cloudy dam construction spring water was flushed at a rate of 10 m''/min. After removing suspended solids from the spring water, it passed through a filtered water channel and was collected in a water collection beet provided downstream.
−過水の濁度は減少して透視度30口以上となったので
そのまま河川に放流した。U字溝下層流(懸濁水)に沈
砂池で処理されたが連続1過装置全用いない場合に較べ
分離効率は尚く短時間で上澄水が透視度30m以上とな
り放流可能であった。-The turbidity of the excess water decreased and the visibility became over 30 mouths, so it was discharged directly into the river. Although the lower flow (suspended water) of the U-shaped groove was treated in a settling basin, the separation efficiency was still higher than when the continuous filtration device was not used at all, and the supernatant water had a visibility of 30 m or more and could be discharged in a short time.
連続逍水全続けたところ1M間後vc1)=過水量が7
0%程度にまで低下したので、濾過水流路側に湧出水を
10 mj/ hr で30分間通水してf退部全逆洗
し1布内に目Mりした土砂を除去した。再び下層に通水
すると1過水流量は最初のf通商の場合の96チ迄回復
した。After continuous water application for 1M, the amount of excess water was 7.
Since it had decreased to about 0%, spring water was passed through the filtrate flow path at a rate of 10 mj/hr for 30 minutes to backwash the entire f-recess and remove the dirt that had formed inside the cloth. When the water was passed to the lower layer again, the flow rate of 1 per water recovered to 96 cm, which was in the case of the first f-commerce.
実施例2
低位土地の住宅街では大雨時の排水対策として深層地下
水層へ降雨水を浸透して住宅街の浸水による被讐を最小
限にとどめる試みがあり、このため住宅域にU字#を縦
横に設置して降雨水を集め排出している。Example 2 In residential areas on low-lying land, there is an attempt to minimize damage caused by flooding in residential areas by infiltrating rainwater into deep underground water layers as a drainage measure during heavy rains. They are installed vertically and horizontally to collect and discharge rainwater.
この地下水層への浸透方式の場合、降雨当初は極めて効
率良く浸透排出することができるが間もなく降雨水に随
伴される土砂により地下浸透層が口塞、!lllを起し
排水効率が急激に低下してくるという欠点がある。In the case of this infiltration method to the groundwater layer, it is possible to infiltrate and drain extremely efficiently at the beginning of rainfall, but soon the underground infiltration layer becomes clogged by the sediment accompanying the rainwater! This method has the disadvantage that the drainage efficiency rapidly decreases.
この住宅街のふたつ@U字型道路側溝(断面積60 c
m X 60 cm )内に05調φの孔のあいた多孔
樹脂板製の平行板(巾45m)?側面とし、同様の材料
からなる巾4mの底面と一ヒ面からなる第1図に示した
ような形状の長さ10mの濾過水流路を6個水路に平行
に水路底から10crnの位置に設置した。Two U-shaped road gutters in this residential area (cross-sectional area: 60 cm)
Parallel plate (width 45 m) made of porous resin plate with holes of 05 scale φ in the width (width 45 m)? Six 10 m long filtrate channels with a shape as shown in Figure 1, each consisting of a 4 m wide bottom and a side made of the same material, are installed parallel to the water channel at a distance of 10 crn from the water channel bottom. did.
また約100m四方の区域当り1個ある地下浸透用の井
戸の四方30愼分11−X1mのふた付きU字溝を用い
た実施例1に示したユニットを設置しユニット濾過水流
路に前記60副×60mのU字型側溝内の濾過水が流れ
こみ懸濁水路には土砂を含む懸濁水が流れこむようにし
た。このf過装置を設置することにより地下浸透層の目
基ジによる効率低下は著しく軽減され半永久的Vこ排水
稼動できるようになった。口塞りは降雨量約1000−
程度になる度に逆洗全行うことにより充分にe過性能ヲ
回復することができた。In addition, the unit shown in Example 1 using a U-shaped groove with a lid measuring 11 x 1 m for 30 wells on each side for underground infiltration, which is one well per approximately 100 m square area, was installed, and the 60 sub-wells were installed in the filtrate water flow path of the unit. Filtered water from a 60 m U-shaped gutter flows into the suspension channel, and suspended water containing soil flows into the suspension channel. By installing this f-filtration device, the decrease in efficiency due to the scale of the underground permeation layer was significantly reduced, and semi-permanent V-drainage operation became possible. The amount of rainfall is about 1000-
By performing complete backwashing every time the condition reached a certain level, we were able to sufficiently recover the e-overperformance.
本設備全導入することにより本来なら数時間分の涌留容
量金有する沈砂池を必要とするのか不快となり、住宅地
の有効利用に多大の経済効果が得られた。By fully introducing this equipment, the need for a settling basin with a storage capacity of several hours was no longer necessary, and a great economic effect was obtained in the effective use of residential areas.
実施例6
従来560 、’/日の栗色廃水fakC及び高分子凝
集剤を用いた凝集沈澱処理の後涌留時間8時間以上の大
型沈降槽で処理していた工場の凝集沈澱処理後の廃水全
沈降槽に導く断面積1m X 1 mのU字溝内に実施
例1と同一の寸法で多孔鋼板が孔径7 tynX 7
cmのノ(ンチング鋼板でf布としてポリエチレンモノ
フィラメント製の平織りf布を張ったユニットを全要約
2 kmにわたって設置し、大型沈降槽の代りに小型沈
降槽(滞留時間30分)を設置した。濾過水及び小屋沈
降槽を出た上澄水を最終調整槽でpHを調節しpHとT
OCを測定しながら河川に放流した。水質はpH6,5
〜B、0、TOC15〜20 pprnで無色で透視度
も55cm以上であった。これにより大型沈降槽が不要
になり、設備費が軽減されたのみならず工場敷地の有効
利用をはかることができ、経済効果は極めて大きかった
。Example 6 All of the wastewater after coagulation and sedimentation treatment from a factory that was conventionally treated in a large sedimentation tank with a retention time of 8 hours or more after coagulation and sedimentation treatment using a polymer flocculant A perforated steel plate with the same dimensions as in Example 1 was installed in a U-shaped groove with a cross-sectional area of 1 m x 1 m leading to the settling tank.
A unit made of thinned steel plates covered with a plain weave fabric made of polyethylene monofilament was installed over a total distance of 2 km, and a small sedimentation tank (residence time 30 minutes) was installed in place of the large sedimentation tank. The pH of the water and supernatant water from the shed settling tank is adjusted in the final adjustment tank, and the pH and
It was discharged into a river while measuring OC. Water quality is pH 6.5
~B, 0, TOC 15-20 pprn, colorless, and transparency was 55 cm or more. This not only eliminated the need for a large sedimentation tank, reducing equipment costs, but also allowed for effective use of the factory site, resulting in extremely large economic effects.
第1図及び第2図は本発明の連続1過装置の実施形態會
示す断面斜視模式図である。
第3図は連続1過装置の凹状断面を有する部分の横方向
の結合方式を示す1例で必9、第4図は流れ方向の結合
の例である。
1 水路壁 6 懸濁水流路
2 濾過水流路 7 多孔質板
3 側面 8 凹部
4 底面 9 凸部
5 上面 10 はめあい部分
せ I 図
+2図
脅 3 図
+ 4 図FIGS. 1 and 2 are schematic cross-sectional perspective views showing embodiments of the continuous one-pass device of the present invention. FIG. 3 shows an example of a lateral coupling method for the concave section of a continuous flow device, and FIG. 4 shows an example of a flow direction coupling method. 1 Channel wall 6 Suspended water flow path 2 Filtered water flow path 7 Porous plate 3 Side surface 8 Recessed portion 4 Bottom surface 9 Convex portion 5 Top surface 10 Fitting portion I Figure + 2 Figure 3 Figure + 4 Figure
Claims (1)
た水路と平行なf過水流路を有し、少なくとも側面の一
部が多孔質板及び/又はl」布で構成きれている連続f
過装置。 2)f−i過水流路と水路底部が離れていることを特徴
とする特許請求の範囲第1項記載の連続1過装置。[Scope of Claims] 1) The water channel has an overwater flow path parallel to the water channel partitioned by a plurality of side surfaces and a surface connecting these, and at least a portion of the side surfaces are porous plates and/or l. Continuous f made up of cloth
device. 2) The continuous 1 filtration device according to claim 1, characterized in that the f-i filtration flow path and the bottom of the water channel are separated from each other.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP59006734A JPS60150811A (en) | 1984-01-18 | 1984-01-18 | Continuous filter |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP59006734A JPS60150811A (en) | 1984-01-18 | 1984-01-18 | Continuous filter |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS60150811A true JPS60150811A (en) | 1985-08-08 |
Family
ID=11646451
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP59006734A Pending JPS60150811A (en) | 1984-01-18 | 1984-01-18 | Continuous filter |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS60150811A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100843036B1 (en) | 2007-03-19 | 2008-07-01 | 한상배 | Horizontal Filtering Device for Wastewater and Water Treatment |
-
1984
- 1984-01-18 JP JP59006734A patent/JPS60150811A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100843036B1 (en) | 2007-03-19 | 2008-07-01 | 한상배 | Horizontal Filtering Device for Wastewater and Water Treatment |
WO2008114897A1 (en) * | 2007-03-19 | 2008-09-25 | Sang Bae Han | Horizontal filtering device for wastewater and water treatment |
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