JPH02139008A - Cleaning method for filter - Google Patents

Cleaning method for filter

Info

Publication number
JPH02139008A
JPH02139008A JP29187988A JP29187988A JPH02139008A JP H02139008 A JPH02139008 A JP H02139008A JP 29187988 A JP29187988 A JP 29187988A JP 29187988 A JP29187988 A JP 29187988A JP H02139008 A JPH02139008 A JP H02139008A
Authority
JP
Japan
Prior art keywords
filter
filter layer
cleaning
layer
cleaning fluid
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
JP29187988A
Other languages
Japanese (ja)
Other versions
JP2829993B2 (en
Inventor
Yoshinari Fujisawa
能成 藤沢
Hideji Takeuchi
竹内 秀二
Shinichi Endo
伸一 遠藤
Seiichi Kanamori
聖一 金森
Yuji Yoshii
吉井 裕二
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP29187988A priority Critical patent/JP2829993B2/en
Publication of JPH02139008A publication Critical patent/JPH02139008A/en
Application granted granted Critical
Publication of JP2829993B2 publication Critical patent/JP2829993B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Abstract

PURPOSE:To clean a filter, even when washing fluid is introduced with small flow velocity, in a short period of time almost completely by introducing a grain material into a filter layer fixed to a filter together with the washing fluid and cleaning the same. CONSTITUTION:A filter 1 is formed by disposing a filter layer 3 fixed in a filter main body 2, and a filter medium of large void content is filled in the filter layer 3. A grain material 4 is stored in a bottom section of the filter main body 2 during filtering operation, and washing fluid 7 is introduced from the lower section of the filter main body when a filter layer 3 is cleaned. The grain material 4 is flown up by the upward flow of the fluid 7 to be cleaned and fluidized in a filter main body 2 including the filter layer 3, and the fluid 7 only forms cleaning drain 8 to be drained out of the front section of the main body 2. The grain material 4 is collided with the filter medium filled in the filter layer 3 to peel off suspended solids of the filter layer 3.

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は濾層を固定した濾過器における4層の洗浄方法
に係り、特に都市下水、産業排水などの有機性排水を処
理する前記濾過器の4層を洗浄するのに好適な方法に関
する。
Detailed Description of the Invention [Industrial Application Field] The present invention relates to a four-layer cleaning method for a filter having a fixed filter layer, and particularly to the filter for treating organic wastewater such as urban sewage and industrial wastewater. A method suitable for cleaning four layers of.

[従来の技術] 用水や排水中の懸濁性固形物(以下、ssと云う)を除
去する場合、濾材を充填して濾層を形成した濾過器を使
用し、被処理水を濾過する操作が行われている。この濾
過器においては、SSの捕捉によって濾層に目詰まりが
生ずるため、ある濾過時間が経過する毎に濾層の洗浄を
行う必要がある。濾層の洗浄は、濾層の下方から、水、
水及び空気などの洗浄流体を供給し、濾層に付着した5
St−剥離して洗浄流体中に懸濁させ、洗浄流体ととも
に排出する方法によって行われている。
[Prior Art] When removing suspended solids (hereinafter referred to as ss) from water or wastewater, the water to be treated is filtered using a filter filled with a filter material to form a filter layer. is being carried out. In this filter, the filter layer becomes clogged due to the capture of SS, so it is necessary to wash the filter layer every time a certain filtration time elapses. To wash the filter layer, use water and water from below the filter layer.
Cleaning fluid such as water and air is supplied, and the 5
This is carried out by a method in which St- is peeled off, suspended in a cleaning fluid, and discharged together with the cleaning fluid.

[発明が解決しようとする課wi] 濾層を洗浄する際、充填された濾材が粒状濾材であれば
、洗浄流体の上昇流によって濾材粒子が移動したりある
いは流動したりし、濾材粒子同志の擦り合いや衝突を繰
り返すので、濾材に付着したSSは容易に剥離する。し
かし、濾材を充填した濾層が固定されている場合には、
洗浄流体を供給しても濾材は実質的に動くことはなく、
従って、この場合の濾材の洗浄は洗浄流体のエネルギー
だけで行われることになる。
[Problem to be solved by the invention] When cleaning a filter layer, if the filled filter medium is a granular filter medium, the filter medium particles move or flow due to the upward flow of the cleaning fluid, and the filter medium particles become separated from each other. SS adhering to the filter medium is easily peeled off due to repeated rubbing and collision. However, if the filter layer filled with filter media is fixed,
Even when cleaning fluid is supplied, the filter media does not move substantially.
Therefore, cleaning of the filter medium in this case is performed only by the energy of the cleaning fluid.

このため、濾層が固定されている場合には、濾層の洗浄
は長時間を要する。また、洗浄流体のエネルギーだけで
洗浄するので、洗浄流体の流速を大きくしなければなら
ず、従って、多量の洗浄流体を必要とする。さらに、こ
のような洗浄においては、ときには濾層の洗浄が不十分
の状態となることがある。濾層の洗浄が不十分であると
、付着したSSが固着して以後の剥離が困難になって、
濾層が部分的に閉塞して被処理水の偏流が生じ濾過効率
が低下したり、さらには、濾材に固着したSSが醗酵し
てガスを発生し、SSの除去率を低下させたり、あるい
は装置の腐食や悪臭発生の原因となる。
Therefore, if the filter layer is fixed, cleaning the filter layer requires a long time. Further, since cleaning is performed using only the energy of the cleaning fluid, the flow rate of the cleaning fluid must be increased, and therefore a large amount of cleaning fluid is required. Furthermore, in such washing, the filter layer may sometimes be insufficiently washed. If the filter layer is not washed sufficiently, the attached SS will stick and become difficult to remove later.
Partial blockage of the filter layer may cause a biased flow of the water to be treated, reducing filtration efficiency. Furthermore, SS stuck to the filter medium may ferment and generate gas, reducing the SS removal rate. This may cause corrosion of the equipment and generation of bad odors.

本発明は、濾層が固定されている濾過器における従来技
術の問題点を解決し、濾層の洗浄時間が短く、洗浄流体
の使用量が少なく、且つ濾層の洗浄をほぼ完全に行うこ
とができる濾過器の洗浄方法を提供することを目的とす
る。
The present invention solves the problems of the prior art in filters with a fixed filter layer, reduces the cleaning time of the filter layer, uses less cleaning fluid, and almost completely cleans the filter layer. The purpose of the present invention is to provide a filter cleaning method that enables the cleaning of filters.

[課題を解決するための手段及び作用]上記の目的を達
成するために、本発明の方法においては、濾層を固定し
た濾過器における濾層の洗浄方法において、前記濾層に
洗浄流体とともに粒状物を導入して前記濾層を洗浄する
[Means and effects for solving the problem] In order to achieve the above object, in the method of the present invention, in a method for cleaning a filter layer in a filter having a fixed filter layer, particulate particles are added to the filter layer together with a cleaning fluid. to wash the filter layer.

この際、導入した粒状物を濾層中に滞留させながら流動
させて濾層を洗浄してもよく、また、導入した粒状物を
洗浄流体とともに濾層を通過させて濾過器本体から排出
し、排出した粒状物を回収して前記濾過器本体内に循環
しながら濾層を洗浄してもよい。
At this time, the introduced particulates may be allowed to flow while remaining in the filter layer to wash the filter layer, or the introduced particulates may be passed through the filter layer together with the cleaning fluid and discharged from the filter body. The filter layer may be washed while collecting the discharged particulate matter and circulating it within the filter main body.

本発明の洗浄方法は、一般の濾材に比べ空隙率の大きい
濾材を充填して濾層が形成され、この濾層を固定した構
成による濾過器に適用するものである。そして、充填さ
れた濾材に粒状物を衝突させ、この衝突エネルギーによ
って濾材に付着したSSを剥離するものである。この洗
浄時に濾過器本体内を通過する洗浄流体の流速は、洗浄
流体が水だけの場合には40〜100m/時程度、空気
と水を別々に供給し空気次いで水の順序で洗浄する場合
の空気及び水の流速は、それぞれ30〜Loom/時程
度、40〜100m/時程度にする。また水と空気を同
時に供給する場合には50〜200m/時程度にする。
The cleaning method of the present invention is applied to a filter in which a filter layer is formed by filling a filter medium with a larger porosity than a general filter medium, and the filter layer is fixed. Then, particles are caused to collide with the filled filter medium, and SS adhering to the filter medium is peeled off by this collision energy. The flow rate of the cleaning fluid passing through the filter body during this cleaning is approximately 40 to 100 m/hour when the cleaning fluid is water only, and when air and water are supplied separately and cleaning is performed in the order of air and water. The flow rates of air and water are approximately 30 to 100 m/hour and approximately 30 to 100 m/hour, respectively. In addition, when water and air are supplied at the same time, the flow rate is approximately 50 to 200 m/hour.

粒状物としては、砂、アンスラサイトなどの天然物、金
属粉、セラミックスなどの無機合成物、合成樹脂などの
粒のように、耐磨耗性があり、被処理水によって変質す
ることがなく、溶出成分を含まないものを選定する。
Granular materials such as natural materials such as sand and anthracite, inorganic composite materials such as metal powder and ceramics, and synthetic resin grains have abrasion resistance and do not change in quality due to the water being treated. Select one that does not contain eluted components.

粒状物の種類、比重、粒子径などは洗浄条件によって適
宜法める。このうち、粒状物の粒子径は洗浄流体の流速
によって決定され1通常は第1表に示した程度の大きさ
にする。
The type, specific gravity, particle size, etc. of the granular material are determined as appropriate depending on the cleaning conditions. Among these, the particle size of the granules is determined by the flow rate of the cleaning fluid, and is usually set to the size shown in Table 1.

第1表に記載した粒子径は洗浄流体の流速が次の範囲に
おける値を示したものである0粒子径を限定した洗浄流
体の流速は、洗浄流体が水だけの場合には40〜70m
/時、水と空気を同時に供給する場合にはその合計量に
よる流速が70〜100m/時、空気と水を別々に供給
し空気次いで水の順序で洗浄する場合には30〜70m
/時のである。
The particle sizes listed in Table 1 indicate the values in which the flow velocity of the cleaning fluid is within the following range.
/hour, when water and air are supplied at the same time, the flow rate based on the total amount is 70 to 100 m/hour, and when air and water are supplied separately and the air and water are washed in that order, the flow rate is 30 to 70 m/hour.
/It is time.

第1表  粒状物の粒径例(龍) 濾層への粒状物の導入量は、濾層容積に対し1〜10%
程度か適当であり、好ましくは3〜7%程度にするのが
よい。
Table 1 Example of particle size of granular material (Dragon) The amount of granular material introduced into the filter layer is 1 to 10% of the filter layer volume.
The amount is appropriate, preferably about 3 to 7%.

[実施例] 第8図〜第10図は、本発明の洗浄方法が適用できる濾
過器に充填される濾材の一部を模式的に示した図である
[Example] FIGS. 8 to 10 are diagrams schematically showing a part of a filter medium filled in a filter to which the cleaning method of the present invention can be applied.

第8図の濾材20は、塩化ビニリデン、ポリエチレン、
塩化ビニールなどの合成繊維あるいはステンレス鋼など
の金属線等の耐水性繊維21を結合剤で被覆結合して不
織に形成し、三次元の網目様構造の直方体や立方体にし
たものである。濾材20を構成する耐水性繊維21の径
は100デニール(約0.091園諷〉〜10000デ
ニール(約0−0−91aの範囲である。そして、濾材
20の空隙率は90%〜99.5%の範囲である。この
空隙率は、濾過器の洗浄時において粒状物の通過または
流動が容易であり、且つSSの除去率が低下しない範囲
である。この濾材20により濾層を形成する方法は、濾
過塔内に敷き詰めるように充填して固定層とする。
The filter medium 20 in FIG. 8 is made of vinylidene chloride, polyethylene,
Water-resistant fibers 21 such as synthetic fibers such as vinyl chloride or metal wires such as stainless steel are coated and bonded with a binder to form a non-woven structure into a rectangular parallelepiped or cube having a three-dimensional mesh-like structure. The diameter of the water-resistant fibers 21 constituting the filter medium 20 is in the range of 100 denier (approximately 0.091 mm) to 10,000 denier (approximately 0-0-91 a), and the porosity of the filter medium 20 is 90% to 99. The porosity is in the range of 5%. This porosity is within a range where particulates can easily pass through or flow during cleaning of the filter, and the removal rate of SS does not decrease. This filter medium 20 forms a filter layer. The method is to fill a filtration tower so as to cover it all over to form a fixed bed.

第9図の各濾材20は各種の濾材材料を円筒状に形成し
たものである。その濾材材料として、 la1図は第7
図の濾材と同様に耐水性繊維を不織に形成したものであ
り、(b)図は金属線あるいは合成樹脂の単繊維を織物
状にしたちである。またIC1図は多数の細孔を設けた
金属板あるいは合成樹脂板である。これらの濾材は濾過
塔内に規則充填あるいは不規則充填して使用する。
Each filter medium 20 in FIG. 9 is formed from various filter medium materials into a cylindrical shape. As the filter medium material, the la1 diagram shows the 7th
Like the filter medium shown in the figure, it is made of non-woven water-resistant fibers, and the figure (b) is made of metal wire or single fibers of synthetic resin woven into a woven form. Further, IC1 diagram shows a metal plate or a synthetic resin plate provided with a large number of pores. These filter media are used by being packed regularly or irregularly in a filtration tower.

第10図の濾材は、fat図及びfb1図の濾材材料2
2をIC1図のように組み立てたものである。(a)図
の濾材材料22は金属線あるいは合成樹脂の単繊維を織
物状にしたらであり、またtbt図の濾材材料22は多
数の細孔を設けた金属板あるいは合成樹脂板である。(
C)図は組み立てられた濾材の断面を示し、22は上記
の濾材材料、23は濾材材料の保持枠であり、保持枠2
3は濾材材料22を挟んで濾材20を形成させるととも
に、その厚さを適度にすることによって濾材材料22.
22の間隔を決めるスペーサーの役割をしている。この
保持枠23の厚さを変えることによって空隙率の異なる
濾材20を得ることができる。この濾材20は濾過塔内
に敷き詰めて充填する。
The filter material in Figure 10 is the filter material 2 in the fat diagram and fb1 diagram.
2 is assembled as shown in the IC1 diagram. The filter material 22 in the figure (a) is a woven metal wire or single fiber of synthetic resin, and the filter material 22 in the tbt figure is a metal plate or a synthetic resin plate provided with a large number of pores. (
C) The figure shows a cross section of the assembled filter medium, 22 is the above-mentioned filter medium material, 23 is a holding frame for the filter medium material, and holding frame 2
3 forms the filter medium 20 by sandwiching the filter medium material 22, and the thickness of the filter medium 22.
It plays the role of a spacer that determines the distance between 22. By changing the thickness of this holding frame 23, filter media 20 with different porosity can be obtained. This filter medium 20 is spread and packed inside the filter tower.

以下、上記のような空隙率が非常に大きい濾材を充填し
た濾過器の洗浄方法について説明する。
Hereinafter, a method for cleaning a filter filled with a filter medium having a very high porosity as described above will be described.

第1図は本発明の第一実施例を示した図である。第1図
において、1は濾過器本体2内に固定された濾M3を備
えた濾過器であり、濾層3には′第8図〜第10図に示
したような空隙率の大きい濾材が充填されている。4は
砂、アンスラサイト、合成樹脂粒などの粒状物、5は被
処理水、6は濾過水、7は洗浄流体(水あるいは水及び
空気)、8は洗浄排水を示す、また、(a1図は濾過操
作を実施中の状態、lb1図は濾層を洗浄中の状態、f
c1図は濾層の洗浄が終了した状態を示す、(a)図に
おいて、濾過操作中は粒状物4は濾過器本体2の底部に
貯留されている。(b)図において、濾過器本体2の下
部から洗浄流体7を導入すると、粒状物4は洗浄流体7
の上昇流によって吹き上げられ、濾層3を含む濾過器本
体2内を流動し、洗浄流体7だけが洗浄排水8となって
濾過器本体2上部から排出する。この流動によって粒状
物4が濾層3に充填されている濾材と衝突し、濾層のS
Sが剥離する。剥離したSSは洗浄排水8中に懸濁して
排出する。(C)図において、洗浄流体の導入を中止す
ると、粒状物4は濾過器本体2の底部に沈降し、濾過操
作を開始できる状態となる。この方法においては比較的
沈降速度が大きい粒状物を使用する。なお、洗浄排水8
中には若干の粒状物が混入するので、この粒状物は別途
回収し、流失分相当の粒状物は補給する。
FIG. 1 is a diagram showing a first embodiment of the present invention. In FIG. 1, 1 is a filter equipped with a filter M3 fixed in the filter body 2, and the filter layer 3 has a filter medium with a large porosity as shown in FIGS. 8 to 10. Filled. 4 indicates granular materials such as sand, anthracite, and synthetic resin particles, 5 indicates water to be treated, 6 indicates filtered water, 7 indicates cleaning fluid (water or water and air), and 8 indicates cleaning wastewater. is the state in which the filtration operation is being performed, lb1 is the state in which the filter layer is being washed, f
Figure c1 shows a state in which cleaning of the filter layer has been completed. In Figure (a), particulate matter 4 is stored at the bottom of the filter body 2 during the filtration operation. (b) In the figure, when the cleaning fluid 7 is introduced from the lower part of the filter body 2, the particulate matter 4 is removed by the cleaning fluid 7.
The cleaning fluid 7 is blown up by the upward flow and flows inside the filter body 2 including the filter layer 3, and only the cleaning fluid 7 becomes cleaning waste water 8 and is discharged from the upper part of the filter body 2. Due to this flow, the particulate matter 4 collides with the filter material filled in the filter layer 3, and the S of the filter layer
S peels off. The peeled SS is suspended in cleaning waste water 8 and discharged. In the figure (C), when the introduction of the cleaning fluid is stopped, the particulate matter 4 settles to the bottom of the filter body 2, and the filtering operation can be started. This method uses granules that have a relatively high settling velocity. In addition, cleaning drainage 8
Some particulate matter will be mixed in, so this particulate matter will be collected separately and the particulate matter equivalent to the amount lost will be replenished.

第2図は本発明の第二実施例を示し、第1図の方法に1
工程を付加した方法を示した図である。
FIG. 2 shows a second embodiment of the invention, in which the method of FIG.
FIG. 3 is a diagram showing a method with additional steps.

本実施例の説明においては、第1図で説明済みの部分に
ついては同一の符号を付し説明を省略する。第2図にお
いて、(a)図は濾過操作を実施中の状態、tbt図は
洗浄流体だけで濾層を洗浄中の状態、IC1図は粒状物
を導入して濾層を洗浄中の状態、Ta2図は濾層の洗浄
が終了した状態を示す、第1図の方法に付加された工程
は(b1図の工程である。(b)図において、粒状物4
を濾過器本体2の底部に貯留させたまま、粒状物4の貯
留部より上に位置する濾過器本体2の底部から洗浄流体
(水島るいは水及び空気)7を導入する。洗浄流体7は
粒状物7を流動させることなく、濾層3を洗浄し、剥離
したSSを含む洗浄排水8となって排出する。洗浄の初
期段階における濾層の洗浄は比較的−容易であり1粒状
物導入の効果は洗浄の中間段階あるいは終期段階におい
て顕著に認められる。
In the description of this embodiment, the same reference numerals will be given to the parts already explained in FIG. 1, and the explanation will be omitted. In FIG. 2, (a) is a state in which a filtration operation is being performed, a TBT diagram is a state in which the filter layer is being washed with only cleaning fluid, and an IC1 diagram is a state in which particulate matter is introduced and the filter layer is being washed. Figure Ta2 shows the state in which cleaning of the filter layer has been completed.The process added to the method in Figure 1 is the process in Figure b1.
The cleaning fluid (Mizushima or water and air) 7 is introduced from the bottom of the filter body 2 located above the storage part of the particulate matter 4 while the water is stored at the bottom of the filter body 2. The cleaning fluid 7 cleans the filter layer 3 without causing the particulate matter 7 to flow, and is discharged as a cleaning waste water 8 containing the separated SS. It is relatively easy to wash the filter layer in the early stages of washing, and the effect of introducing a single particulate material is noticeable in the intermediate or final stages of washing.

このため、ある程度までのSSの剥離は洗浄流体だけで
も比較的短時間で行うことができる。このような理由か
ら、上記tb1図の工程が付加されている。この工程を
付加した方法はSSが多量に付着した濾層を洗浄する場
合に適する。
Therefore, SS can be peeled off to a certain extent in a relatively short time using only the cleaning fluid. For this reason, the step shown in Figure tb1 above is added. The method including this step is suitable for cleaning a filter layer to which a large amount of SS has adhered.

第3図は本発明の第三実施例を示し、第2図の方法に更
に2工程を付加し且つ1工程の洗浄流体を変えた方法を
示した図である6本実施例の説明においては、第2図で
説明済みの部分については同一の符号を付し説明を省略
する。第3図において、(a)図は濾過操作を実施中の
状態、tb1図は洗浄流体だけで濾層を洗浄中の状態、
+C1図は粒状物を導入して濾層を洗浄中の状態、td
1図は静置させた状態、telは洗浄流体だけで濾層を
洗浄中の状態、fflは濾層の洗浄が終了した状態を示
す、第2図の方法に付加された工程はfd1図及び[2
1図の工程であり、洗浄流体を変えた工程はfc1図の
工程である。
FIG. 3 shows a third embodiment of the present invention, and is a diagram showing a method in which two more steps are added to the method of FIG. 2 and the cleaning fluid in one step is changed.6 In the description of this embodiment, , the parts already explained in FIG. 2 are designated by the same reference numerals and the explanation thereof will be omitted. In Fig. 3, (a) shows a state in which the filtration operation is being performed, and tb1 shows a state in which the filter layer is being washed with only the washing fluid.
+C1 figure is the state where particulate matter is introduced and the filter layer is being washed, td
Figure 1 shows the state where the filter layer is left standing, tel shows the state where the filter layer is being washed with only cleaning fluid, and ffl shows the state where the filter layer has been washed. [2
This is the process shown in Figure 1, and the process in which the cleaning fluid was changed is the process shown in Figure fc1.

Ic1図において、粒状物4を濾過器本体2の底部に貯
留させたまま、粒状物4の貯留部より上に位置する濾過
器本体2の底部から洗浄流体7として空気だけを導入し
、fb1図の工程でしょできなかったSSを濾層から剥
離する。この場合、導入する洗浄流体7が空気だけであ
るため2SSは濾過器本体2内に滞留する。(d)図に
おいて、洗浄流体の導入を中止して静置し、粒状物4を
濾過器本体2のの底部に沈降させる。この際、濾層3か
ら剥離したSSは浮遊したままの状態である。(e)図
において、洗浄流体7として水だけを導入し、主として
Ic1図の工程で剥離させたSSを洗浄排水8中に懸濁
させて排出する。洗浄流体7は粒状物7を流動させるこ
となく、濾層3を洗浄し、剥離したSSを含む洗浄排水
8となって排出する。洗浄の初期段階における濾層の洗
浄は比較的容易であり1粒状物導入の効果は洗浄の中間
段階あるいは終期段階において顕著に認められる。この
ため、ある程度までのSSの剥離は洗浄流体だけでも比
較的短時間で行うことができる。このよ、うな理由から
、上記+bJ図の工程が付加されている。この工程を付
加した方法はSSが多量に付着した濾層を洗浄する場合
に適する。この方法によれば、粒状物を流動させたまま
の状態で洗浄排水を排出することがないので、粒状物の
流出がなく、その回収及び補給などの操作が不要になる
In Figure Ic1, while the particulate matter 4 is stored at the bottom of the filter body 2, only air is introduced as the cleaning fluid 7 from the bottom of the filter body 2 located above the storage part of the particulate matter 4, and in Figure fb1. The SS that could not be removed in step 2 is peeled off from the filter layer. In this case, since the introduced cleaning fluid 7 is only air, the 2SS remains in the filter body 2. In the figure (d), the introduction of the cleaning fluid is stopped and the filter is allowed to stand still, allowing the particulate matter 4 to settle to the bottom of the filter body 2. At this time, the SS separated from the filter layer 3 remains in a floating state. In the figure (e), only water is introduced as the cleaning fluid 7, and the SS peeled off mainly in the step of Figure Ic1 is suspended in the cleaning waste water 8 and discharged. The cleaning fluid 7 cleans the filter layer 3 without causing the particulate matter 7 to flow, and is discharged as a cleaning waste water 8 containing the separated SS. It is relatively easy to wash the filter layer in the initial stages of washing, and the effect of introducing a single particulate material is noticeable in the intermediate or final stages of washing. Therefore, SS can be peeled off to a certain extent in a relatively short time using only the cleaning fluid. For this reason, the step shown in the +bJ diagram above is added. The method including this step is suitable for cleaning a filter layer to which a large amount of SS has adhered. According to this method, the cleaning waste water is not discharged with the particulate matter still flowing, so there is no outflow of the particulate matter, and operations such as collection and replenishment of the particulate matter are not necessary.

第4図は本発明の第四実施例を示した図である1本実施
例の説明においては、第1図で説明済みの部分について
は同一の符号を付し説明を省略する0本実施例の濾過器
1には粒状物の分離器10、粒状物の貯槽11及び付帯
する流路よりなる粒状物循環手段9が設けられている。
FIG. 4 is a diagram showing a fourth embodiment of the present invention.1 In the explanation of this embodiment, the same reference numerals are given to the parts already explained in FIG. 1, and the explanation will be omitted.0 This embodiment The filter 1 is provided with a particulate material circulation means 9 consisting of a particulate material separator 10, a particulate material storage tank 11, and an accompanying flow path.

(a)図は濾過操作を実施中の状態、fb1図は濾層を
洗浄中の状態、Ic1図は濾層の洗浄が終了した状態を
示す、(a)図において、濾過操作中は粒状物4は粒状
物循環手段9の貯槽11内に蓄えられている。(b)図
において、粒状物循環手段9の弁12を開けて粒状物4
を濾過器本体2に流入させ、これと同時に1過器本体2
の下部から洗浄流体7を導入する6粒状物4は洗浄流体
7とともに4層3を通過し、分離器10に入る0粒状物
4と洗浄流体7、が濾層3を通過する間に、粒状物4が
濾層3に充填されている濾材と衝突し、濾層のSSを剥
離する0分離器10では粒状物4が沈降分離されて貯槽
11に送られ、一方洗浄流体7の水はSSを含んだ洗浄
排水8となって排出する。(C)図において、洗浄終了
時には洗浄流体を流したままの状態で弁12を閉じ、粒
状物4を回収して貯槽11に蓄える。この方法において
は比較的沈降速度が小さい粒状物を使用する。
(a) Figure shows the state in which the filtration operation is being performed, Figure fb1 shows the state in which the filter layer is being washed, and Figure Ic1 shows the state in which the cleaning of the filter layer has been completed. 4 are stored in a storage tank 11 of the particulate circulation means 9. (b) In the figure, the valve 12 of the particulate matter circulation means 9 is opened and the particulate matter 4 is removed.
is caused to flow into the filter body 2, and at the same time, the 1 filter body 2
The particulate matter 4 passes through the four layer 3 together with the cleaning fluid 7 and enters the separator 10 while the particulate matter 4 and the cleaning fluid 7 pass through the filter layer 3. The particulate matter 4 collides with the filter medium filled in the filter layer 3, and the SS of the filter layer is separated.In the separator 10, the particulate matter 4 is sedimented and separated and sent to the storage tank 11, while the water of the cleaning fluid 7 is separated from the SS of the filter layer. is discharged as cleaning wastewater 8 containing In the figure (C), at the end of cleaning, the valve 12 is closed while the cleaning fluid continues to flow, and the particulate matter 4 is collected and stored in the storage tank 11. This method uses granules that have a relatively low settling rate.

第5図は本発明の第五実施例を示し、第4図の方法に1
工程を付加した方法を示した図である。
FIG. 5 shows a fifth embodiment of the present invention, in which the method of FIG.
FIG. 3 is a diagram showing a method with additional steps.

本実施例の説明においては、第4図で説明済みの部分に
ついては同一の符号を付し説明を省略する。第5図にお
いて、fat図は濾過操作を実施中の状態、tb1図は
洗浄流体だけで濾層を洗浄中の状態、+C1図は粒状物
を導入して濾層を洗浄中の状態、td1図は波層の洗浄
が終了した状態を示す、第4図の方法に付加した工程は
lb1図の工程である。
In the description of this embodiment, the same reference numerals are given to the parts already explained in FIG. 4, and the explanation will be omitted. In Figure 5, the fat diagram shows the state in which the filtration operation is being performed, the tb1 diagram shows the state in which the filter layer is being washed with only cleaning fluid, the +C1 diagram shows the state in which the filter layer is being washed by introducing particulate matter, and the td1 diagram 1 shows the state in which the cleaning of the wave layer has been completed. The step added to the method of FIG. 4 is the step of lb1.

lb1図において、粒状物4を貯槽】1に貯留させたま
ま、濾過器本体2の底部から洗浄流体7を導入する。洗
浄流体7は波層3を洗浄し、 i11離したSSを含む
洗浄排水8となって排出する。この方法は第2図及び第
3図の方法と同様にSSが多量に付着した波層を洗浄す
る場合に適する。
In Figure lb1, a cleaning fluid 7 is introduced from the bottom of the filter main body 2 while the granules 4 are stored in the storage tank 1. The cleaning fluid 7 cleans the wave layer 3 and is discharged as a cleaning waste water 8 containing SS separated by i11. This method, like the methods shown in FIGS. 2 and 3, is suitable for cleaning a wave layer to which a large amount of SS has adhered.

次に、本発明の方法により濾過器の洗浄を実施した結果
について説明する。
Next, the results of cleaning a filter using the method of the present invention will be explained.

(実施例) 直径10cIl、高さ2,5mの濾過器に第7図に示し
た濾材を充填した濾過器を作製した。充填した波層の条
件は第2表のごとくにした。この濾過器に5S165〜
200 lIg/ IIを含む生下水を濾過速度120
m/日で24時間連続通水して濾過した。この濾過にお
けるSSの除去率は平均的85%、波層のSS捕捉量は
約19 kg / m”であった。
(Example) A filter having a diameter of 10 cIl and a height of 2.5 m was filled with the filter medium shown in FIG. 7. The conditions for the filled wave layer were as shown in Table 2. 5S165~ for this filter
Filter raw sewage containing 200 lIg/II at a filtration rate of 120
Water was continuously passed for 24 hours at a rate of m/day for filtration. The SS removal rate in this filtration was on average 85%, and the amount of SS trapped in the wave layer was approximately 19 kg/m''.

第2表 波層の条件 第3表 洗浄条件 このSSが付着した波層を第3表に示す条件で洗浄した
。なお、粒状物を濾層中で流動させる洗浄には砂を使用
し、粒状物が波層を通過する洗浄には合成樹脂粒を使用
した。この実験の結果は第6図及び第7図に示す、第6
図及び第7図において、0は粒状物が砂で流層中で流動
させて洗浄した場合、Δは粒状物が合成樹脂粒で波層を
通過させて洗浄した場合、・は粒状物無添加の場合であ
る。
Conditions for the second surface wave layer Table 3 Cleaning conditions The wave layer to which SS was attached was cleaned under the conditions shown in Table 3. Note that sand was used for cleaning in which the granules were made to flow in the filter layer, and synthetic resin particles were used in the cleaning in which the granules passed through the wave layer. The results of this experiment are shown in Figures 6 and 7.
In Figures and Figure 7, 0 indicates when the granules are sand and are washed by flowing in a fluid bed, Δ is when the granules are synthetic resin particles and are washed by passing through a wave layer, and . is when no granules are added. This is the case.

第6図は洗浄流体の流速が40m/時の場合である。第
6図で明らかなように、粒状物を添加した場合には洗浄
時間10分で濾層に付着したSSの99%を剥離して回
収しているのに対し、粒状物無添加の場合には20分経
過しても93%程度を回収しているに過ぎず、波層を静
注にするためには更に長時間を要する状態であった。こ
のように、本発明の方法によれば極めて短時間で波層の
洗浄を行うことができる。また、この実験のように、洗
浄流体を小さな流速で導入しても短時間で洗浄が完了す
る0粒状物を濾層中で流動させて洗浄した場合と、波層
を通過させて洗浄した場合との間に差はなかった。
FIG. 6 shows a case where the flow velocity of the cleaning fluid is 40 m/hour. As is clear from Figure 6, when granules were added, 99% of the SS adhering to the filter layer was peeled off and recovered within 10 minutes of washing, whereas when no granules were added. Even after 20 minutes, only about 93% of the amount was recovered, and it would take a longer time to administer the wave layer intravenously. As described above, according to the method of the present invention, the wave layer can be cleaned in an extremely short time. In addition, as in this experiment, even if the cleaning fluid is introduced at a small flow rate, the cleaning can be completed in a short time.There is a case where 0 particulates are washed by flowing in the filter layer, and a case where it is washed by passing through a wave layer. There was no difference between the two.

第7図は洗浄流体の流速が50m/時の場合である。第
7図においても、本発明の方法と粒状物無添加の方法と
の差は顕著であった0本発明の方法では濾層に付着した
SSの99%を回収までの所要時間は8分間であるのに
対し、粒状物無添加の方法では20分間を要し、洗浄時
間は2倍以上であった。
FIG. 7 shows a case where the flow velocity of the cleaning fluid is 50 m/hour. As shown in Figure 7, the difference between the method of the present invention and the method without the addition of particulate matter was remarkable. In the method of the present invention, the time required to recover 99% of the SS attached to the filter layer was 8 minutes. On the other hand, the method without the addition of particulates required 20 minutes, which was more than double the cleaning time.

[発明の効果] 本発明は、波層が固定された濾過器の洗浄に際し、洗浄
流体ととともに粒状物を導入する方法であり、波層の濾
材に付着したSSの剥離は粒状物の衝突によってなされ
るので、洗浄流体を小さな流速で導入しても、波層の洗
浄は極めて短時間で済み、且つほぼ完全な洗浄ができる
[Effects of the Invention] The present invention is a method in which particulate matter is introduced together with a cleaning fluid when cleaning a filter to which a wave layer is fixed, and the SS attached to the filter medium of the wave layer is peeled off due to the collision of the particulate matter. Therefore, even if the cleaning fluid is introduced at a small flow rate, the wave layer can be cleaned in a very short time and can be almost completely cleaned.

従って、洗浄流体である水や圧縮空気の使用量が節減さ
れて濾過の処理費が低減するとともに、濾過器の稼働率
が向上する。
Therefore, the amount of water and compressed air used as cleaning fluids is reduced, the processing cost for filtration is reduced, and the operating rate of the filter is improved.

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

第1図は本発明の第一実施例を示す図、第2図は本発明
の第二実施例を示す図、第3図は本発明の第三実施例を
示す図、4図は本発明の第四実施例を示す図、5図は本
発明の第五実施例を示す図、第6図及び第7図は本発明
の方法による洗浄実験結果の説明図、第8図〜第10図
は本発明の洗浄方法が適用できる濾過器に充填される濾
材の一部を模式的に示した図である。 1・・・濾過器、2濾過器本体、3・・・濾層、4−・
・・粒状物、5・・・被処理水、6・・・濾過水、8・
・・洗浄排水、9・・・粒状物循環手段、10・・・分
離器、11・・・貯槽、20・・・濾材。
Fig. 1 is a diagram showing a first embodiment of the present invention, Fig. 2 is a diagram showing a second embodiment of the invention, Fig. 3 is a diagram showing a third embodiment of the invention, and Fig. 4 is a diagram showing a third embodiment of the invention. FIG. 5 is a diagram showing a fifth embodiment of the present invention, FIGS. 6 and 7 are explanatory diagrams of the results of a cleaning experiment using the method of the present invention, and FIGS. 8 to 10 1 is a diagram schematically showing a part of a filter medium filled in a filter to which the cleaning method of the present invention can be applied. 1... Filter, 2 Filter body, 3... Filter layer, 4-...
... Granular matter, 5... Water to be treated, 6... Filtered water, 8.
...Washing waste water, 9.. Particulate matter circulation means, 10.. Separator, 11.. Storage tank, 20.. Filter medium.

Claims (3)

【特許請求の範囲】[Claims] (1)濾層を固定した濾過器における濾層の洗浄方法に
おいて、前記濾層に洗浄流体とともに粒状物を導入して
前記濾層を洗浄することを特徴とする濾過器の洗浄方法
(1) A method for cleaning a filter layer in a filter having a fixed filter layer, characterized in that the filter layer is washed by introducing particulate matter into the filter layer together with a cleaning fluid.
(2)請求項1記載の濾過器の洗浄方法において、濾層
に導入した粒状物を濾層中で流動させることを特徴とす
る濾過器の洗浄方法。
(2) The method for cleaning a filter according to claim 1, characterized in that the particulate matter introduced into the filter layer is made to flow in the filter layer.
(3)請求項1記載の濾過器の洗浄方法において、濾層
に導入した粒状物を洗浄流体とともに濾層を通過させて
濾過器本体から排出し、排出した粒状物を回収して前記
濾過器本体内に循環することを特徴とする濾過器の洗浄
方法。
(3) In the method for cleaning a filter according to claim 1, the particulate matter introduced into the filter layer is passed through the filter layer together with the cleaning fluid and discharged from the filter body, and the discharged particulate matter is collected and removed from the filter body. A method for cleaning a filter, characterized by circulating the air within the main body.
JP29187988A 1988-11-18 1988-11-18 How to clean the filter Expired - Lifetime JP2829993B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP29187988A JP2829993B2 (en) 1988-11-18 1988-11-18 How to clean the filter

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29187988A JP2829993B2 (en) 1988-11-18 1988-11-18 How to clean the filter

Publications (2)

Publication Number Publication Date
JPH02139008A true JPH02139008A (en) 1990-05-29
JP2829993B2 JP2829993B2 (en) 1998-12-02

Family

ID=17774624

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Link
JP (1) JP2829993B2 (en)

Also Published As

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JP2829993B2 (en) 1998-12-02

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