JPS6344005B2 - - Google Patents

Info

Publication number
JPS6344005B2
JPS6344005B2 JP58120183A JP12018383A JPS6344005B2 JP S6344005 B2 JPS6344005 B2 JP S6344005B2 JP 58120183 A JP58120183 A JP 58120183A JP 12018383 A JP12018383 A JP 12018383A JP S6344005 B2 JPS6344005 B2 JP S6344005B2
Authority
JP
Japan
Prior art keywords
water
valve
matrix
backwashing
quick
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.)
Expired
Application number
JP58120183A
Other languages
Japanese (ja)
Other versions
JPS6012111A (en
Inventor
Kazuyuki Koyama
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.)
Ebara Corp
Original Assignee
Ebara Infilco Co 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 Ebara Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP58120183A priority Critical patent/JPS6012111A/en
Publication of JPS6012111A publication Critical patent/JPS6012111A/en
Publication of JPS6344005B2 publication Critical patent/JPS6344005B2/ja
Granted legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C1/00Magnetic separation
    • B03C1/02Magnetic separation acting directly on the substance being separated
    • B03C1/025High gradient magnetic separators
    • B03C1/031Component parts; Auxiliary operations
    • B03C1/032Matrix cleaning systems

Landscapes

  • Water Treatment By Electricity Or Magnetism (AREA)

Description

【発明の詳細な説明】 1 発明の技術分野 本発明は、火力・原子力発電所等における高温
高圧水系中のクラツドを除去するための電磁フイ
ルタ、特に強磁性体のスチールウール等をマトリ
ツクスとして充填し、これにより高勾配磁場を発
生させる形式の、いわゆる高勾配電磁フイルタの
逆洗方法及びそのための装置に関するものであ
る。
[Detailed Description of the Invention] 1. Technical Field of the Invention The present invention relates to an electromagnetic filter for removing crud in high-temperature, high-pressure water systems in thermal power plants, nuclear power plants, etc. This invention relates to a method for backwashing a so-called high-gradient electromagnetic filter, which generates a high-gradient magnetic field, and an apparatus therefor.

2 従来技術の説明 一般に電磁フイルタは、マトリツクスとこれを
磁化させる電磁コイルとを備え、流体中の強磁性
体および弱磁性体の懸濁粒子(クラツド)を磁力
により前記マトリツクスで捕捉して分離除去する
過工程を行なうものであるが、過継続により
マトリツクス内にクラツドが堆積してその差圧が
増大するか、あるいは過機能減退により過水
水質が悪化するときは、過を中断してマトリツ
クスの逆洗を行なわなければならない。
2 Description of the Prior Art Generally, an electromagnetic filter includes a matrix and an electromagnetic coil that magnetizes the matrix, and uses magnetic force to capture suspended particles (cruds) of ferromagnetic and weakly magnetic substances in the matrix and separate and remove them. However, if crud accumulates in the matrix and the differential pressure increases due to continued overflow, or if the overwater quality deteriorates due to decreased overfunction, the overflow is interrupted and the matrix is removed. Must be backwashed.

しかしながら、従来逆洗廃液はそのまま直接廃
液処理装置へ送つて処理するようにしているた
め、この廃液処理装置に掛かる負担が大きく、該
処理装置の容量を大きくする必要があり、運転・
維持管理も容易でないなどの問題点があつた。
However, conventionally, backwash waste liquid is sent directly to the waste liquid treatment equipment for treatment, which places a large burden on this waste liquid treatment equipment, requiring a large capacity of the treatment equipment, and increasing operational efficiency.
There were problems such as maintenance and management being difficult.

3 発明の目的 本発明は、上記従来システムの問題点を的確に
解消し、電磁フイルタの逆洗廃液の排出量を大幅
に減少させることができる逆洗方法及びそのため
の装置を提供することを目的とするものである。
3. Purpose of the Invention The purpose of the present invention is to provide a backwashing method and a device therefor, which can accurately solve the problems of the above-mentioned conventional system and significantly reduce the amount of backwash waste liquid discharged from electromagnetic filters. That is.

4 発明の構成 本発明は、高温高圧水を過する電磁コイル、
マトリツクスを備えた高勾配電磁フイルタの逆洗
方法において、逆洗排水中のクラツドをその磁気
凝集の作用により沈降分離し、得られる上澄水を
逆洗水として再利用することを特徴とする電磁フ
イルタの逆洗方法である。
4. Structure of the invention The present invention provides an electromagnetic coil that passes high-temperature and high-pressure water;
A method for backwashing a high-gradient electromagnetic filter equipped with a matrix, in which crud in backwash wastewater is sedimented and separated by the action of magnetic coagulation, and the resulting supernatant water is reused as backwash water. This is a backwashing method.

また本発明は、高温高圧水を過する電磁コイ
ル、マトリツクスを備えた高勾配電磁フイルタの
逆洗装置において、前記マトリツクスの流入側に
急開弁を有するフラツシユ排水路を接続し、この
急開弁の流出側と沈降分離装置を連通せしめると
共に、該沈降分離装置と前記マトリツクスの流入
側をポンプを有する返送路により接続し、さらの
前記マトリツクスの流出側に加圧ガスの供給路を
接続したことを特徴とする電磁フイルタの逆洗装
置である。
The present invention also provides a backwashing device for a high-gradient electromagnetic filter equipped with an electromagnetic coil and a matrix for passing high-temperature, high-pressure water, in which a flush drain having a quick-opening valve is connected to the inflow side of the matrix, and the quick-opening valve is connected to the inflow side of the matrix. The sedimentation separation device is connected to the outflow side of the matrix, and the sedimentation separation device and the inflow side of the matrix are connected by a return path having a pump, and further a pressurized gas supply path is connected to the outflow side of the matrix. This is an electromagnetic filter backwashing device characterized by:

5 実施例の説明 本発明の一実施例を第1図に基づいて説明する
と、電磁フイルタ1内にスチールウールによるマ
トリツクス2が通水隔板3によつて保持され、そ
の流入側及び流出側にそれぞれ空間4及び空間5
が区画形成されている。前記通水隔板3は多孔板
であつてマトリツクス2を保持すると共に通水を
均一に分布する役目をする。また前記マトリツク
ス2の外部には電磁コイル6が取り囲んで配備さ
れていて、この電磁コイル6に直流が流れるとマ
トリツクス2が磁化され、さらにスチールウール
の尖鋭部分には磁力が収束して高勾配が発生する
ように構成されている。
5 Description of Embodiments An embodiment of the present invention will be described based on FIG. space 4 and space 5 respectively
are divided into sections. The water flow partition plate 3 is a perforated plate that holds the matrix 2 and serves to uniformly distribute water flow. Further, an electromagnetic coil 6 is arranged outside the matrix 2 to surround it, and when a direct current flows through the electromagnetic coil 6, the matrix 2 is magnetized, and the magnetic force is concentrated on the sharp portion of the steel wool, creating a high gradient. configured to occur.

前記マトリツクス2の流入側の空間4には流入
弁7を備えた原水Aの流入路8が、流出側の空間
5には流出弁9を備えた過水Bの流出路10が
それぞれ接続され、さらに流入路8と流出路10
はバイパス弁11を有するバイパス路12により
直接連結されている。
An inflow path 8 for raw water A equipped with an inflow valve 7 is connected to the space 4 on the inflow side of the matrix 2, and an outflow path 10 for excess water B equipped with an outflow valve 9 is connected to the space 5 on the outflow side. Furthermore, an inlet passage 8 and an outlet passage 10
are directly connected by a bypass passage 12 having a bypass valve 11.

一方、前記流入路8には急開弁13を設けたフ
ラツシユ排水路14が分岐してあり、その端部は
フラツシユタンクを兼ねた沈降分離槽15が接続
されている。
On the other hand, a flash drain channel 14 having a quick-open valve 13 branches off from the inflow channel 8, and the end thereof is connected to a sedimentation separation tank 15 which also serves as a flash tank.

この沈降分離槽15は底部が逆円錐状の密閉可
能な円筒状容器であつて、頂部に排気弁16を有
する排気路17、側壁に複数の流出弁18a〜1
8dを上下方向多段に分岐配備した上澄水Eの流
出路19及び底部に排出弁20を設けた沈降クラ
ツド水Dの排出路21がそれぞれ接続されてい
る。さらに、沈降分離槽15の中央部上方には多
孔管等で構成したデイストリビユータ15a、こ
れを包囲するように円筒状の衝突板15bがそれ
ぞれ固定配備され、この衝突板15bの直上には
飛沫同伴を防止するための邪魔板15cが配設さ
れている。そして、前記流出路19は貯留槽22
に連結され、該貯留槽22の底部はポンプ23及
び返送弁24を介在配備した返送路25により前
記電磁フイルタ1の空間4に連通されている。な
お、前記排出路21は廃液処理装置(図示せず)
に接続されている。
This sedimentation separation tank 15 is a sealable cylindrical container with an inverted conical bottom, an exhaust passage 17 having an exhaust valve 16 at the top, and a plurality of outflow valves 18a to 18 on the side wall.
8d is connected to an outflow path 19 for supernatant water E which is branched in multiple stages in the vertical direction, and an outflow path 21 for sedimented cladding water D which is provided with a discharge valve 20 at the bottom. Furthermore, above the central part of the sedimentation separation tank 15, a distributor 15a composed of a perforated tube, etc., and a cylindrical collision plate 15b are fixedly arranged to surround this, and directly above the collision plate 15b are A baffle plate 15c is provided to prevent entrainment. The outflow path 19 is connected to the storage tank 22.
The bottom of the storage tank 22 is connected to the space 4 of the electromagnetic filter 1 through a return path 25 in which a pump 23 and a return valve 24 are interposed. Note that the discharge path 21 is a waste liquid treatment device (not shown).
It is connected to the.

さらに、電磁フイルタ1の空間5には脱気弁2
6を備えた脱気路27及び加圧ガスCの供給弁2
8を有する供給路29が接続され、脱気路27の
端部は前記沈降分離槽15の頂部近傍に接続され
ている。
Furthermore, a degassing valve 2 is provided in the space 5 of the electromagnetic filter 1.
6 and a supply valve 2 for pressurized gas C.
8 is connected thereto, and the end of the deaeration path 27 is connected to the vicinity of the top of the settling tank 15.

次に、第2図は本発明の別の実施例を示してい
るが、この場合、フラツシユ排水路14の端部は
フラツシユタンク31に接続され、このフラツシ
ユタンク31内の廃液が沈降分離槽15′で処理
されたのち上澄水Eが貯留槽22に流入するよう
に構成されている。
Next, FIG. 2 shows another embodiment of the present invention, in which the end of the flush drainage channel 14 is connected to a flush tank 31, and the waste liquid in this flush tank 31 is separated by sedimentation. The supernatant water E is configured to flow into the storage tank 22 after being treated in the tank 15'.

すなわち、前記フラツシユタンク31は頂部に
排気弁16′を有する排気路17′、側壁中間部に
排出弁32を有するフラツシユ排水の排出路33
がそれぞれ接続され、該排出路33の端部は沈降
分離槽15′の上部に開口配備されている。また
フラツシユタンク31の底部にも排出弁32′を
有する排出路33′、及び排出弁34を有する排
出路35が接続され、排出路33′は排出路33
に合流し、排出路35は廃液処理装置(図示せ
ず)に接続されている。
That is, the flush tank 31 has an exhaust passage 17' having an exhaust valve 16' at the top, and an exhaust passage 33 for flush drainage having an exhaust valve 32 at the middle part of the side wall.
are connected to each other, and the ends of the discharge passages 33 are opened at the upper part of the settling tank 15'. Further, a discharge passage 33' having a discharge valve 32' and a discharge passage 35 having a discharge valve 34 are connected to the bottom of the flush tank 31.
The discharge path 35 is connected to a waste liquid treatment device (not shown).

さらに前記貯留槽22には給水Fの供給路36
が接続され、その底部はポンプ23ならびに返送
路37,25及び38を介してそれぞれフラツシ
ユタンク31の下部、電磁フイルタ1の空間4及
び原水貯留槽39に連通されている。なお、第2
図中40,41,42及び43は返送弁、44は
電磁フイルタ1内に保有される水を原水貯留槽3
9へ返送するためのポンプであり、45は多孔管
等で構成されたデイストリビユータである。
Further, the storage tank 22 has a supply path 36 for water supply F.
are connected, and the bottom thereof communicates with the lower part of the flush tank 31, the space 4 of the electromagnetic filter 1, and the raw water storage tank 39 via the pump 23 and return passages 37, 25, and 38, respectively. In addition, the second
In the figure, 40, 41, 42, and 43 are return valves, and 44 is a raw water storage tank 3 for water held in the electromagnetic filter 1.
9, and 45 is a distributor made of a perforated pipe or the like.

前記沈降分離槽15′はコンクリート製の円形
沈殿池であつて、その水面上方及び溢流樋15″
にはそれぞれ15d、15eが設けられ、塵埃の
混入を防止できるようになつている。なお、槽内
水面付近にセンタウエルを、槽底部に沈降クラツ
ド水の掻寄機をさらに水面下に傾斜板による沈降
促進部材を浸漬配備すれば、沈降分離をより効果
的に行なうことができる。
The sedimentation separation tank 15' is a circular sedimentation tank made of concrete, and the area above the water surface and the overflow gutter 15''
are provided with 15d and 15e, respectively, to prevent dust from entering. Sedimentation separation can be carried out more effectively by providing a centawell near the water surface in the tank, a scraper for the sedimented crud water at the bottom of the tank, and a sedimentation promotion member with an inclined plate submerged below the water surface.

しかして、第1図例において電磁フイルタ1に
よる過工程は、流入弁7及び流出弁9を開き、
急開弁13及びバイパス弁11を閉めて行なわ
れ、かつ電磁コイル6は通電されている。すなわ
ち、処理するべき原水A(高温高圧水)は流入弁
7を経て電磁フイルタ1の空間4に入り、次いで
マトリツクス2を通過する間にクラツドが除去さ
れ、過水Bは空間5から流出弁9を経て系に戻
る。
Therefore, in the example shown in FIG. 1, the overflow by the electromagnetic filter 1 opens the inflow valve 7 and the outflow valve 9,
The quick opening valve 13 and the bypass valve 11 are closed, and the electromagnetic coil 6 is energized. That is, raw water A (high-temperature, high-pressure water) to be treated enters the space 4 of the electromagnetic filter 1 through the inlet valve 7, and then the crud is removed while passing through the matrix 2, and the excess water B passes from the space 5 to the outflow valve 9. Return to the system via .

この過工程の継続によりマトリツクス2内に
クラツドが堆積してその差圧が増大するか或いは
過機能減退により過水水質が悪化するので、
これらを検出して過を中断して逆洗工程に移
る。
As this over-processing continues, crud will accumulate in the matrix 2 and the differential pressure will increase, or over-water quality will deteriorate due to over-functioning.
When these are detected, the filtration is interrupted and the process moves on to the backwashing process.

この逆洗工程に入るときは、まずバイパス弁1
1を開き流出弁9を閉め、ついで流入弁7を閉め
て電磁コイル6の通電を停止する。これにより高
温高圧水はバイパス路12からバイパスされると
共に、電磁フイルタ1内部には高温高圧水がその
まま保留される。
When entering this backwashing process, first bypass valve 1
1 is opened, the outflow valve 9 is closed, and then the inflow valve 7 is closed to stop the energization of the electromagnetic coil 6. As a result, the high-temperature, high-pressure water is bypassed from the bypass path 12, and the high-temperature, high-pressure water is retained inside the electromagnetic filter 1 as it is.

一方、沈降分離槽15については排気弁16を
開き、予め流出弁18aのみを開くことにより槽
内水位をデイストリビユータ15aが水没する高
さにしておく。
On the other hand, regarding the sedimentation separation tank 15, the exhaust valve 16 is opened and only the outflow valve 18a is opened in advance, so that the water level in the tank is set to a level at which the distributor 15a is submerged.

かかる状態でフラツシユ排水路14に設けた急
開弁13を急激に開くと、電磁フイルタ1内の高
温高圧水は急激な減圧によりその一部が蒸発して
体積が膨張するので、空間5内の水がマトリツク
ス2内を急激に流下し、その剪断力によりスチー
ルウールに付着していたクラツドは剥離除去され
る。この場合、フラツシユ排水はデイストリビユ
ータ15aから沈降分離槽15内に貯留されてい
る水中に放散されて混合し、フラツシユ排水中の
水蒸気も凝縮し、全量が沈降分離槽15に受け入
れられる。
When the quick-opening valve 13 provided in the flash drain 14 is suddenly opened in such a state, the high-temperature, high-pressure water in the electromagnetic filter 1 will be partially evaporated due to the sudden pressure reduction and its volume will expand. Water rapidly flows down inside the matrix 2, and the shearing force of the water causes the crud adhering to the steel wool to be peeled off and removed. In this case, the flash wastewater is dispersed from the distributor 15a into the water stored in the sedimentation separation tank 15 and mixed, the water vapor in the flash drainage is also condensed, and the entire amount is received in the sedimentation separation tank 15.

しかしながら、一般に上記1回の操作では逆洗
効果は充分とはなり難いので、以下の要領で沈降
分離槽15による上澄水を逆洗水として使用しさ
らに複数回の逆洗操作を行なう。
However, in general, the backwashing effect is not sufficient with the above-mentioned one operation, so the supernatant water from the sedimentation separation tank 15 is used as backwash water and the backwash operation is performed multiple times in the following manner.

すなわち、再び電磁コイル6を励磁してからポ
ンプ23を作動し、返送弁24を開いて貯留槽2
2に貯留されたほぼ常温の上澄水を電磁フイルタ
1に返送して過水を所定量空間5内に貯める。
次いで電磁コイル6を消磁し供給弁28を開けて
加圧空気、加圧窒素などの加圧ガスCを空間5の
上方に供給して所定圧力に加圧する。しかるのち
急開弁13を急激に開けば、前記過水は一気に
マトリツクス2内を通過し、クラツドの除去が行
なわれる。
That is, after energizing the electromagnetic coil 6 again, the pump 23 is operated, and the return valve 24 is opened to drain the storage tank 2.
The supernatant water at approximately room temperature stored in 2 is returned to the electromagnetic filter 1, and excess water is stored in a predetermined amount of space 5.
Next, the electromagnetic coil 6 is demagnetized, the supply valve 28 is opened, and a pressurized gas C such as pressurized air or pressurized nitrogen is supplied above the space 5 to pressurize it to a predetermined pressure. Then, when the quick-opening valve 13 is suddenly opened, the excess water passes through the matrix 2 at once, and the crud is removed.

このようにして上澄水の過水による逆洗操作
を2〜5回繰り返したのち、逆洗工程終了時には
排気弁16を開放したまま電磁フイルタ1による
上澄水の過水を空間5及び第1図太い実線で示
す、脱気路27を含む流路に充満させて脱気す
る。この場合、流出弁9と供給弁28を接続する
流路内の気体は、これらの弁に近接して設けたコ
ツクを開放することにより脱気できる。脱気路2
7内の気体は排気弁17から排気できるが、脱気
終了は脱気路27の端部に設けたコツクを開放す
ることにより確認することができる。かくて正規
の過工程に戻ることになるが、上記のように脱
気操作を行なつているので、過水中に空気等が
混入する心配はない。
After repeating the backwashing operation by supernatant water in this manner 2 to 5 times, at the end of the backwashing process, the supernatant water is supernatant in the space 5 and into the space 5 with the electromagnetic filter 1 open while the exhaust valve 16 is left open. The flow path including the deaeration path 27, shown by the solid line, is filled and degassed. In this case, the gas in the flow path connecting the outflow valve 9 and the supply valve 28 can be degassed by opening a socket provided close to these valves. Deaeration path 2
The gas in the chamber 7 can be exhausted from the exhaust valve 17, and the completion of the exhaust can be confirmed by opening the stop provided at the end of the exhaust passage 27. In this way, the process returns to the regular overflow process, but since the deaeration operation is performed as described above, there is no fear that air or the like will get mixed into the overwater.

このようにして沈降分離槽15には初めに高温
の逆洗排水、次いでほぼ常温の逆洗排水が流入す
るわけであるが、逆洗排水が高温であつてもこれ
が沈降分離槽15内の水と混合するので極めて効
果的に短時間で冷却され、したがつて槽壁に熱応
力が生ずる心配はない。なお、前記2回目以降の
逆洗排水はほぼ常温になつているから上記熱応力
の問題がないことは勿論である。
In this way, high-temperature backwash wastewater first flows into the sedimentation separation tank 15, and then backwash wastewater at approximately room temperature flows, but even if the backwash wastewater is at a high temperature, the water in the sedimentation separation tank 15 Since the water is mixed with the water, it is very effectively cooled in a short time, and there is no fear of thermal stress occurring on the tank walls. Incidentally, since the backwashing water from the second and subsequent times is at approximately room temperature, it goes without saying that there is no problem of the above-mentioned thermal stress.

沈降分離槽15内にはデイストリビユータ15
aを包囲する衝突板15bが設けてあるので、た
とえデイストリビユータ15aが水面上にあつて
も高温の逆洗排水が直接槽壁に向かつて噴出され
ることがないし、槽内の水が撹乱されてクラツド
の沈降分離を妨げるようなトラブルも防止でき、
さらに、流入する逆洗排水が槽内に均等にほぼ放
射状に分配される効果も得られる(デイストリビ
ユータ15aによつても、このような分配作用が
生ずる)。
A distributor 15 is installed in the sedimentation separation tank 15.
Since the collision plate 15b surrounding the distributor 15a is provided, even if the distributor 15a is above the water surface, high-temperature backwash wastewater will not be ejected directly toward the tank wall, and the water in the tank will not be disturbed. It also prevents troubles that would interfere with sedimentation and separation of the crud.
Furthermore, an effect can be obtained in which the inflowing backwash wastewater is evenly distributed almost radially within the tank (this distribution effect also occurs due to the distributor 15a).

しかして、沈降分離槽15内の逆洗排水は適宜
時間静置される間に、該排水中のクラツドは、磁
気を帯びているため自然に凝集すると共にこの凝
集物により凝集作用が促進される結果、効果的に
クラツドの沈降分離が行なわれ、沈降クラツド水
Dは槽底部に沈殿する。
Therefore, while the backwash wastewater in the sedimentation separation tank 15 is allowed to stand still for a suitable period of time, the crud in the wastewater naturally aggregates because it is magnetic, and the flocculation action is promoted by the aggregates. As a result, the sedimentation and separation of the crud is effectively carried out, and the sedimented crud water D settles at the bottom of the tank.

かくて得られた上澄水Eは流出弁18a〜18
dのうち適宜のものを開け、沈殿したクラツドが
混入しないように静かに溢流させ、貯留槽22に
貯留する一方、沈降クラツド水Dは排出路21を
介して前記廃液処理装置に移送する。
The supernatant water E thus obtained flows through the outflow valves 18a to 18.
d is opened, the water is allowed to overflow gently so that the precipitated crud does not get mixed in, and is stored in the storage tank 22, while the precipitated crud water D is transferred to the waste liquid treatment device via the discharge path 21.

次に、第2図例においては、過工程は第1図
例と全く同じ要領で行なわれるが逆洗工程は次の
ようにして実施される。
Next, in the example shown in FIG. 2, the overflow process is carried out in exactly the same manner as in the example shown in FIG. 1, but the backwashing process is carried out as follows.

すなわち、予めフラツシユタンク31内のデイ
ストリビユータ45が水没していることを確認す
る(水没していない場合は、貯留槽22内の上澄
水を供給する)。次いで第1図例と同じ要領でま
ず原水Aの過水により逆洗を行なつたのち、貯
留槽22の貯留水の過水により複数回逆洗す
る。逆洗工程が終了したら排出弁23を開けてフ
ラツシユタンク31内の排水を沈降分離槽15′
に排水しクラツドを沈降分離する。したがつて、
デイストリビユータ45は通常は通常水面下にあ
るが、所望により、排出弁32′を開けてフラツ
シユタンク31内排水の全量を沈降分離槽15′
へ抜き出してもよく、排出弁34を開けてフラツ
シユタンク31の底部の排水のみを直接廃液処理
装置へ移送してもよい。
That is, it is confirmed in advance that the distributor 45 in the flash tank 31 is submerged in water (if not submerged in water, the supernatant water in the storage tank 22 is supplied). Next, in the same manner as in the example shown in FIG. 1, backwashing is first performed by overflowing the raw water A, and then backwashing is performed multiple times using overflowing water stored in the storage tank 22. When the backwashing process is completed, the discharge valve 23 is opened and the waste water in the flash tank 31 is drained into the sedimentation separation tank 15'.
Drain the water and separate the crud by sedimentation. Therefore,
The distributor 45 is normally located below the water surface, but if desired, the discharge valve 32' may be opened to drain the entire amount of waste water from the flash tank 31 to the sedimentation separation tank 15'.
Alternatively, the discharge valve 34 may be opened and only the waste water at the bottom of the flash tank 31 may be directly transferred to the waste liquid treatment device.

なお、この実施例では原水Aを電磁フイルタ系
外へ排出したくない場合、あるいは貯留槽22内
の上澄水量が逆洗に必要な量を超えた場合などに
は、該上澄水の一部又は電磁フイルタ1内の原
水、過水をポンプ23と44により又はポンプ
44によりそれぞれ原水貯留槽39へ返送するこ
ともできる。
In this embodiment, if it is not desired to discharge the raw water A out of the electromagnetic filter system, or if the amount of supernatant water in the storage tank 22 exceeds the amount required for backwashing, a portion of the supernatant water is Alternatively, the raw water and excess water in the electromagnetic filter 1 can be returned to the raw water storage tank 39 by the pumps 23 and 44 or by the pump 44, respectively.

6 発明の作用ならびに効果 以上述べたように本発明により、電磁フイルタ
の逆洗廃液の系外への排出量が大幅に減少でき、
したがつて逆洗廃液処理装置の容量が小さなもの
ですむうえ、逆洗用に返送して再利用する上澄水
の温度はほぼ常温となつているので逆洗工程をよ
り安全かつ簡便に実施することができ、クラツド
の沈降分離はクラツドが帯びている磁気による凝
集作用に基づいて行なわれるため凝集剤を添加す
る必要がなく、沈降分離装置の構造も簡単に維持
管理も簡便に行なえるなど多大の効果をもたらす
ものである。
6. Functions and Effects of the Invention As described above, according to the present invention, the amount of electromagnetic filter backwash waste liquid discharged to the outside of the system can be significantly reduced.
Therefore, the capacity of the backwash waste liquid processing equipment can be small, and the temperature of the supernatant water returned and reused for backwashing is almost room temperature, making the backwashing process safer and easier. Sedimentation separation of crud is carried out based on the flocculating effect of the crud's magnetism, so there is no need to add a flocculant, and the sedimentation separation equipment has a simple structure and is easy to maintain. It brings about the effect of

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

第1図は本発明装置の一実施例のフローシー
ト、第2図は別の実施例のフローシートである。 A……原水、B……過水、C……加圧ガス、
D……沈降クラツド水、E……上澄水、F……給
水、1……電磁フイルタ、2……マトリツクス、
3……通水隔板、4,5……空間、6……電磁コ
イル、7……流入弁、8……流入路、9,18a
〜18d……流出弁、10,19……流出路、1
1……バイパス弁、12……バイパス路、13…
…急開弁、14……フラツシユ排水路、15,1
5′……沈降分離槽、15″……溢流樋、15a,
45……デイストリビユータ、15b……衝突
板、15c……邪魔板、15d,15e……蓋
板、16,16′……排気弁、17,17′……排
気路、20,32,32′,34……排出弁、2
1,33,33′,35……排出路、22……貯
留槽、23,44……ポンプ、24,40〜43
……返送弁、25,37,38……返送路、26
……脱気弁、27……脱気路、28……供給弁、
29……ガス供給路、31……フラツシユタン
ク、36……供給路、39……原水貯留槽。
FIG. 1 is a flow sheet of one embodiment of the apparatus of the present invention, and FIG. 2 is a flow sheet of another embodiment. A... Raw water, B... Overwater, C... Pressurized gas,
D...Sedimented cladding water, E...Supernatant water, F...Water supply, 1...Electromagnetic filter, 2...Matrix,
3... Water flow partition plate, 4, 5... Space, 6... Electromagnetic coil, 7... Inflow valve, 8... Inflow path, 9, 18a
~18d... Outflow valve, 10, 19... Outflow path, 1
1... Bypass valve, 12... Bypass path, 13...
...Quick opening valve, 14...Flats drain, 15,1
5'... Sedimentation separation tank, 15''... Overflow gutter, 15a,
45... Distributor, 15b... Collision plate, 15c... Baffle plate, 15d, 15e... Lid plate, 16, 16'... Exhaust valve, 17, 17'... Exhaust path, 20, 32, 32 ', 34...Discharge valve, 2
1, 33, 33', 35...Discharge path, 22...Storage tank, 23, 44...Pump, 24, 40-43
... Return valve, 25, 37, 38 ... Return path, 26
... Degassing valve, 27... Degassing path, 28... Supply valve,
29... Gas supply path, 31... Flash tank, 36... Supply path, 39... Raw water storage tank.

Claims (1)

【特許請求の範囲】 1 高温高圧水を過する電磁コイル、マトリツ
クスを備えた高勾配電磁フイルタの逆洗方法にお
いて、逆洗排水中のクラツドをその磁気凝集の作
用により沈降分離し、得られる上澄水を逆洗水と
して再利用することを特徴とする電磁フイルタの
逆洗方法。 2 高温高圧水を過する電磁コイル、マトリツ
クスを備えた高勾配電磁フイルタの逆洗装置にお
いて、前記マトリツクスの流入側に急開弁を有す
るフラツシユ排水路を接続し、この急開弁の流出
側と沈降分離装置を連通せしめると共に、該沈降
分離装置と前記マトリツクスの流入側をポンプを
有する返送路により接続し、さらに前記マトリツ
クスの流出側に加圧ガスの供給路を接続したこと
を特徴とする電磁フイルタの逆洗装置。 3 前記返送路に設けた前記ポンプの吸込側に、
前記沈降分離装置による上澄水の貯留槽を配備し
た特許請求の範囲第2項記載の逆洗装置。 4 前記沈降分離装置が、前記急開弁の流出側と
直接的に連通された逆円錐状の底部を有する密閉
可能な円筒状の容器であつて頂部に排気弁、側壁
に上澄水流出弁、底部に沈降クラツド水の排出
弁、ならびに内部に、流入するフラツシユ排水の
分配噴出部材及び衝突部材をそれぞれ備えたもの
である特許請求の範囲第3項記載の逆洗装置。 5 前記沈降分離装置が前記急開弁の流出側と間
接的に連通された、水面上方に蓋板を備えたコン
クリート製の円形沈殿池があり、該円形沈殿池と
前記急開弁の間に、頂部に排気弁、内部に前記急
開弁と連通するフラツシユ排水の分配噴出部材を
それぞれ備えた密閉可能なフラツシユタンクが介
在配備されている特許請求の範囲第3項記載の逆
洗装置。 6 前記マトリツクスの流出側と前記沈降分離装
置の上方部を、弁を有する脱気路により接続した
特許請求の範囲第4項記載の逆洗装置。 7 前記マトリツクスの流出側と前記フラツシユ
タンクの上方部を、弁を有する脱気路により接続
した特許請求の範囲第5項記載の逆洗装置。 8 前記マトリツクスの流入側と過するべき高
温高圧水の貯留装置を、ポンプを有する管路によ
り接続し、電磁フイルタ内の水を前記貯留装置へ
返送できるようにした特許請求の範囲第6項又は
第7項記載の逆洗装置。
[Claims] 1. In a method for backwashing a high-gradient electromagnetic filter equipped with an electromagnetic coil and matrix that passes high-temperature, high-pressure water, the crud in the backwash wastewater is sedimented and separated by the action of its magnetic coagulation. A method for backwashing an electromagnetic filter characterized by reusing clear water as backwash water. 2. In a backwashing device for a high-gradient electromagnetic filter equipped with an electromagnetic coil and a matrix that passes high-temperature, high-pressure water, a flush drain having a quick-opening valve is connected to the inflow side of the matrix, and the outlet side of the quick-opening valve and An electromagnetic device characterized in that a sedimentation separation device is communicated with the sedimentation separation device, and the sedimentation separation device and the inflow side of the matrix are connected by a return path having a pump, and further a pressurized gas supply path is connected to the outflow side of the matrix. Filter backwashing device. 3 On the suction side of the pump provided in the return path,
The backwashing device according to claim 2, further comprising a storage tank for supernatant water produced by the sedimentation separation device. 4. The sedimentation separation device is a sealable cylindrical container having an inverted conical bottom directly communicating with the outflow side of the quick-opening valve, an exhaust valve at the top, and a supernatant water outflow valve at the side wall; 4. The backwashing device according to claim 3, further comprising a discharge valve for sedimented clutter water at the bottom, and a distribution spouting member and a collision member for inflowing flush wastewater inside. 5. There is a circular sedimentation basin made of concrete with a cover plate above the water surface, in which the sedimentation separator is indirectly connected to the outflow side of the quick-opening valve, and between the circular settling basin and the quick-opening valve, there is a 4. The backwashing device according to claim 3, further comprising a sealable flush tank having an exhaust valve at the top thereof and a flush water distribution/spouting member inside thereof communicating with the quick-opening valve. 6. The backwashing device according to claim 4, wherein the outflow side of the matrix and the upper part of the sedimentation separation device are connected by a degassing path having a valve. 7. The backwashing device according to claim 5, wherein the outflow side of the matrix and the upper part of the flash tank are connected by a degassing path having a valve. 8. Claim 6 or 8, wherein the inflow side of the matrix and a storage device for high-temperature, high-pressure water to be passed through are connected by a pipe line having a pump, so that the water in the electromagnetic filter can be returned to the storage device. The backwashing device according to item 7.
JP58120183A 1983-07-04 1983-07-04 Method and apparatus for backwashing electromagnetic filter Granted JPS6012111A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58120183A JPS6012111A (en) 1983-07-04 1983-07-04 Method and apparatus for backwashing electromagnetic filter

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58120183A JPS6012111A (en) 1983-07-04 1983-07-04 Method and apparatus for backwashing electromagnetic filter

Publications (2)

Publication Number Publication Date
JPS6012111A JPS6012111A (en) 1985-01-22
JPS6344005B2 true JPS6344005B2 (en) 1988-09-02

Family

ID=14779963

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58120183A Granted JPS6012111A (en) 1983-07-04 1983-07-04 Method and apparatus for backwashing electromagnetic filter

Country Status (1)

Country Link
JP (1) JPS6012111A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62273020A (en) * 1986-05-20 1987-11-27 Kawasaki Steel Corp Method for backwashing electromagnetic filter
JP2005334719A (en) * 2004-05-25 2005-12-08 Shoei:Kk REMOTE DATA MANAGEMENT SYSTEM, REMOTE DATA MANAGEMENT METHOD, REMOTE DATA MANAGEMENT PROGRAM, AND COMPUTER-READABLE RECORDING MEDIUM CONTAINING THE PROGRAM
CN109343494A (en) * 2018-11-12 2019-02-15 中冶京诚工程技术有限公司 Magnetic flocculation water purification monitoring system and method based on Internet of Things

Also Published As

Publication number Publication date
JPS6012111A (en) 1985-01-22

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