JPH0957147A - Method and apparatus for flocculating fine substance - Google Patents

Method and apparatus for flocculating fine substance

Info

Publication number
JPH0957147A
JPH0957147A JP7213865A JP21386595A JPH0957147A JP H0957147 A JPH0957147 A JP H0957147A JP 7213865 A JP7213865 A JP 7213865A JP 21386595 A JP21386595 A JP 21386595A JP H0957147 A JPH0957147 A JP H0957147A
Authority
JP
Japan
Prior art keywords
water
fine particle
aggregating
substance
magnetic force
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
JP7213865A
Other languages
Japanese (ja)
Other versions
JP2738522B2 (en
Inventor
Sachiko Hayashi
幸子 林
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 JP7213865A priority Critical patent/JP2738522B2/en
Publication of JPH0957147A publication Critical patent/JPH0957147A/en
Application granted granted Critical
Publication of JP2738522B2 publication Critical patent/JP2738522B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To flocculate a fine substance in water without adding a flocculant. SOLUTION: Columnar magnetic elements 3 are arranged in the cylindrical member 1 provided on the way of piping permitting water containing a fine substance to flow and water is allowed to flow through the annular passages 4 formed between the magnetic elements 3 and the inner wall surface 1a of the cylindrical member 1.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、廃水、地下水、河
川水、湖沼水、海水、槽内水などの水の中に含まれてい
る微粒物質の凝集方法および凝集装置に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a flocculation method and a flocculation device for fine particles contained in water such as waste water, ground water, river water, lake water, sea water, and in-tank water.

【0002】[0002]

【従来の技術】廃水、地下水、河川水、湖沼水、海水、
槽内水などの水に含まれている微粒物質、例えば懸濁物
質を除去する場合、従来、プレコート濾過若しくはサブ
ミクロンの目開きを有するセラミック製フィルターまた
は中空糸膜フィルターにより濾過を行うか、または凝集
剤を添加して懸濁物質の粒径を大きくして沈降分離を行
うか若しくは浮上分離が行われていた。
2. Description of the Related Art Wastewater, groundwater, river water, lake water, seawater,
In the case of removing fine particles contained in water such as water in a tank, for example, suspended matter, conventionally, filtration is performed by a precoat filtration or a ceramic filter or a hollow fiber membrane filter having a submicron opening, or A flocculant was added to increase the particle size of the suspended substance for sedimentation separation or floating separation.

【0003】[0003]

【発明が解決しようとする課題】しかし、上述した濾過
方法によると、例えばプレコート濾過による場合には、
プレコート材がその都度破棄されるため、廃棄物が多く
なるという問題がある。また、中空糸膜フィルターの場
合には、透過流速を大きくすることができないため、ど
うしても所定の透過流量を確保しようとすると、装置を
大きくする必要があり、したがって設備が高価になると
いう問題がある。さらに、凝集剤を添加する場合には、
凝集剤の添加装置および沈降分離または浮上分離を行う
ための装置が必要となり、したがってやはり設備全体が
高価になるとともに、凝集剤がすべて懸濁物質として排
出されるため、廃棄物が増加するという問題もあった。
However, according to the above-mentioned filtration method, for example, in the case of precoat filtration,
Since the precoat material is discarded each time, there is a problem that the amount of waste increases. Further, in the case of the hollow fiber membrane filter, since the permeation flow velocity cannot be increased, there is a problem that the device needs to be large in size in order to ensure a predetermined permeation flow rate, and therefore the equipment becomes expensive. . Furthermore, when adding a coagulant,
The problem is that a coagulant addition device and a device for performing sedimentation or flotation are required, so that the entire equipment is also expensive, and the coagulant is discharged as suspended matter, resulting in increased waste. There was also.

【0004】そこで、本発明は、凝集剤などを添加する
ことなく微粒物質の凝集を行い得る凝集方法およびその
装置を提供することを目的とする。
Therefore, it is an object of the present invention to provide an aggregating method and apparatus capable of aggregating fine particles without adding an aggregating agent or the like.

【0005】[0005]

【課題を解決するための手段】上記課題を解決するた
め、本発明の微粒物質の凝集方法は、微粒物質を含む水
に磁気力を作用させて微粒物質を凝集させる方法であ
る。
In order to solve the above-mentioned problems, the method of aggregating a fine particle substance of the present invention is a method of causing a magnetic force to act on water containing the fine particle substance to agglomerate the fine particle substance.

【0006】また、上記の凝集方法において、水の流速
を1〜3m/sの範囲内とし、また磁石体の磁気力(磁
束密度)を1000〜10000ガウスの範囲内とし、
さらに水に電解物質または電解物質を含む液体を添加す
るようにする方法である。
In the above coagulation method, the flow velocity of water is within the range of 1 to 3 m / s, and the magnetic force (magnetic flux density) of the magnet body is within the range of 1000 to 10000 gauss.
Further, it is a method of adding an electrolytic substance or a liquid containing an electrolytic substance to water.

【0007】また、本発明の微粒物質の凝集装置は、微
粒物質を含む水を流す流路の途中に介装される筒状体の
内部に、円柱状の磁石体を配置したものである。さら
に、上記の凝集装置において、筒状体内を流れる水の流
速を1〜3m/sの範囲内となるようにし、また磁石体
の磁気力(磁束密度)を1000〜10000ガウスの
範囲内としたものである。
Further, the apparatus for aggregating fine particles of the present invention is one in which a cylindrical magnet body is arranged inside a cylindrical body which is interposed in the middle of a flow path for flowing water containing the fine particles. Further, in the above-mentioned aggregating apparatus, the flow velocity of water flowing in the tubular body is set within the range of 1 to 3 m / s, and the magnetic force (magnetic flux density) of the magnet body is set within the range of 1000 to 10000 gauss. It is a thing.

【0008】上記の各構成によると、微粒物質を含む水
に、磁気力を作用させて微粒物質を凝集させるようにし
たので、凝集剤を添加することなく、凝集を行わせるこ
とができる。
According to each of the above constructions, the magnetic force is applied to the water containing the fine particle substance to cause the fine particle substance to aggregate, so that the aggregation can be performed without adding the aggregating agent.

【0009】[0009]

【発明の実施の形態】以下、本発明の実施の形態におけ
る微粒物質の凝集方法および凝集装置を、図面に基づき
説明する。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, a method and apparatus for aggregating a fine particle substance according to an embodiment of the present invention will be described with reference to the drawings.

【0010】まず、微粒物質の凝集装置を図1に基づき
説明する。この凝集装置は、廃水、地下水、河川水、湖
沼水、海水、槽内水などの水に含まれている微粒物質、
例えば懸濁物質を含む水を流す配管経路(流路)の途中
に介装される筒状体(例えば、PVC管により構成され
ている)1と、この筒状体1の内部に挿入されるととも
に、複数個の板状ブラケット2により両端部が固定され
た棒状の磁石体3とにより構成されている。
First, an apparatus for aggregating fine particles will be described with reference to FIG. This flocculating device is used for fine particles contained in water such as wastewater, groundwater, river water, lake water, seawater, and tank water.
For example, a cylindrical body (for example, constituted by a PVC pipe) 1 interposed in the middle of a piping path (flow path) through which water containing a suspended substance flows, and is inserted into the cylindrical body 1. At the same time, it is composed of a bar-shaped magnet body 3 whose both ends are fixed by a plurality of plate-shaped brackets 2.

【0011】また、この磁石体3は、筒状体1の内壁面
1aに対して所定の隙間すなわち環状通路4を有するよ
うな外径にされかつ筒状体1よりも少し短くされてい
る。この棒状の磁石体3は、円柱状の小磁石5が複数個
直列に並べられて構成され、またその両端部には、流れ
の抵抗を軽減させるための流線型のガイド部6が設けら
れている。この小磁石5は、S極とN極とが互いに対向
するように配列され、またこの小磁石5としては永久磁
石が使用される。
The magnet body 3 has an outer diameter such that it has a predetermined gap, that is, an annular passage 4 with respect to the inner wall surface 1a of the tubular body 1, and is slightly shorter than the tubular body 1. The rod-shaped magnet body 3 is formed by arranging a plurality of columnar small magnets 5 in series, and streamlined guide portions 6 for reducing flow resistance are provided at both ends thereof. . The small magnets 5 are arranged so that the S poles and the N poles face each other, and a permanent magnet is used as the small magnets 5.

【0012】さらに、磁石の磁気力(磁束密度)として
は、1000〜10000ガウスの範囲内のものが使用
され、この磁気力のもとで、通過される水の流速が約1
〜3m/sの範囲内とされる。
Further, the magnetic force (magnetic flux density) of the magnet is within the range of 1000 to 10000 gauss, and under this magnetic force, the flow velocity of the passing water is about 1
Within the range of 3 m / s.

【0013】次に、微粒物質の凝集方法について説明す
る。懸濁物質を含む水を上記凝集装置に供給する。する
と、この水は、筒状体1内の環状空通路4を、所定の速
度(例えば約1.5m/sの速度)で流れる。この時、
筒状体1内に配置されている磁石体3の磁気力が水に作
用し、水の中に含まれている懸濁物質が凝集され、例え
ば数ミクロン〜数十ミクロン程度の大きさになる。
Next, a method for agglomerating the fine particles will be described. Water containing suspended material is fed to the flocculation device. Then, this water flows through the annular empty passage 4 in the tubular body 1 at a predetermined speed (for example, a speed of about 1.5 m / s). This time,
The magnetic force of the magnet body 3 arranged in the tubular body 1 acts on water to agglomerate the suspended substance contained in the water, for example, a size of several microns to several tens of microns. .

【0014】また、必要に応じて、微粒物質を含む水
に、電解物質として例えば塩化ナトリウムまたはこのよ
うな電解物質を含む液体が添加される。このように、磁
気力を作用させることにより凝集が行われるのは、水に
溶けている荷電粒子にローレンツ力が働き、磁気流体力
学効果が生じ、この効果により、荷電粒子間で結晶化・
凝集が促進されるからであると思われる。
If necessary, sodium chloride or a liquid containing such an electrolytic substance is added as an electrolytic substance to water containing the fine particle substance. As described above, the aggregation is performed by applying the magnetic force. The Lorentz force acts on the charged particles dissolved in water, and the magnetohydrodynamic effect is generated.
This is probably because aggregation is promoted.

【0015】なお、水にコロイド粒子が含まれている場
合には、コロイド粒子は、水の中で粒子表面が「負」に
帯電し、相互の反発力によって安定した分散状態を保っ
ているが、磁場の中に水を通すと、イオン分極して電場
が生じ、粒子表面電荷の中和作用により、粒子間の引力
(ファンデル・ワース引力)が働き、粒子同士の接近が
容易になり、やはり凝集が生じる。
When water contains colloidal particles, the surface of the colloidal particles is charged "negatively" in water, and a stable dispersion state is maintained by mutual repulsion. , When water is passed through a magnetic field, an electric field is generated due to ion polarization, and an attractive force between particles (van der Worth attractive force) works due to a neutralizing effect of particle surface charge, which facilitates mutual approach of particles, After all, aggregation occurs.

【0016】このように、凝集した懸濁物質(または、
コロイド粒子)は、通常の濾過装置にて除去される。
Thus, the suspended substance (or
Colloidal particles) are removed by a usual filtration device.

【0017】[0017]

【実施例】以下、上述した凝集方法の実験結果を図2に
基づき説明する。まず、実験に使用した装置について説
明する。
The experimental results of the agglomeration method described above will be described below with reference to FIG. First, the device used in the experiment will be described.

【0018】図2において、11は水を貯溜する貯溜タ
ンクで、この貯溜タンク11の下部には懸濁物質を含ん
だ水を移送する移送配管12の一端部が接続され、また
この移送配管12の他端部は貯溜タンク11の上部に開
放(または接続)されている。
In FIG. 2, reference numeral 11 denotes a storage tank for storing water. One end of a transfer pipe 12 for transferring water containing suspended substances is connected to the lower portion of the storage tank 11, and the transfer pipe 12 is also connected. The other end is open (or connected) to the upper part of the storage tank 11.

【0019】上記移送配管12の途中には、下流側から
順番に、水の循環ポンプ13および本発明に係る磁石体
を有する凝集装置14が介装されている。そして、電気
伝導度が約500μS(ジーメンス)/cmの上水を貯
溜タンク11内に入れた後、標準懸濁物質としてカオリ
ン(土屋カオリン製:ASP−170:平均粒径が0.
4μmのもの)を添加して分散させた。この時の、懸濁
濃度は、約300PPMであった。
A water circulating pump 13 and an aggregating device 14 having a magnet body according to the present invention are provided in the middle of the transfer pipe 12 in this order from the downstream side. Then, after pouring clean water having an electric conductivity of about 500 μS (Siemens) / cm into the storage tank 11, kaolin (manufactured by Tsuchiya Kaolin: ASP-170: average particle size of 0.
4 μm) was added and dispersed. At this time, the suspension concentration was about 300 PPM.

【0020】この状態で、循環ポンプ13を駆動させ、
2500リットル/時の流量でもって、懸濁物質を含む
水を移送配管12を介して凝集装置14に供給し、そし
てこの凝集装置14から出た水を分析した。
In this state, the circulation pump 13 is driven,
Water containing suspended solids was fed to the agglomerator 14 via the transfer line 12 at a flow rate of 2500 l / h and the water leaving the agglomerator 14 was analyzed.

【0021】この時の凝集装置(磁気処理部)14にお
ける磁石体の磁気力、すなわち磁束密度は0ガウス(磁
石体を配置しない状態)、1400ガウス,2400ガ
ウス,7000ガウスの4種類で行い、また水の電気伝
導度は、500μs/cm、および塩化ナトリウム(電
解物質の一例)を約2000PPM加えて電気伝導度を
約3600μS/cmにした場合の凝集状態を調べた結
果を、下記の[表1]に示す。
At this time, the magnetic force of the magnet body in the aggregating device (magnetic processing unit) 14, that is, the magnetic flux density is 0 gauss (in a state where the magnet body is not arranged), 1400 gauss, 2400 gauss, and 7000 gauss. The electrical conductivity of water was 500 μs / cm, and the result of examining the aggregation state when the electrical conductivity was approximately 3600 μS / cm by adding approximately 2000 PPM of sodium chloride (an example of an electrolytic substance) is shown in the table below. 1].

【0022】[0022]

【表1】 [Table 1]

【0023】上記の[表1]から、磁気力を作用させた
場合、すなわち磁気処理を行った場合の方が、凝集して
いることが良く分かる。また、この凝集の程度は、磁気
力が強い程、また水の電気伝導度が大きい程、凝集効果
が大きいことが分かる。
From the above-mentioned [Table 1], it is clear that the aggregates are formed when the magnetic force is applied, that is, when the magnetic treatment is performed. Further, it can be seen that the degree of aggregation is larger as the magnetic force is stronger and the electric conductivity of water is larger.

【0024】なお、図3に、上水にカオリンを添加した
場合の粒径分布の状態をグラフ化したものを示す。この
時の実験条件は下記の通りである。
FIG. 3 is a graph showing the state of particle size distribution when kaolin is added to tap water. The experimental conditions at this time are as follows.

【0025】 流量:2.4m3 /hr,流速:1.6m/s 懸濁濃度:約300mg/リットル 電気伝導度:約500μS/cmFlow rate: 2.4 m 3 / hr, flow rate: 1.6 m / s Suspension concentration: about 300 mg / liter Electrical conductivity: about 500 μS / cm

【0026】[0026]

【発明の効果】以上のように本発明の微粒物質の凝集方
法および凝集装置の構成によると、微粒物質を含む水
に、磁気力を作用させて微粒物質を凝集させるようにし
たので、例えばプレコート材のように廃棄物を出すこと
がなく、また凝集剤を使用する場合に比べて、凝集剤の
添加およびその処理設備を必要とせず、したがって微粒
物質を含む処理設備を、容易にかつ安価に製作すること
ができる。
As described above, according to the method of aggregating a fine particle substance and the configuration of the aggregating apparatus of the present invention, the magnetic force is applied to the water containing the fine particle substance to agglomerate the fine particle substance. Compared to the case where a coagulant is used, it does not generate waste like materials, and does not require addition of a coagulant and its treatment equipment, and therefore, a treatment equipment containing fine particles can be easily and inexpensively. Can be manufactured.

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

【図1】本発明の実施の形態における微粒物質の凝集装
置の断面図である。
FIG. 1 is a cross-sectional view of a fine particle substance aggregating apparatus according to an embodiment of the present invention.

【図2】同実施の形態における凝集方法の実験設備を示
す概略構成図である。
FIG. 2 is a schematic configuration diagram showing experimental equipment for an aggregation method according to the same embodiment.

【図3】同実施の形態における凝集方法の実験例の結果
を示すグラフである。
FIG. 3 is a graph showing the results of an experimental example of the aggregation method in the same embodiment.

【符号の説明】 1 筒状体 1a 内壁面 3 磁石体 4 環状通路 5 小磁石[Explanation of reference numerals] 1 cylindrical body 1a inner wall surface 3 magnet body 4 annular passage 5 small magnet

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】微粒物質を含む水に磁気力を作用させて微
粒物質を凝集させることを特徴とする微粒物質の凝集方
法。
1. A method of aggregating a fine particle substance, which comprises causing a magnetic force to act on water containing the fine particle substance to agglomerate the fine particle substance.
【請求項2】磁気力を作用させる際の微粒物質を含む水
の流速を、1〜3m/sの範囲内としたことを特徴とす
る請求項1記載の微粒物質の凝集方法。
2. The method for aggregating a fine particle substance according to claim 1, wherein the flow velocity of the water containing the fine particle substance at the time of applying the magnetic force is set in the range of 1 to 3 m / s.
【請求項3】磁気力を1000〜10000ガウスの範
囲内としたことを特徴とする請求項1または2記載の微
粒物質の凝集方法。
3. The method for aggregating a fine particle substance according to claim 1 or 2, wherein the magnetic force is within a range of 1000 to 10000 gauss.
【請求項4】水中に電解物質または電解物質を含む液体
を添加することを特徴とする請求項1ないし3のいずれ
かに記載の微粒物質の凝集方法。
4. The method for aggregating a fine particle substance according to claim 1, wherein an electrolytic substance or a liquid containing the electrolytic substance is added to water.
【請求項5】微粒物質を含む水を流す流路の途中に介装
される筒状体の内部に、円柱状の磁石体を配置したこと
を特徴とする微粒物質の凝集装置。
5. An apparatus for aggregating a fine particle substance, wherein a cylindrical magnet body is arranged inside a tubular body interposed in the middle of a flow path for flowing water containing the fine particle substance.
【請求項6】磁石体を永久磁石により構成したことを特
徴とする請求項5記載の微粒物質の凝集装置。
6. The aggregating apparatus for fine particle substances according to claim 5, wherein the magnet body is constituted by a permanent magnet.
【請求項7】筒状体の内壁面と磁石体との間に形成され
る環状通路を流れる水の流速を1〜3m/sの範囲内と
なるように構成したことを特徴とする請求項6記載の微
粒物質の凝集装置。
7. A flow velocity of water flowing through an annular passage formed between the inner wall surface of the cylindrical body and the magnet body is set to be within a range of 1 to 3 m / s. 6. A device for aggregating fine particles according to item 6.
【請求項8】磁石体の磁気力を1000〜10000ガ
ウスの範囲内としたことを特徴とする請求項6または7
記載の微粒物質の凝集装置。
8. The magnetic force of the magnet body is set within the range of 1000 to 10000 gauss.
An aggregating apparatus for the fine-particle substances described.
JP7213865A 1995-08-23 1995-08-23 Method and apparatus for aggregating fine particles Expired - Fee Related JP2738522B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7213865A JP2738522B2 (en) 1995-08-23 1995-08-23 Method and apparatus for aggregating fine particles

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7213865A JP2738522B2 (en) 1995-08-23 1995-08-23 Method and apparatus for aggregating fine particles

Publications (2)

Publication Number Publication Date
JPH0957147A true JPH0957147A (en) 1997-03-04
JP2738522B2 JP2738522B2 (en) 1998-04-08

Family

ID=16646306

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2738522B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7943043B2 (en) 2007-04-27 2011-05-17 Toko Co., Ltd. Magnetic field forming device for active water and fluid treatment apparatus using the same
JP2013147539A (en) * 2012-01-17 2013-08-01 National Institute Of Advanced Industrial Science & Technology Method for recycling used grease and device therefor
JP2013147538A (en) * 2012-01-17 2013-08-01 National Institute Of Advanced Industrial Science & Technology Method for recycling used grease and device therefor

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JPS5095179A (en) * 1973-12-26 1975-07-29
JPS59189991A (en) * 1983-04-11 1984-10-27 Hitachi Metals Ltd Water disposal device
JPS60222154A (en) * 1984-04-20 1985-11-06 Hitachi Plant Eng & Constr Co Ltd Magnetic coagulator
JPH032033A (en) * 1989-05-31 1991-01-08 Hitachi Chem Co Ltd Composite laminate
JPH04110091A (en) * 1990-08-31 1992-04-10 Japan Kemitsukusu:Kk Magnetic fluid device
JPH0716598A (en) * 1993-06-30 1995-01-20 Nippon Tainetsu Kagaku Kogyo Kk Method for activating water, method for clarifying water in closed lake and marsh and apparatus therefor

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Publication number Priority date Publication date Assignee Title
JPS5095179A (en) * 1973-12-26 1975-07-29
JPS59189991A (en) * 1983-04-11 1984-10-27 Hitachi Metals Ltd Water disposal device
JPS60222154A (en) * 1984-04-20 1985-11-06 Hitachi Plant Eng & Constr Co Ltd Magnetic coagulator
JPH032033A (en) * 1989-05-31 1991-01-08 Hitachi Chem Co Ltd Composite laminate
JPH04110091A (en) * 1990-08-31 1992-04-10 Japan Kemitsukusu:Kk Magnetic fluid device
JPH0716598A (en) * 1993-06-30 1995-01-20 Nippon Tainetsu Kagaku Kogyo Kk Method for activating water, method for clarifying water in closed lake and marsh and apparatus therefor

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7943043B2 (en) 2007-04-27 2011-05-17 Toko Co., Ltd. Magnetic field forming device for active water and fluid treatment apparatus using the same
JP2013147539A (en) * 2012-01-17 2013-08-01 National Institute Of Advanced Industrial Science & Technology Method for recycling used grease and device therefor
JP2013147538A (en) * 2012-01-17 2013-08-01 National Institute Of Advanced Industrial Science & Technology Method for recycling used grease and device therefor

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