JP2004167372A - Flocculating method and apparatus for suspended particle - Google Patents

Flocculating method and apparatus for suspended particle Download PDF

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Publication number
JP2004167372A
JP2004167372A JP2002336043A JP2002336043A JP2004167372A JP 2004167372 A JP2004167372 A JP 2004167372A JP 2002336043 A JP2002336043 A JP 2002336043A JP 2002336043 A JP2002336043 A JP 2002336043A JP 2004167372 A JP2004167372 A JP 2004167372A
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Japan
Prior art keywords
filter
liquid
particles
oil
suspended
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Japanese (ja)
Inventor
Hironori Muraki
弘則 村木
Hiroyuki Aida
寛幸 会田
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Sumitomo Densetsu Co Ltd
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Sumitomo Densetsu Co Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P70/00Climate change mitigation technologies in the production process for final industrial or consumer products
    • Y02P70/10Greenhouse gas [GHG] capture, material saving, heat recovery or other energy efficient measures, e.g. motor control, characterised by manufacturing processes, e.g. for rolling metal or metal working

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  • Auxiliary Devices For Machine Tools (AREA)
  • Grinding-Machine Dressing And Accessory Apparatuses (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Filtering Materials (AREA)
  • Filtration Of Liquid (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a flocculating method in which a polluted liquid containing negatively electrified particles is effectively purified. <P>SOLUTION: The polluted liquid in a tank 2 is passed through a flocculating device 12 where cations are supplied to the liquid to enhance the flocculatability of the suspended particles. The liquid is fed to filtration equipment 13 and is filtered by a filter 13a previously penetrated with an oil-component. The equally good alternative is to directly add the oil-component to the polluted liquid and to filter the liquid by the filter after stirring. In either method, the oil-component acts as the nucleus for particle flocculation and the flocculation and the particles are effectively caught. <P>COPYRIGHT: (C)2004,JPO

Description

【0001】
【発明の属する技術分野】
この発明は、切削、研削、切断などに用いられる水溶性のクーラント液や加工部品の洗浄排液、生物処理水など、負に帯電した微粒子を含んでいる汚濁液の浄化を効果的に行うことを可能ならしめた懸濁粒子の凝集方法と、その方法の実施に用いる懸濁粒子凝集装置に関する。
【0002】
【従来の技術】
各種廃液中に含まれる汚濁物質は、濾材で捕捉できないものが多く、濾過法では効率的な除去が難しい。このため、一般的な水処理では中和処理などの前処理を行った後に凝集剤を加えて液中の浮遊粒子を凝集させ、粒子が凝集してできるフロック(綿状物)を大きくして沈降させるなどの方法で除去している。
【0003】
疎水性コロイド粒子の凝集は、粒子の表面に存在する電荷(凝集阻害因子)と反対符号のイオンを加える方法でなされる。
【0004】
電解質を加えると、粒子間の反発ポテンシャルが減少し、相対的に粒子間の引力が上回り、粒子が互いに引き寄せられて凝集することはDLVO理論として知られ、また、イオンによる凝集はイオンの価数が大きいほど低濃度で起こることはシュルツハーディの法則として知られている。
【0005】
ところで、冒頭で述べたクーラント液などは、循環させて繰り返し使用され、循環の途中に濾過器で濾過されるが、濾過器で捕捉できない粒子が残る。ところが、工場内で使用するために種々の制約を受け、一般的水処理で行っている沈殿槽を用いる凝集沈殿除去が行えない。
【0006】
そこで、本出願人は、クーラント液などを沈殿槽なしで浄化できる凝集方法と、凝集器を特願2002−113027号で提案している。
【0007】
その提案済の方法は、汚濁液中に陽イオンを流出させて液中の懸濁粒子を凝集させる。また、凝集器は、容器内に凝集剤(陽イオンを発生させる物質)を充填し、容器に導入する汚濁液を内部の凝集剤に接触通過させるようにしている。なお、凝集剤は、マグネシウム、酸化マグネシウム、水酸化マグネシウム、炭酸マグネシウム、酸化カルシウム、水酸化カルシウム、炭酸カルシウムなどのアルカリ土類金属やアルミニウム、酸化アルミニウム、水酸化アルミニウムなどの顆粒、ペレット、チップなどが有効なことが分かっている。この凝集剤として、多孔質酸化マグネシウムや多孔質水酸化マグネシウムの顆粒、ペレット、チップなどを用いると特に優れた凝集効果が得られる。
【0008】
【発明が解決しようとする課題】
凝集器に通して凝集させた汚濁液中の懸濁粒子は、凝集器通過後の汚濁液をペーパフィルタなどに通して漉し取る。
【0009】
ところが、非常に目の細かいフィルタを使用しても、せっかく凝集させた懸濁粒子の一部がフィルタを通り抜けてしまうという問題に直面した。クーラント液などは浄化再生が不十分であると長期にわたる繰り返し使用が望めない。
【0010】
そこで、この発明は、改善されたより良い方法を提供して懸濁粒子の凝集、除去をより効果的に行えるようにすることを課題としている。
【0011】
【課題を解決するための手段】
上記の課題を解決するため、この発明においては、負に帯電した粒子を含む汚濁液中に陽イオンを供給して液中の懸濁粒子を凝集させ、さらに、凝集粒子を油分に接触させてフィルタで漉し取る懸濁粒子の凝集方法を提供する。
【0012】
汚濁液に対する陽イオンの供給は、陽イオンを発生させる物質を溶解して添加する方法、汚濁液を通す容器に陽イオンを発生させる物質を入れ、この物質に汚濁液を接触通過させる方法、液を入れたタンクに前記物質を沈めておく方法などで行える。
【0013】
懸濁粒子に接触させる油は、低粘度油が好ましい。この油分は予めフィルタに付着させておいてもよいし、陽イオンを流出させた汚濁液中に油分を直接添加してもよい。前者の場合、油分を付着させたフィルタに陽イオン供給後の汚濁液を通す。また、後者は油分を添加した汚濁液を攪拌してフィルタに通す。
【0014】
この方法を実施するために、この発明においては、負に帯電した粒子を含む汚濁液を通過させてこの汚濁液中に陽イオンを流出させる凝集器と、油分をしみ込ませたフィルタで汚濁液中の凝集粒子を漉し取る濾過器とを備えている懸濁粒子凝集装置も併せて提供する。
【0015】
この懸濁粒子凝集装置は、ペーパフィルタを送りをかけて濾過部に連続的または間欠的に供給しながら濾過を行うものが好ましい。
【0016】
また、凝集器として、陽イオンを発生させる凝集剤を容器に収納し、その凝集剤の上部において容器の内部に空間を形成し、容器の下部から導入した汚濁液を前記凝集剤に接触させて通過させ、前記空間を経て容器の上部から流出させるものを用いるのも好ましい。
【0017】
【作用】
発明者は、懸濁粒子を漉し採ったペーパフィルタを観察して油分がたまたま付着していた箇所に漉し採られた粒子が集中していることに気づいた。そこで、ペーパフィルタに意図的に機械油を軽く噴霧してしみ込ませ、このペーパフィルタに懸濁粒子凝集後の汚濁液を通してみた。その結果、懸濁粒子の捕捉が非常に良くなされており、油分が粒子の捕捉に効果を奏することを見いだした。
【0018】
また、陽イオンを供給した汚濁液に油分を加え、攪拌後に濾過したところ、この方法でもペーパフィルタにしみ込ませた場合と同様に捕捉性が高まることが分かった。油分が粒子凝集の核となり、また、油分がフィルタに対する凝集粒子吸着のつなぎの役目を果たすのではないかと考えられる。
【0019】
換言すれば、本出願人が特願2002−113027号で提案している方法では、循環させて使用する液は特に、凝集時間を長くとれないためフロックの成長が十分に進まず、フィルタ通過時に再分散するなどして漉し取り難くなるのと、フィルタによる吸着がなされないことにあるのではないかと考えられ、この方法の不満足な部分が油分の使用によって解消される。
【0020】
【発明の実施の形態】
図1にこの発明の方法の実施形態を示す。図は工作機械のクーラント液の浄化を例に挙げている。
【0021】
図中1は水溶性クーラント液の供給装置である。クーラント液を入れたタンク2と、タンク2内の液を汲み上げるポンプ3とを備えるこの供給装置1で液を循環させて工作機械4の工作部に供給する。循環経路の戻り路を通ってタンク2に戻された使用済みの液は使用の繰り返しによって次第に汚れて濁ってくるのでこれをこの発明の方法で浄化する。
【0022】
図の10がこの発明の方法を実施する懸濁粒子凝集装置である。この装置10は、タンク2内の汚濁液を汲み上げるポンプ11aと、そのポンプ11aを通過した液に陽イオンを供給する凝集器12と、凝集器12を通過してタンク2に戻された液をポンプ11bで汲み上げ、その液を濾過する濾過装置13とから成る。
【0023】
凝集器12は、容器の中に陽イオンを溶出させる凝集剤を入れ、その凝集剤に汚濁液を接触させて通過させるようにしてある。凝集剤は既述の物質の顆粒、ペレット、チップなどでよい。陽イオンは、陽イオン発生物質を溶解してタンク2内の液に添加する方法や陽イオン発生物質をタンク2中に沈めておく方法によっても供給することができ、凝集器12を使用することは必須の要件にはならない。
【0024】
濾過装置13は、ロール巻きした帯状フィルタ13aをフィーダ13bで連続的または間欠的に繰り出して濾過部に供給し、濾過部を通過したフィルタの表面の付着物をスクレパー13cで掻き落として回収し、その後、使用済みフィルタを巻き取って回収するものにしているが、これに限定されるものではない。使い捨てする帯状フィルタ13aは、安価で、焼却処理も可能なペーパフィルタが好ましい。このフィルタ13aに予め機械油を噴霧してしみ込ませておき、凝集器12に通して陽イオンを添加し、さらにタンク2に戻してここで凝集を進めた液をポンプ11bで汲み上げてこのフィルタ13aで漉す。濾過後の液はタンク13dに回収し、きれいになった液をクーラント液供給装置1のタンク2に戻す。
【0025】
なお、凝集器12に対する汚濁液の導入は数回繰り返すのが望ましい。
【0026】
図2に、凝集器12の好ましい形態の一例を示す。この凝集器12は、上部と下部に汚濁液の出入口を有する容器12aの中に陽イオンを溶出させる凝集剤12bを充填し、この凝集剤12bの上部に空間12cを生じさせ、容器12aの下部から導入した汚濁液を凝集剤12bに接触させて通過させ、空間12cに流れた液を容器上部の口から流出させる構造にしている。
【0027】
この凝集器12は、汚濁液と凝集剤12bの接触効果が高い。図のように汚濁液を下から上に向けて流すと水流によって凝集剤12bが空間12c内で躍動し(いわゆる踊りが生じる)、それによって汚濁液との接触効果が高められる。図の12d、12eは凝集剤流出防止用のスクリーンである。このスクリーンの目詰まり対策としてここでは凝集剤12bのサイズを大きくし、スクリーンの目孔を大きくしているが、目詰まりの抑制は、特願2002−113027号で述べているような逆洗回路を設けて行うこともできる。
【0028】
また、上述したように、油分は汚濁液に直接加えてもよい。
【0029】
以下に、凝集実験の結果を述べる。
−実験1−
ビーカに入れた400ccの水道水に分散剤入りアルミナ粉(粒子径0.1ミクロン)4gを投入し、攪拌してコロイド水を作った。そして、このコロイド水を2本の試験管に入れた。試験管の一方には陽イオンを溶出させる凝集剤(多孔質水酸化マグネシウムのペレット)を0.4g入れ(以下これを試験管Iという)、他方の試験管は凝集剤無しとして(これを試験管IIという)コロイド水の透明度向上の状況を観察した。
【0030】
試験管注入後1時間経過の段階では2本の試験管の透明度に差は見られなかったが、6時間経過後は試験管Iの液は上から1cmぐらいまでがかなり透明になったのに対し、試験管IIの液がかなり透明になったのは上から僅か0.3cm程度であった。
【0031】
また、12時間経過後は、試験管Iの液は上から1cm程度がさらに透明になり、その下側も透明度が増してきた。これに対し、試験管IIの液は全体が濁ってしまった。
【0032】
23時間経過後は、試験管Iの液は全体の透明度が高まった。一方、試験管IIの液は上から1cm程度しか透明にならなかった。
【0033】
この実験から、凝集剤を使用すると、ゆっくりではあるが凝集効果が現れることが分かる。
【0034】
−実験2−
実験1で用いたものと同じアルミナコロイド水400ccに凝集剤(多孔質水酸化マグネシウムのペレット)0.4gを加え、これを市販の機械油(商品名クレ556)を軽くスプレー塗布した♯950のペーパフィルタに4回通したところ高い透明度に濾過できた。この実験ではペーパフィルタによる濾過の際に、大きな粒子が成長するのが確認された。これに対し、凝集剤を加えていないコロイド水は、同じ機械油を同様に塗布したペーパフィルタに10回通しても透明度は良くならなかった。
【0035】
−実験3−
実験2と同じアルミナコロイド水400ccに凝集剤(多孔質水酸化マグネシウムのペレット)0.4gを加え、さらに、このコロイド水に前記機械油(商品名クレ556)0.4ccを直接吹き込み、攪拌後♯950のペーパフィルタ(油散布無し)に通した。この濾過を約10回繰り返したところかなりの透明度に濾過することができた。一方、凝集剤を添加していないアルミナコロイド水は粒子の成長が見られず、♯950のペーパフィルタ(油散布無し)に10回通した後にも白濁したままであった。
【0036】
−実験4−
実験2と同じアルミナコロイド水400ccを試料Aとし、また、クーラント液は界面活性剤を含むものが一般的であるのでそれを模擬したものとして試料Aにさらに非イオン界面活性剤(ポリエチレングリコールモノラウレート)を0.4cc添加したものを試料Bとし、両試料を目穴5ミクロンのペーパフィルタで濾過した。その結果、試料A、Bとも白濁しており完全な濾過はできなかった。
【0037】
次に、試料A、Bに凝集剤(多孔質水酸化マグネシウムのペレット)0.4gを加え、30分間放置後に目穴5ミクロンのペーパフィルタで濾過したところ、試料A、Bとも完全ではないが凝集剤なしよりも良い結果が得られた。
【0038】
また、試料A、Bに凝集剤(多孔質水酸化マグネシウムのペレット)0.4gとともに機械油(商品名クレ556)0.4ccを投入し、これを攪拌後目穴5ミクロンのペーパフィルタで濾過したところ、試料Aは透明度が高まった。試料Bは少し白濁しておりAほどではなかったがこれも透明度が高まった。なお、試料Aは油分が淡い黄色の塊になって濾過する前の水面に浮いていた。
【0039】
この機械油を加えた両試料A、Bを、同じ機械油を散布してしみ込ませた目穴5ミクロンのペーパフィルタで濾過したところ、試料Aは完全に透明になった。また、試料Bは完全ではなかったが機械油をしみ込ませていないフィルタ使用時よりも透明度が高まった。
【0040】
以上の実験結果から、非イオン系界面活性剤を含む液と含まない液には若干効果に差が出るが、どちらの液に対しても電解質(陽イオン)と油分の併用が極めて有効なことを確認できた。
【0041】
【発明の効果】
以上述べたように、この発明においては、懸濁粒子の凝集、捕捉を、汚濁液に陽イオンを加え、これをさらに油分に接触させる方法によって行うので、負に帯電した粒子を含む汚濁液の浄化を効果的に行うことができ、工場内使用するクーラント液などの浄化度を高めて液の再使用期間を長くすることができる。
【0042】
また、この発明の方法を実施する凝集装置は、凝集器内の凝集剤に汚濁液を接触通過させ、その後この液を予め油分を付着させたフィルタで濾過するので大きな沈澱槽を設けずに懸濁粒子の凝集、捕捉を行うことができ、装置の小型化、それによる使用制限の緩和が図れる。
【0043】
なお、凝集器として容器の上部に空間を設け、汚濁液を下部から上部に向けて通すものを用いる装置は、凝集器が目詰まりし難く、液を循環させながら浄化する装置の稼働効率向上も図れる。
【図面の簡単な説明】
【図1】この発明の方法と装置の実施形態を示す図
【図2】この発明の装置に利用する凝集器の一例を示す断面図
【符号の説明】1 クーラント液供給装置
2 タンク
3 ポンプ
4 工作機械
10 懸濁粒子凝集装置
11a、11b ポンプ
12 凝集器
12a 容器
12b 凝集剤
12c 空間
12d、12e スクリーン
13 濾過装置
13a 帯状フィルタ
13b フィーダ
13c スクレパー
13d タンク
[0001]
BACKGROUND OF THE INVENTION
The present invention effectively purifies a contaminated liquid containing negatively charged fine particles such as a water-soluble coolant liquid used for cutting, grinding, cutting, etc., cleaning waste liquid of processed parts, biological treatment water, etc. The present invention relates to a method for agglomerating suspended particles that enable the above-mentioned method and a suspended particle aggregating apparatus used for carrying out the method.
[0002]
[Prior art]
Many pollutants contained in various waste liquids cannot be captured by the filter medium, and it is difficult to remove them efficiently by the filtration method. For this reason, in general water treatment, after pretreatment such as neutralization treatment, a flocculant is added to agglomerate floating particles in the liquid, and the flocs (cotton) formed by the aggregation of particles are increased. It is removed by methods such as sedimentation.
[0003]
Aggregation of the hydrophobic colloidal particles is performed by a method of adding ions having the opposite sign to the charge (aggregation inhibitor) present on the surface of the particles.
[0004]
When electrolyte is added, the repulsive potential between the particles decreases, the attractive force between the particles relatively increases, and the particles are attracted to each other and agglomerate. This is known as DLVO theory. It is known as Schulz Hardy's law that the smaller the value, the lower the concentration.
[0005]
By the way, the coolant liquid described at the beginning is repeatedly used after being circulated, and is filtered by a filter in the middle of the circulation, but particles that cannot be captured by the filter remain. However, due to various restrictions for use in a factory, coagulation sediment removal using a sedimentation tank that is carried out in general water treatment cannot be performed.
[0006]
Therefore, the present applicant has proposed a coagulation method and a coagulator capable of purifying coolant liquid and the like without a precipitation tank in Japanese Patent Application No. 2002-113027.
[0007]
The proposed method causes cations to flow into the turbid liquid to agglomerate suspended particles in the liquid. In addition, the aggregator is filled with a flocculant (a substance that generates cations) in a container so that the contaminated liquid introduced into the container is brought into contact with the internal flocculant. The flocculants include alkaline earth metals such as magnesium, magnesium oxide, magnesium hydroxide, magnesium carbonate, calcium oxide, calcium hydroxide and calcium carbonate, granules such as aluminum, aluminum oxide and aluminum hydroxide, pellets, chips, etc. Is known to be effective. As the aggregating agent, particularly excellent aggregating effect can be obtained by using porous magnesium oxide or porous magnesium hydroxide granules, pellets, chips and the like.
[0008]
[Problems to be solved by the invention]
The suspended particles in the turbid liquid aggregated through the aggregator are passed through the paper filter or the like after passing through the aggregator.
[0009]
However, even if a very fine filter is used, there is a problem that some of the suspended particles that have been agglomerated pass through the filter. If the coolant and the like are not sufficiently purified and regenerated, they cannot be used repeatedly over a long period of time.
[0010]
Accordingly, an object of the present invention is to provide an improved and better method so that suspended particles can be aggregated and removed more effectively.
[0011]
[Means for Solving the Problems]
In order to solve the above-described problems, in the present invention, a cation is supplied to a contaminated liquid containing negatively charged particles to aggregate suspended particles in the liquid, and the aggregated particles are contacted with oil. Provided is a method for agglomerating suspended particles which are filtered off.
[0012]
The supply of cations to the contaminated liquid is made by dissolving and adding a substance that generates cations, putting the substance that generates cations in a container through which the contaminated liquid is passed, and allowing the contaminated liquid to pass through this substance. This can be done by immersing the substance in a tank containing the
[0013]
The oil brought into contact with the suspended particles is preferably a low viscosity oil. This oil component may be attached to the filter in advance, or the oil component may be directly added to the contaminated liquid from which the cation has flowed out. In the former case, the lysate after supplying the cation is passed through a filter to which oil has adhered. In the latter case, the contaminated liquid to which oil has been added is stirred and passed through a filter.
[0014]
In order to carry out this method, in the present invention, a pollutant containing negatively charged particles is allowed to pass and a cation is allowed to flow into the pollutant, and a filter impregnated with oil is used in the pollutant. A suspended particle aggregating apparatus including a filter for removing the agglomerated particles is also provided.
[0015]
This suspended particle aggregating apparatus is preferably one that performs filtration while feeding a paper filter continuously or intermittently to the filtration unit.
[0016]
Further, as a flocculator, a flocculating agent that generates cations is housed in a container, a space is formed inside the container at the upper part of the flocculating agent, and a contaminant introduced from the lower part of the container is brought into contact with the flocculating agent. It is also preferable to use what is allowed to pass through and flows out from the upper part of the container through the space.
[0017]
[Action]
The inventor observed a paper filter obtained by picking up suspended particles, and noticed that the picked up particles were concentrated at the locations where the oils happened to be attached. Therefore, the paper filter was intentionally lightly sprayed with mechanical oil, and the suspended liquid after aggregation of suspended particles was passed through the paper filter. As a result, it was found that the suspended particles were trapped very well and that the oil component was effective in trapping the particles.
[0018]
In addition, when oil was added to the turbid liquid supplied with cations and filtered after stirring, it was found that this method also improved the trapping ability as in the case of impregnating the paper filter. It is thought that the oil component serves as a nucleus of particle aggregation, and the oil component plays a role in adsorbing the aggregated particles to the filter.
[0019]
In other words, in the method proposed by the present applicant in Japanese Patent Application No. 2002-113027, the liquid to be circulated is not particularly long because the floc growth does not proceed sufficiently because the agglomeration time cannot be taken long, and the liquid passes through the filter. It is thought that it is difficult to remove the wrinkle due to re-dispersion or the like, and it is considered that the adsorption by the filter is not performed, and the unsatisfactory part of this method is eliminated by using the oil.
[0020]
DETAILED DESCRIPTION OF THE INVENTION
FIG. 1 shows an embodiment of the method of the present invention. The figure gives an example of cleaning the coolant of a machine tool.
[0021]
In the figure, reference numeral 1 denotes a water-soluble coolant supply device. The liquid is circulated and supplied to the machine part of the machine tool 4 by the supply device 1 including the tank 2 containing the coolant liquid and the pump 3 that pumps up the liquid in the tank 2. Since the used liquid returned to the tank 2 through the return path of the circulation path becomes gradually dirty and turbid due to repeated use, it is purified by the method of the present invention.
[0022]
10 in the figure is a suspended particle aggregating apparatus for carrying out the method of the present invention. The apparatus 10 includes a pump 11a that pumps up the contaminated liquid in the tank 2, a coagulator 12 that supplies cations to the liquid that has passed through the pump 11a, and a liquid that has passed through the aggregator 12 and returned to the tank 2. It comprises a filtration device 13 that is pumped up by a pump 11b and filters the liquid.
[0023]
The aggregator 12 is configured such that a flocculant that elutes cations is placed in a container, and a turbid liquid is brought into contact with the flocculant to pass therethrough. The flocculant may be granules, pellets, chips, etc. of the aforementioned substances. The cation can be supplied by a method in which the cation generating substance is dissolved and added to the liquid in the tank 2 or a method in which the cation generating substance is submerged in the tank 2, and the aggregator 12 is used. Is not an essential requirement.
[0024]
The filter device 13 continuously or intermittently feeds the rolled belt-like filter 13a with a feeder 13b and supplies it to the filtration unit, and scrapes and collects deposits on the surface of the filter that has passed through the filtration unit with a scraper 13c. Thereafter, the used filter is wound up and collected, but is not limited thereto. The disposable band filter 13a is preferably a paper filter that is inexpensive and can be incinerated. The filter 13a is preliminarily sprayed with machine oil, added with cations through the agglomerator 12, and returned to the tank 2, where the agglomerated liquid is pumped up by the pump 11b.漉The filtered liquid is collected in the tank 13d, and the cleaned liquid is returned to the tank 2 of the coolant liquid supply apparatus 1.
[0025]
In addition, it is desirable to introduce the contaminated liquid into the aggregator 12 several times.
[0026]
In FIG. 2, an example of the preferable form of the aggregator 12 is shown. This aggregator 12 is filled with a flocculant 12b that elutes cations in a container 12a having an inlet and a outlet for a pollutant at the upper part and the lower part, and a space 12c is formed above the flocculant 12b. In this structure, the turbid liquid introduced from above is allowed to pass through the flocculant 12b so that the liquid that has flowed into the space 12c flows out from the mouth at the top of the container.
[0027]
The aggregator 12 has a high contact effect between the contaminated liquid and the aggregating agent 12b. As shown in the figure, when the pollutant is flowed from the bottom to the top, the flocculant 12b is vibrated in the space 12c by the water flow (so-called dance occurs), thereby enhancing the contact effect with the pollutant. 12d and 12e in the figure are screens for preventing the flocculant from flowing out. Here, as a countermeasure against clogging of the screen, the size of the flocculant 12b is increased and the apertures of the screen are enlarged, but the clogging is suppressed by a backwash circuit as described in Japanese Patent Application No. 2002-113027. It can also be performed.
[0028]
Further, as described above, the oil may be added directly to the turbid liquid.
[0029]
The results of the aggregation experiment are described below.
-Experiment 1
4 g of alumina powder (particle diameter 0.1 micron) containing a dispersant was added to 400 cc of tap water in a beaker and stirred to produce colloidal water. And this colloidal water was put into two test tubes. One test tube contains 0.4 g of a flocculant (porous magnesium hydroxide pellet) that elutes cations (hereinafter referred to as test tube I), and the other test tube has no flocculant (this is tested). The state of improvement in the transparency of colloidal water (tube II) was observed.
[0030]
Although there was no difference in the transparency of the two test tubes at the stage of 1 hour after the test tube injection, the liquid in the test tube I became quite transparent up to about 1 cm from the top after 6 hours. On the other hand, it was only about 0.3 cm from the top that the liquid in the test tube II became quite transparent.
[0031]
Further, after 12 hours, the liquid in the test tube I became more transparent about 1 cm from the top, and the transparency also increased on the lower side. On the other hand, the whole liquid in the test tube II became cloudy.
[0032]
After 23 hours, the overall transparency of the liquid in test tube I increased. On the other hand, the liquid in the test tube II became transparent only about 1 cm from the top.
[0033]
From this experiment, it can be seen that when a flocculant is used, a flocculating effect appears slowly.
[0034]
-Experiment 2-
In # 950, 0.4 g of flocculant (porous magnesium hydroxide pellets) was added to 400 cc of the same alumina colloidal water used in Experiment 1, and this was lightly spray-coated with a commercial machine oil (trade name Kure 556). When it passed through the paper filter four times, it could be filtered with high transparency. In this experiment, it was confirmed that large particles grew during filtration with a paper filter. On the other hand, the colloidal water to which no flocculant was added did not improve the transparency even when it was passed through a paper filter coated with the same machine oil in the same manner 10 times.
[0035]
-Experiment 3-
0.4 g of a flocculant (porous magnesium hydroxide pellets) is added to 400 cc of the same alumina colloidal water as in Experiment 2, and 0.4 cc of the machine oil (trade name Kure 556) is directly blown into the colloidal water. It was passed through a # 950 paper filter (no oil spread). When this filtration was repeated about 10 times, it was able to be filtered with considerable transparency. On the other hand, the alumina colloidal water to which no flocculant was added did not show particle growth, and remained cloudy even after passing 10 times through a # 950 paper filter (no oil spraying).
[0036]
-Experiment 4
400 cc of the same alumina colloidal water as in Experiment 2 is used as sample A, and the coolant liquid generally contains a surfactant. Therefore, as a simulation, sample A is further added to a nonionic surfactant (polyethylene glycol monolaur). Sample B was added with 0.4 cc of the rate), and both samples were filtered with a paper filter having a pore size of 5 microns. As a result, both samples A and B were cloudy and could not be completely filtered.
[0037]
Next, 0.4 g of a flocculant (porous magnesium hydroxide pellets) was added to Samples A and B. After standing for 30 minutes and filtered through a paper filter with a 5 micron aperture, both Samples A and B were not complete. Better results were obtained than without the flocculant.
[0038]
Samples A and B were charged with 0.4 g of flocculant (porous magnesium hydroxide pellets) and 0.4 cc of machine oil (trade name Kure 556), and after stirring, filtered through a paper filter with a pore size of 5 microns. As a result, the transparency of Sample A increased. Sample B was slightly cloudy and not as high as A, but this also increased transparency. In addition, the sample A floated on the water surface before the oil became a light yellow lump and was filtered.
[0039]
When both samples A and B to which this machine oil was added were filtered with a paper filter having a pore size of 5 μm soaked with the same machine oil, the sample A became completely transparent. Sample B was not perfect, but the transparency was higher than when using a filter not impregnated with machine oil.
[0040]
From the above experimental results, there is a slight difference in the effect between the liquid containing nonionic surfactant and the liquid not containing it, but the combined use of electrolyte (cation) and oil is extremely effective for both liquids. Was confirmed.
[0041]
【The invention's effect】
As described above, in the present invention, the suspension particles are aggregated and trapped by a method in which a cation is added to the contaminated liquid and this is further brought into contact with the oil. Purification can be performed effectively, the degree of purification of the coolant liquid used in the factory can be increased, and the liquid reuse period can be extended.
[0042]
In the flocculating apparatus for carrying out the method of the present invention, a turbid liquid is brought into contact with the flocculating agent in the flocculator, and then the liquid is filtered through a filter to which oil has been attached in advance. Agglomeration and trapping of turbid particles can be performed, and the size of the apparatus can be reduced and the use restriction can be relaxed accordingly.
[0043]
In addition, an apparatus using an agglomerator with a space in the upper part of the container and passing the pollutant liquid from the lower part to the upper part is less likely to clog the agglomerator, and also improves the operating efficiency of the apparatus for purifying while circulating the liquid. I can plan.
[Brief description of the drawings]
FIG. 1 is a diagram showing an embodiment of the method and apparatus of the present invention. FIG. 2 is a cross-sectional view showing an example of an aggregator used in the apparatus of the present invention. Description of reference numerals 1 Coolant liquid supply device 2 Tank 3 Pump 4 Machine tool 10 Suspended particle aggregating device 11a, 11b Pump 12 Aggregator 12a Container 12b Aggregating agent 12c Space 12d, 12e Screen 13 Filtration device 13a Strip filter 13b Feeder 13c Scraper 13d Tank

Claims (6)

負に帯電した粒子を含む汚濁液中に陽イオンを供給して液中の懸濁粒子を凝集させ、さらに、凝集粒子を油分に接触させてフィルタで漉し取る懸濁粒子の凝集方法。A method for aggregating suspended particles in which a cation is supplied to a contaminated liquid containing negatively charged particles to agglomerate suspended particles in the liquid, and the aggregated particles are contacted with oil to be rubbed with a filter. 前記油分を予めフィルタに付着させ、このフィルタに陽イオン供給後の汚濁液を通す請求項1記載の懸濁粒子の凝集方法。The method for agglomerating suspended particles according to claim 1, wherein the oil is attached to a filter in advance, and the lysate after supplying cations is passed through the filter. 陽イオンを流出させた汚濁液中に油分を添加し、その後、汚濁液をフィルタに通す請求項1記載の懸濁粒子の凝集方法。The method for agglomerating suspended particles according to claim 1, wherein an oil is added to the contaminated liquid from which the cation has flowed out, and then the contaminated liquid is passed through a filter. 負に帯電した粒子を含む汚濁液を通過させてこの汚濁液中に陽イオンを流出させる凝集器と、油分をしみ込ませたフィルタで汚濁液中の凝集粒子を漉し取る濾過器とを備えている懸濁粒子凝集装置。It is equipped with a coagulator that allows negatively charged particles containing particles to pass through and allows cations to flow out into the solution, and a filter that removes the aggregated particles in the solution using a filter soaked with oil. Suspended particle aggregator. 前記フィルタとしてペーパフィルタを用い、このペーパフィルタを送りをかけて濾過部に連続的または間欠的に供給しながら濾過を行う請求項4記載の懸濁粒子凝集装置。The suspended particle aggregating apparatus according to claim 4, wherein a paper filter is used as the filter, and filtration is performed while feeding the paper filter continuously or intermittently to the filtration unit. 前記凝集器として、陽イオンを発生させる凝集剤を容器に収納し、その凝集剤の上部において容器の内部に空間を形成し、容器の下部から導入した汚濁液を前記凝集剤に接触させて通過させ、前記空間を経て容器の上部から流出させるものを用いた請求項4または5に記載の懸濁粒子凝集装置。As the aggregator, a flocculating agent that generates cations is accommodated in a container, a space is formed inside the container at the upper part of the aggregating agent, and a contaminant introduced from the lower part of the container is brought into contact with the aggregating agent and passes therethrough. The suspended particle agglomeration apparatus according to claim 4 or 5, wherein a device that flows out from the upper part of the container through the space is used.
JP2002336043A 2002-11-20 2002-11-20 Flocculating method and apparatus for suspended particle Pending JP2004167372A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1741679A2 (en) 2005-07-06 2007-01-10 Peter Schöndorfer Process for improving the supply of calcium and magnesium in biological wastewater treatment plant
JP2011115911A (en) * 2009-12-04 2011-06-16 Toyota Central R&D Labs Inc Method and device for preventing functional degradation of water-soluble processing liquid
CN110614586A (en) * 2018-06-20 2019-12-27 北京铂阳顶荣光伏科技有限公司 Cooling water circulation system and application method thereof

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1741679A2 (en) 2005-07-06 2007-01-10 Peter Schöndorfer Process for improving the supply of calcium and magnesium in biological wastewater treatment plant
EP1741679A3 (en) * 2005-07-06 2008-07-30 Peter Schöndorfer Process for improving the supply of calcium and magnesium in biological wastewater treatment plant
JP2011115911A (en) * 2009-12-04 2011-06-16 Toyota Central R&D Labs Inc Method and device for preventing functional degradation of water-soluble processing liquid
CN110614586A (en) * 2018-06-20 2019-12-27 北京铂阳顶荣光伏科技有限公司 Cooling water circulation system and application method thereof

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