JPH0788478A - Wastewater treatment method - Google Patents

Wastewater treatment method

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Publication number
JPH0788478A
JPH0788478A JP5236359A JP23635993A JPH0788478A JP H0788478 A JPH0788478 A JP H0788478A JP 5236359 A JP5236359 A JP 5236359A JP 23635993 A JP23635993 A JP 23635993A JP H0788478 A JPH0788478 A JP H0788478A
Authority
JP
Japan
Prior art keywords
pva
polymethacrylic acid
wastewater
complex
water
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
JP5236359A
Other languages
Japanese (ja)
Other versions
JP3266711B2 (en
Inventor
Hitoshi Maruyama
均 丸山
Hirotoshi Miyazaki
弘年 宮崎
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.)
Kuraray Co Ltd
Original Assignee
Kuraray 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 Kuraray Co Ltd filed Critical Kuraray Co Ltd
Priority to JP23635993A priority Critical patent/JP3266711B2/en
Publication of JPH0788478A publication Critical patent/JPH0788478A/en
Application granted granted Critical
Publication of JP3266711B2 publication Critical patent/JP3266711B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Addition Polymer Or Copolymer, Post-Treatments, Or Chemical Modifications (AREA)

Abstract

PURPOSE:To carry out wastewater treatment efficiently by a flocculating and precipitating method in which polymethacrylic acid in a prescribed wt.% based on the content of polyvinyl alcohol is added to wastewater whose pH is adjusted to be a prescribed pH value and polyvinyl alcohol is flocculated and precipitated. CONSTITUTION:Wastewater is adjusted to be pH 3.5-6.5 and polymethacrylic acid in 0.1-400wt.% based on the content of polyvinyl alcohol(PVA) is added to the wastewater. Consequently, PVA at a low concentration in the wastewater is reacted with polymethacrylic acid to produce PVA-polymethacrylic acid complex, which is a water-insoluble precipitating complex, and to flocculate and precipitate the complex. In the case pH is lower than 3.5, even if the complex is produced, the complex does not have a water-insoluble structure. Also, in the case pH is 6.5 or higher, polymethacrylic acid becomes an alkaline salt and the water-insoluble complex is hardly produced, though that depends on the concentration of PVA in the wastewater.

Description

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

【0001】[0001]

【産業上の利用分野】本発明はポリビニルアルコールを
含有する排水処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a wastewater treatment method containing polyvinyl alcohol.

【0002】[0002]

【従来の技術】ポリビニルアルコール(以下PVAと略
称する。)は経糸糊剤、各種バインダー、接着剤、紙や
布の表面処理剤、硬仕上げ剤などに広く使用されてお
り、他に類を見ない優れたフィルム強度とタフネスを有
した水溶性高分子として知られている。これらの使用分
野によっては、一度使用されたPVAを、再度、水に溶
解して使用する場合がある。例えば経糸糊付けした織布
の糊抜きを行う場合、紙や不織布を再使用する為に再生
処理時に再度、水に溶解する場合などである。これらの
排水中に溶解したPVAの処理方法としては、活性汚泥
法が一般に用いられているが、特定の資化菌を用いて処
理する必要があることから、処理費用が高く、かつ広い
処理面積が必要である。他の排水処理方法としては、凝
集沈澱法が一般によく用いられているが、1%以下の薄
い濃度のPVAを凝集沈澱させる薬剤がないことから、
処理できないのが現状であった。またPVAを保護コロ
イド剤として用いた水性エマルジョン、例えば酢酸ビニ
ルエマルジョン、アクリルエマルジョン、エチレン−酢
酸ビニル共重合体エマルジョン等の排水処理についても
凝集沈降法が非常に困難であった。
2. Description of the Related Art Polyvinyl alcohol (hereinafter referred to as PVA) is widely used as a warp sizing agent, various binders, adhesives, surface treatment agents for paper and cloth, hard finishing agents, etc. Not known as a water-soluble polymer with excellent film strength and toughness. Depending on the field of use, PVA used once may be used again after being dissolved in water. For example, when desizing a woven fabric with warp glue, it is necessary to re-dissolve it in water at the time of a recycling process in order to reuse paper or nonwoven fabric. The activated sludge method is generally used as a method for treating PVA dissolved in these wastewaters, but it requires treatment with a specific assimilating bacterium, resulting in high treatment cost and a wide treatment area. is necessary. As another wastewater treatment method, the coagulation-sedimentation method is generally used, but since there is no agent that coagulates and precipitates PVA in a thin concentration of 1% or less,
The current situation is that it cannot be processed. The coagulation-sedimentation method is also very difficult for wastewater treatment of aqueous emulsions using PVA as a protective colloid agent, such as vinyl acetate emulsions, acrylic emulsions, and ethylene-vinyl acetate copolymer emulsions.

【0003】[0003]

【発明が解決しようとする課題】本発明の目的は、従
来、PVAを含有する排水の処理方法としては使用する
ことが不可能であった凝集沈澱方法を用いて、より安価
で効率の良いPVAを含有する排水処理方法を提供する
ものである。
DISCLOSURE OF THE INVENTION The object of the present invention is to use a coagulating sedimentation method, which has hitherto been impossible to be used as a method for treating wastewater containing PVA, to make the PVA cheaper and more efficient. The present invention provides a wastewater treatment method containing

【0004】[0004]

【課題を解決するための手段】本発明者らはかかる現状
に鑑み、鋭意検討した結果、排水中のPVAを凝集沈降
法により処理する方法として、ポリメタクリル酸をPV
Aの含有量に対して0.1〜400重量%を添加してポ
リビニルアルコールを凝集沈降させることを特徴とする
PVAを含有する排水の処理方法を見出したものであ
る。すなわち、本発明に使用するポリメタクリル酸は排
水中の非常に希薄な濃度のPVAと反応してPVA−ポ
リメタクリル酸の複合体を生じ、水に不溶な沈降物を生
じ、PVAを水中から分離しうることを見出し本発明に
至ったものである。
DISCLOSURE OF THE INVENTION As a result of intensive studies in view of the present situation, the present inventors have found that polymethacrylic acid is used as a method for treating PVA in wastewater by a coagulation sedimentation method.
The present invention has found a method for treating wastewater containing PVA, which is characterized by adding 0.1 to 400% by weight to the content of A to coagulate and precipitate polyvinyl alcohol. That is, the polymethacrylic acid used in the present invention reacts with a very dilute concentration of PVA in the waste water to form a PVA-polymethacrylic acid complex, which produces a water-insoluble precipitate, which separates PVA from water. The present invention has been found to be possible and has led to the present invention.

【0005】ポリメタクリル酸とPVAの複合体を生成
せしめ有効にPVAを分離するためには、排水中のpH
が3.5〜6.5であり、好ましくは4.0〜6.0が
よい。pHが3.5より小さいとポリメタクリル酸より
強酸が多く存在していることになり、複合体が生成して
も水の不溶性の構造を取りえず、分離が不十分になるこ
とが多い。またpHが6.5よりも大きい場合には排水
中のPVAの濃度にもよるが、ポリメタクリル酸がアル
カリ性の塩になり、水不溶性の複合体を作ることが困難
となる。pHの調整方法としては、排水処理において一
般に行われている方法で良い。pH調整する時期につい
ては、特に制限はないが、ポリメタクリル酸を添加する
前あるいはポリメタクリル酸と同時に添加することが好
ましい。但し、PVAとポリメタクリル酸とが水不溶性
の複合体を生成した後は、pH値が上記範囲以外になっ
ても該複合体が壊れず、PVAが水溶性に変化しないこ
とから、pHの範囲は自由に取り得る。
In order to form a complex of polymethacrylic acid and PVA and effectively separate PVA, the pH in the waste water is adjusted.
Is 3.5 to 6.5, and preferably 4.0 to 6.0. When the pH is less than 3.5, more strong acid is present than polymethacrylic acid, and even if a complex is formed, the insoluble structure of water cannot be taken and separation is often insufficient. When the pH is higher than 6.5, polymethacrylic acid becomes an alkaline salt, which makes it difficult to form a water-insoluble complex, depending on the concentration of PVA in the wastewater. As a method for adjusting the pH, a method generally used in wastewater treatment may be used. The timing of pH adjustment is not particularly limited, but it is preferable to add it before or at the same time as polymethacrylic acid is added. However, after forming a water-insoluble complex of PVA and polymethacrylic acid, the complex does not break even if the pH value is out of the above range, and the PVA does not change to be water-soluble. Can be taken freely.

【0006】本発明で使用するポリメタクリル酸はメタ
クリル酸を単独重合したものが好ましく、場合によって
は少量の他の単量体との共重合体でもよい。しかし、他
の単量体の共重合割合は10モル%以下であることが好
ましい。ポリメタクリル酸の分子量は特に限定はない
が、数平均重合度で100〜10000であり、好まし
くは200〜2000である。ポリメタクリル酸の分子
量が100より小さいと、PVAとの強固な複合体が生
成しにくく、10000より大きい場合にはポリメタク
リル酸の製造が困難であり、水溶液での取扱いが難し
く、複合体の生成速度も非常に遅いものになる。ポリメ
タクリル酸の使用形態としては、特に制限はなく、固体
状態、微粉末状のもの、水溶液、あるいは他の担体等に
吸着しているものを使用してもよいが、一般的には一定
の濃度の溶液にして添加する。ポリメタクリル酸のPV
Aに対する添加量はPVAの含有量に対して0.1〜4
00重量%であり、さらに好ましくは10〜200重量
%である。ポリメタクリル酸の添加量が0.1重量%よ
りも小さい場合には水不溶性の複合体を生成しないため
使用できず、また400重量%よりも大の場合でも強固
な水不溶体性の複合体の生成が困難なため使用できな
い。
The polymethacrylic acid used in the present invention is preferably a homopolymer of methacrylic acid, and in some cases, it may be a copolymer with a small amount of another monomer. However, the copolymerization ratio of the other monomer is preferably 10 mol% or less. The molecular weight of polymethacrylic acid is not particularly limited, but the number average degree of polymerization is 100 to 10,000, and preferably 200 to 2,000. When the molecular weight of polymethacrylic acid is less than 100, it is difficult to form a strong complex with PVA, and when it is more than 10,000, it is difficult to produce polymethacrylic acid, and it is difficult to handle it in an aqueous solution, thus forming a complex. The speed will also be very slow. The use form of polymethacrylic acid is not particularly limited, and may be a solid state, a fine powder, an aqueous solution, or one adsorbed on another carrier, etc., but generally it is fixed. Add a solution having a concentration. PV of polymethacrylic acid
The amount of addition to A is 0.1 to 4 with respect to the content of PVA.
It is 00% by weight, and more preferably 10 to 200% by weight. When the amount of polymethacrylic acid added is less than 0.1% by weight, it cannot be used because it does not form a water-insoluble complex, and even when it is more than 400% by weight, it is a strong water-insoluble complex. Cannot be used because it is difficult to generate.

【0007】排水中のPVAについては特に限定はな
く、どのようなPVAであっても処理可能である。例え
ばPVAとしては、重合度100〜10000および鹸
化度20〜100モル%の範囲のPVA、さらには無変
性のPVA、カルボキシル基変性PVA、スルホン酸変
性PVA、カチオン変性PVA、疎水基を導入したPV
Aやその他種々の変性PVAが本発明の対象になる。ま
たPVA単独ばかりでなくPVAを保護コロイド剤とし
て用いた水性エマルジョン、例えば酢酸ビニルエマルジ
ョン、アクリルエマルジョン、エチレン−酢酸ビニル共
重合体エマルジョン等の排水処理についても本発明の凝
集沈澱方法による排水処理方法が取り得る。これらのエ
マルジョンの場合、添加するポリメタクリル酸の量は、
エマルジョンの重量濃度に対する量でなく含まれるPV
Aの量に対して加える必要があり、PVAの含有量に対
して0.1〜400重量%を添加して処理する必要があ
る。但し一般的にはエマルジョン中のPVAの量が不明
の場合が多く、通常エマルジョンの固形分に対して5〜
50重量%を最適添加量とすれば良い。
The PVA in the waste water is not particularly limited, and any PVA can be treated. For example, as PVA, a PVA having a polymerization degree of 100 to 10,000 and a saponification degree of 20 to 100 mol%, further, unmodified PVA, carboxyl group-modified PVA, sulfonic acid-modified PVA, cation-modified PVA, and PV having a hydrophobic group introduced therein.
A and various other modified PVA are the subject of the present invention. Further, not only PVA alone but also an aqueous emulsion using PVA as a protective colloid agent, for example, vinyl acetate emulsion, acrylic emulsion, ethylene-vinyl acetate copolymer emulsion, etc., is treated by the coagulating sedimentation method of the present invention. Can be taken. For these emulsions, the amount of polymethacrylic acid added is
PV contained not in amount based on weight concentration of emulsion
It is necessary to add it to the amount of A, and it is necessary to add 0.1 to 400% by weight to the content of PVA for treatment. However, in general, the amount of PVA in the emulsion is often unknown, and it is usually 5 to the solid content of the emulsion.
The optimum addition amount may be 50% by weight.

【0008】本発明の排水処理方法は排水中のPVAと
ポリメタクルリ酸との反応で水不溶性の複合体を生成さ
せて、PVAを水中から分離する事を目的に行うもので
あるが、PVAの排水中の濃度、PVAとポリメタクリ
ル酸の配合割合、その他の排水中の混入物およびその他
の種々の要因で生成した水不溶性の複合体が小さくなり
沈降分離が遅い場合もあり、このような場合には一般に
使用されている無機凝集剤を併用することによってより
大きな複合体が得られる場合がある。本発明で使用でき
る無機凝集剤としては、例えば硫酸アルミニウム(硫酸
バンド)、ポリ塩化アルミニウム(PAC)、塩化アル
ミニウム、塩化第二鉄、ポリ硫酸第二鉄、硫酸第二鉄、
硫酸第一鉄等が挙げられる。これらの無機凝集剤は一般
には水溶液で使用されることが多いが、本発明の場合、
水溶液の状態だけでなく固体の状態の無機凝集剤でもよ
い。また無機凝集剤は一種または二種以上を混合して使
用することもできる。無機凝集剤は排水中のPVAとポ
リメタクリル酸との反応物が生成された後に添加するこ
とが望ましい。しかし排水のpHの調整にこれらの凝集
剤の水溶液を用いて行うことも可能であり、添加の順序
は特に制限されない。さらにPVAを含む水不溶性の複
合体をより大きな粒子にして、水との分離を効率良く行
わせる為に、状況によっては高分子凝集剤も使用するこ
とができる。高分子凝集剤としては、ポリアクリル酸ナ
トリウム、ポリアクリルアミド、この部分加水分解物、
またはこれにカチオン基を導入したもの、ポリエチレン
オキシド等である。一般には水溶液で使用されることが
多く、固体状で添加されることは希であるが、本発明の
場合、水溶液の状態だけでなく固体の状態の無機凝集剤
でもよい。高分子凝集剤は一種または二種以上を混合し
て使用することもできる。
The wastewater treatment method of the present invention is carried out for the purpose of separating a PVA from water by forming a water-insoluble complex by the reaction between PVA in the wastewater and polymethacryl acid. The concentration of PVA and polymethacrylic acid, the content of PVA and polymethacrylic acid, other contaminants in the waste water, and other water-insoluble complexes formed due to various other factors may become smaller and sedimentation may be slower. In some cases, a larger composite may be obtained by using a commonly used inorganic flocculant together. Examples of the inorganic coagulant that can be used in the present invention include aluminum sulfate (sulfuric acid band), polyaluminum chloride (PAC), aluminum chloride, ferric chloride, polyferric sulfate, ferric sulfate,
Ferrous sulfate etc. are mentioned. These inorganic coagulants are generally used in an aqueous solution, but in the case of the present invention,
Not only an aqueous solution but also a solid state inorganic coagulant may be used. The inorganic coagulants may be used alone or in combination of two or more. The inorganic coagulant is preferably added after the reaction product of PVA and polymethacrylic acid in the waste water is formed. However, the pH of the waste water can be adjusted by using an aqueous solution of these coagulants, and the order of addition is not particularly limited. Furthermore, in order to make the water-insoluble complex containing PVA into larger particles and to efficiently separate it from water, a polymer flocculant can also be used depending on the situation. As the polymer flocculant, sodium polyacrylate, polyacrylamide, a partial hydrolyzate thereof,
Alternatively, a cation group-introduced product, polyethylene oxide or the like is used. In general, it is often used as an aqueous solution and rarely added as a solid, but in the case of the present invention, not only an aqueous solution but also an inorganic coagulant in a solid state may be used. The polymer flocculants may be used alone or in combination of two or more.

【0009】排水処理の装置としては、一般的に使用さ
れている装置を使用することができ、特に新しい機構を
備える必要はない。以下、一般的な処理装置と処理方法
について述べるが、これに限定されるものではない。従
来から通常使用されている連続凝集処理装置はpH計と
急速攪拌機を備えた混和槽と緩速攪拌機を備えた凝集槽
からなっている。混和槽にはpH調整液を定量供給する
定量ポンプが設けられ、凝集槽にはポリメタクリル酸の
水溶液を定量供給する定量ポンプと、場合によっては無
機凝集剤や高分子凝集剤の供給ポンプが備えつけられて
いる。PVA(PVAを保護コロイドにしたエマルジョ
ンを含む)を含有する排水が、定量ポンプによって定量
注入される。pH調整液がpH計の制御下に一定のpH
になるまで供給されて、混合される。この排水は次いで
凝集槽に送られ、ここでポリメタクリル酸を一定量供給
して水不溶性の複合体を生成させる。さらに必要に応じ
て、無機凝集剤や高分子凝集剤を一定量添加してより大
きな凝集フロックに成長させる。生成された凝集フロッ
クは、必要に応じてさらに沈澱槽、浮上分離槽または濃
縮スクリーン等へ供給され、凝集フロックが分離され
る。この連続処理装置ばかりでなく、一槽でバッチ式で
処理する方法でもよく、ポリメタクリル酸の添加につい
ても凝集槽で添加する方法のほかに、混合槽で混合した
後、凝集槽へ送液する方法でもよい。
As an apparatus for treating waste water, an apparatus which is generally used can be used, and it is not necessary to provide a new mechanism. Hereinafter, a general processing apparatus and a general processing method will be described, but the present invention is not limited thereto. A continuous flocculation apparatus usually used conventionally comprises a mixing tank equipped with a pH meter and a quick stirrer, and a flocculation tank equipped with a slow stirrer. The mixing tank is equipped with a metering pump that supplies a fixed amount of pH adjusting solution, and the coagulation tank is equipped with a metering pump that supplies a fixed amount of an aqueous solution of polymethacrylic acid and, in some cases, an inorganic coagulant or polymer coagulant supply pump. Has been. Waste water containing PVA (including emulsion of PVA as protective colloid) is metered by a metering pump. The pH adjustment liquid has a constant pH under the control of the pH meter.
Are fed and mixed until. This waste water is then sent to a flocculation tank where a fixed amount of polymethacrylic acid is fed to form a water-insoluble complex. If necessary, a fixed amount of an inorganic coagulant or a polymer coagulant is added to grow larger floc. The agglomerated flocs thus produced are further supplied to a settling tank, a floating separation tank, a concentration screen or the like, if necessary, to separate the agglomerated flocs. Not only this continuous treatment device, but also a method of performing batch treatment in a single tank may be used. In addition to the method of adding polymethacrylic acid in the coagulation tank, after mixing in the mixing tank, liquid is fed to the coagulation tank. It may be a method.

【0010】[0010]

【実施例】以下に実施例を挙げて本発明をさらに詳しく
説明するが、本発明はこれによって限定されるものでは
ない。尚、実施例中等に断りのないかぎり、「%」およ
び「部」は重量基準を表す。
The present invention will be described in more detail with reference to the following examples, but the present invention is not limited thereto. Unless otherwise specified in the examples, "%" and "parts" are based on weight.

【0011】実施例1 CODが165〜205mg/lのPVAを含む排水
を、pH計と急速攪拌装置を有する混和槽と緩速攪拌機
を有する凝集槽、および沈澱槽からなる連続処理装置を
用いて排水処理を行った。混和槽にはさらにpH調整液
を定量供給できる定量ポンプを備え、凝集槽には重合度
1260のポリメタクリル酸の10%水溶液を供給でき
る定量ポンプと、無機凝集剤の水溶液と高分子凝集剤を
供給できる3つの定量ポンプが設けられている。この凝
集分離工程で処理された処理水は沈澱槽に送液される。
流入する排水のpHは7.2であり、混和槽に供給する
pH調整液としては硫酸バンドの水溶液を用い、排水の
pHが5.0になるようにpH計で流量を制御した。ま
た凝集槽に備え付けた高分子凝集剤はアニオン系高分子
凝集剤「アロンフロック」(東亜合成(株)製)を使用
した。薬剤使用量と凝集分離工程における流入水質と処
理水質を表1および表2に示す。この処理によりPVA
とポリメタクリル酸は水不溶性の複合体フロックを生成
し、沈澱槽の底に凝集沈澱した。
Example 1 Waste water containing PVA having a COD of 165 to 205 mg / l was treated with a continuous treatment device comprising a mixing tank having a pH meter and a rapid stirring device, a coagulation tank having a slow stirring device, and a precipitation tank. Wastewater treatment was performed. The mixing tank is further equipped with a quantitative pump capable of quantitatively supplying the pH adjusting liquid, and the aggregation tank is provided with a quantitative pump capable of supplying a 10% aqueous solution of polymethacrylic acid having a degree of polymerization of 1260, an aqueous solution of an inorganic flocculant and a polymer flocculant. There are three metering pumps that can be supplied. The treated water treated in this coagulation / separation step is sent to the settling tank.
The pH of the inflowing wastewater was 7.2, and an aqueous solution of sulfuric acid band was used as the pH adjusting liquid supplied to the mixing tank, and the flow rate was controlled by a pH meter so that the pH of the wastewater was 5.0. As the polymer flocculant provided in the flocculation tank, an anionic polymer flocculant "Aron Floc" (manufactured by Toagosei Co., Ltd.) was used. Tables 1 and 2 show the amount of chemicals used and the inflow water quality and treated water quality in the coagulation separation process. By this treatment, PVA
And polymethacrylic acid produced water-insoluble complex flocs, which coagulated and settled at the bottom of the settling tank.

【0012】比較例1 実施例1でポリメタクリル酸を使用しない他は、実施例
1と同様にして処理を行った。その結果を表1および表
2に示す。ポリメタクリル酸を使用しない場合はPVA
は凝集沈澱せず、CODの低下もほとんど見られなかっ
た。
Comparative Example 1 The same treatment as in Example 1 was carried out except that polymethacrylic acid was not used in Example 1. The results are shown in Tables 1 and 2. PVA when polymethacrylic acid is not used
Did not aggregate and precipitate, and almost no reduction in COD was observed.

【0013】実施例2 実施例1の排水を処理するにあたり、硫酸水でpHを
4.5に調整し、ポリメタクリル酸を320mg/l使
用した他は、他の凝集剤を添加せず実施例1と同様にし
て処理を行ったところPVAとポリメタクリル酸の複合
体フロックはやや小さかったが、問題なく凝集沈澱し
た。結果を表1および表2に示す。
Example 2 In treating the wastewater of Example 1, the pH was adjusted to 4.5 with sulfuric acid water, and 320 mg / l of polymethacrylic acid was used, and no other coagulant was added. When the treatment was carried out in the same manner as in No. 1, the complex floc of PVA and polymethacrylic acid was slightly small, but coagulated and precipitated without problems. The results are shown in Tables 1 and 2.

【0014】実施例3 実施例1の排水を硫酸水でpHを5.3に調整した後、
ポリメタクリル酸を160mg/l、無機凝集剤として
塩化鉄を70mg/l、実施例1で使用した高分子凝集
剤を1.30mg/l使用した他は、実施例1と同様に
して処理を行った。結果を表1および表2に示す。
Example 3 After adjusting the pH of the wastewater of Example 1 to 5.3 with sulfuric acid water,
Treatment was performed in the same manner as in Example 1 except that polymethacrylic acid was 160 mg / l, iron chloride was 70 mg / l as the inorganic coagulant, and the polymer coagulant used in Example 1 was 1.30 mg / l. It was The results are shown in Tables 1 and 2.

【0015】実施例4 PVAを保護コロイドに用いたエチレン−酢酸ビニル共
重合体エマルジョン(株式会社クラレ製、OM#400
0)の排水を表1の処理条件で実施例1と同様にして行
った。結果を表1および表2に示す。
Example 4 Ethylene-vinyl acetate copolymer emulsion using PVA as a protective colloid (Kuraray Co., Ltd., OM # 400)
The drainage of 0) was performed under the treatment conditions of Table 1 in the same manner as in Example 1. The results are shown in Tables 1 and 2.

【0016】[0016]

【表1】 [Table 1]

【0017】[0017]

【表2】 [Table 2]

【0018】[0018]

【発明の効果】本発明によると、従来は不可能であった
PVAの希薄水溶液から、安価でかつ効率よく、PVA
を沈澱させることが可能である。
According to the present invention, PVA can be produced inexpensively and efficiently from a dilute aqueous solution of PVA which has been impossible in the past.
Can be precipitated.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 排水のpHを3.5〜6.5に調整し、
ポリメタクリル酸をポリビニルアルコールの含有量に対
して0.1〜400重量%を添加してポリビニルアルコ
ールを凝集沈降させることを特徴とするポリビニルアル
コールを含有する排水の処理方法。
1. The pH of the wastewater is adjusted to 3.5 to 6.5,
A method for treating waste water containing polyvinyl alcohol, comprising adding 0.1 to 400% by weight of polymethacrylic acid to the content of polyvinyl alcohol to coagulate and precipitate the polyvinyl alcohol.
JP23635993A 1993-09-22 1993-09-22 Wastewater treatment method Expired - Fee Related JP3266711B2 (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103420464A (en) * 2012-05-15 2013-12-04 株式会社日立制作所 Composite agglomerant solution for water treatment, and water treatment device and method using the same

Citations (14)

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JPS4841548A (en) * 1971-10-02 1973-06-18
JPS4979982A (en) * 1972-12-08 1974-08-01
JPS49116857A (en) * 1973-03-12 1974-11-08
JPS5173756A (en) * 1974-12-20 1976-06-25 Shikibo Ltd Suiyoekikara horibiniruarukooruo bunrisuruhoho
JPS51146751A (en) * 1975-06-11 1976-12-16 Hitachi Ltd Window fan
JPS51148257A (en) * 1975-06-12 1976-12-20 Hitachi Chem Co Ltd Treatment method for styrol resin suspension polymerized waste water h aving polyvinyl alchohol
JPS5218060A (en) * 1975-08-01 1977-02-10 Toyobo Co Ltd Method of treating polyvinyl alcohol-containing drainage
JPS5234547A (en) * 1975-09-12 1977-03-16 Toray Ind Inc Treating waste water containing polyvinyl alochol
JPS5241456A (en) * 1975-09-29 1977-03-31 Toyobo Co Ltd Method for treating waste water containing polyvinyl alcohol
JPS52146961A (en) * 1976-05-31 1977-12-07 Mitsubishi Electric Corp Process for treating waste water containing polyvinyl alcohol
JPS54119760A (en) * 1978-03-08 1979-09-17 Agency Of Ind Science & Technol Treatment method for waste water containing polyvinyl alcohol and/or starch
JPS5531471A (en) * 1978-08-29 1980-03-05 Kimura Kakoki Kk Treatment of vinyl acetate saponification process waste water
JPS5765382A (en) * 1980-10-08 1982-04-20 Agency Of Ind Science & Technol Purification of waste water containing polyvinyl alcohol and/or polysaccharide
JPS6161692A (en) * 1984-08-31 1986-03-29 Kurita Water Ind Ltd Treatment of water containing polyvinyl alcohol

Patent Citations (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4841548A (en) * 1971-10-02 1973-06-18
JPS4979982A (en) * 1972-12-08 1974-08-01
JPS49116857A (en) * 1973-03-12 1974-11-08
JPS5173756A (en) * 1974-12-20 1976-06-25 Shikibo Ltd Suiyoekikara horibiniruarukooruo bunrisuruhoho
JPS51146751A (en) * 1975-06-11 1976-12-16 Hitachi Ltd Window fan
JPS51148257A (en) * 1975-06-12 1976-12-20 Hitachi Chem Co Ltd Treatment method for styrol resin suspension polymerized waste water h aving polyvinyl alchohol
JPS5218060A (en) * 1975-08-01 1977-02-10 Toyobo Co Ltd Method of treating polyvinyl alcohol-containing drainage
JPS5234547A (en) * 1975-09-12 1977-03-16 Toray Ind Inc Treating waste water containing polyvinyl alochol
JPS5241456A (en) * 1975-09-29 1977-03-31 Toyobo Co Ltd Method for treating waste water containing polyvinyl alcohol
JPS52146961A (en) * 1976-05-31 1977-12-07 Mitsubishi Electric Corp Process for treating waste water containing polyvinyl alcohol
JPS54119760A (en) * 1978-03-08 1979-09-17 Agency Of Ind Science & Technol Treatment method for waste water containing polyvinyl alcohol and/or starch
JPS5531471A (en) * 1978-08-29 1980-03-05 Kimura Kakoki Kk Treatment of vinyl acetate saponification process waste water
JPS5765382A (en) * 1980-10-08 1982-04-20 Agency Of Ind Science & Technol Purification of waste water containing polyvinyl alcohol and/or polysaccharide
JPS6161692A (en) * 1984-08-31 1986-03-29 Kurita Water Ind Ltd Treatment of water containing polyvinyl alcohol

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103420464A (en) * 2012-05-15 2013-12-04 株式会社日立制作所 Composite agglomerant solution for water treatment, and water treatment device and method using the same

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