JPH0696149B2 - Method for treating suspension containing metal hydroxide - Google Patents
Method for treating suspension containing metal hydroxideInfo
- Publication number
- JPH0696149B2 JPH0696149B2 JP63332174A JP33217488A JPH0696149B2 JP H0696149 B2 JPH0696149 B2 JP H0696149B2 JP 63332174 A JP63332174 A JP 63332174A JP 33217488 A JP33217488 A JP 33217488A JP H0696149 B2 JPH0696149 B2 JP H0696149B2
- Authority
- JP
- Japan
- Prior art keywords
- metal hydroxide
- suspension containing
- flocs
- zone
- polymer flocculant
- 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 - Lifetime
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- Separation Of Suspended Particles By Flocculating Agents (AREA)
Description
【発明の詳細な説明】 [産業上の利用分野] 本発明は、金属水酸化物を含む懸濁液、例えばメッキ工
場、電解研磨工場、アルマイト工場等の金属表面処理工
場より排出される廃水中に含まれる亜鉛・ニッケル・ア
ルミニウム・錫等の重金属イオンを除去する為に、苛性
ソーダ・炭酸ソーダ・消石灰・石灰石等の中和剤を反応
させて生成した、金属水酸化物の懸濁液から液中の金属
水酸化物を除去する固液分離プロセスに関するものであ
る。The present invention relates to a suspension containing a metal hydroxide, for example, waste water discharged from a metal surface treatment factory such as a plating factory, an electrolytic polishing factory, and an alumite factory. In order to remove heavy metal ions such as zinc, nickel, aluminum, tin, etc. contained in the liquid, a liquid from a suspension of metal hydroxide produced by reacting with a neutralizing agent such as caustic soda, sodium carbonate, slaked lime, limestone, etc. The present invention relates to a solid-liquid separation process for removing metal hydroxide contained therein.
[従来の技術] 従来より、懸濁物質を含む懸濁液から懸濁固形物を分離
処理する方法として、沈殿分離法、浮上分離法、濾過分
離法、吸着分離法などが知られている。[Prior Art] Conventionally, a precipitation separation method, a floatation separation method, a filtration separation method, an adsorption separation method, and the like are known as methods for separating a suspended solid substance from a suspension containing a suspended substance.
特に、金属水酸化物の様に比較的比重が重く、且つ排水
量が多い場合は、沈殿法(例えば昭和54年11月10日技報
堂出版株式会社発行の「固液分離技術」のP.95〜98)が
最も安価で安定した処理が期待できるため、一般に良く
利用されている。In particular, when the specific gravity is relatively heavy like metal hydroxides and the amount of discharged water is large, the precipitation method (for example, P.95- "of" solid-liquid separation technology "issued by Gihodo Publishing Co., Ltd. on November 10, 1979) Since 98) is expected to be the cheapest and stable treatment, it is commonly used.
しかし、亜鉛、アルミ、錫、鉄等の金属イオンと苛性ソ
ーダ、消石灰との反応により生成した金属水酸化物フロ
ックは、そのままでは沈降性が悪く固液分離が困難なた
め、有機高分子凝集剤を添加して、更にフロックを大型
にして、沈降速度を促進させる方法がとられている。However, metal hydroxide flocs produced by the reaction of metal ions such as zinc, aluminum, tin, and iron with caustic soda and slaked lime have poor sedimentation property and solid-liquid separation is difficult as it is. A method is employed in which the flocs are added to increase the size of the flocs to accelerate the sedimentation rate.
しかしながら、このような方法で生成するフロックはみ
かけの粒子径は大きいが、粒子同志の結合が緩く、内部
に大量の水を包含しているため、密度が小さくみかけの
粒子径ほど沈降速度の上昇は期待できない。又、濃縮性
・脱水性も良くない。However, although the flock generated by such a method has a large apparent particle size, the particles are loosely bound to each other and a large amount of water is contained inside, so the density is small and the apparent particle size increases the sedimentation rate. Can't expect. Also, the concentration and dehydration are not good.
[発明が解決しようとする課題] 本発明は、従来の凝集沈殿フロックとは根本的に性質の
異なる緻密で、結合力が強く、高密度なフロックを形成
することにより、従来の凝集沈殿法の沈降速度よりも数
倍沈降速度を高めるとともに、従来必要とされている凝
集沈殿の後に仕上げとして用いられている濾過工程をも
省略できるほど、凝集分離処理の処理効率、安定性を高
め、且つ濃縮性・脱水性の良好なスラッジを同時に生成
する固液分離方法を提供することを目的としたものであ
る。[Problems to be Solved by the Invention] The present invention provides a dense floc having a property fundamentally different from that of a conventional flocculation-precipitation floc, a strong binding force, and a high-density floc to form. In addition to increasing the sedimentation speed several times faster than the sedimentation speed, the efficiency and stability of the coagulation separation treatment can be increased and the concentration can be increased so that the filtration step used as a finishing process after the coagulation sedimentation that is conventionally required can be omitted. It is an object of the present invention to provide a solid-liquid separation method for simultaneously producing sludge having good properties and dehydration properties.
[課題を解決するための手段、作用] 一般に金属水酸化物は、正に荷電しているため、アニオ
ン系高分子凝集剤の添加により、荷電中和と吸着架橋の
作用が働き、フロックを形成する。[Means and Actions for Solving Problems] In general, metal hydroxides are positively charged. Therefore, the addition of an anionic polymer flocculant causes the action of charge neutralization and adsorption crosslinking to form flocs. To do.
発明者らは、上記に示す様な従来の凝集フロックとは、
性質の異なる緻密で結合力が強く、高密度なフロックを
作るため、アニオン系高分子凝集剤の添加と同時に高炉
水砕スラグ微粉を添加し、数十秒急速撹拌し、粗大フロ
ックを形成する前にカチオン系高分子凝集剤を添加し
た。The inventors of the present invention, the conventional floc flocs as shown above,
Before forming coarse floc, add ionic fine-particle flocculant and blast furnace granulated slag fine powder at the same time as the addition of anionic polymer flocculant in order to create dense, strong and high-density floc with different properties. A cationic polymer flocculant was added to.
高炉水砕スラグ微粉は、アニオン系高分子凝集剤の作用
により形成されつつあるフロック中に取り込まれ、多数
の核を作る。Granulated blast furnace granulated slag is incorporated into the flocs that are being formed by the action of the anionic polymer flocculant and forms a large number of nuclei.
又、カチオン系高分子凝集剤の作用により、カチオン系
高分子凝集剤と金属水酸化物・高炉水砕スラグ微粉は吸
着架橋化し、同時にアニオン系高分子凝集剤と複雑な網
目構造を作る。Further, by the action of the cationic polymer flocculant, the cationic polymer flocculant and the metal hydroxide / blast furnace granulated slag fine powder are adsorbed and crosslinked, and at the same time, a complex network structure is formed with the anionic polymer flocculant.
カチオン系高分子凝集剤は、分子鎖中に多くの吸着活性
点を有する為、結合力の強いフロックができる。The cationic polymer flocculant has a large number of adsorption active sites in the molecular chain, and thus can form a floc having a strong binding force.
この時、金属水酸化物とカチオン系高分子凝集剤は、共
に正に荷電していることもあり、一部に分散現象が起こ
りフロックは小さくなる。At this time, both the metal hydroxide and the cationic polymer flocculant may be positively charged, so that a dispersion phenomenon occurs in part and the floc becomes small.
しかし、このフロックは非常に結合力の強いフロックで
あり、緩やかな撹乱により分子鎖が絡まりあい、緻密で
結合力の強い高密度なフロックを形成していく。However, this floc is a floc having a very strong binding force, and the molecular chains are entangled by a gentle disturbance to form a dense, high-density floc having a strong binding force.
この様なフロック群からなる液を更に、上向流で固液分
離槽に流入させる。The liquid composed of such floc groups is further made to flow into the solid-liquid separation tank in an upward flow.
固液分離槽内では、撹拌羽根がゆっくりと回転してお
り、ここで撹拌羽根とフロックが、又フロック同志が衝
突しあい、フロック内の水が放出される。又、転がり運
動により丸い締まったフロックを形成していく。In the solid-liquid separation tank, the stirring blade slowly rotates, where the stirring blade and the flocs collide with each other, and the water in the flocs is discharged. In addition, the rolling motion forms a round and tight flock.
この様にしてできたフロックは、径が1mmから3mmの非常
に良く締まったフロックであり、粒子径は小さいものの
高炉水砕スラグ微粉を核とする緻密なフロックである
為、密度が高く、従来の凝集沈殿法フロックに比べ、沈
降速度を10倍以上に高める事が可能になる。The flock made in this way is a very well-tightened flock with a diameter of 1 mm to 3 mm, and although it has a small particle size, it is a dense flock with granulated blast furnace granulated slag as its core, so it has a high density, It is possible to increase the sedimentation speed 10 times or more compared to the flocculation method of Flocc.
又、この固液分離槽内で形成されたフロック群はスラリ
ーとして間欠的或は、連続的に引き抜かれるが、このス
ラリーについても濃縮性、及び脱水性が、従来法に比べ
かなり良くなる。Further, the floc group formed in the solid-liquid separation tank is intermittently or continuously withdrawn as a slurry, and the concentration and dewatering property of this slurry are considerably better than those of the conventional method.
上記のフロックの核になる物質に関して詳述すると、例
えばベントナイトの様に高いコロイド状特性と高い膨潤
性及び給水性を有しているものは、乾燥体積の数倍以上
の水を吸収してしまい、フロックの径が大きくなる。Explaining in detail the substance that becomes the core of the above-mentioned floc, for example, a substance having high colloidal properties, high swelling property and water supply property such as bentonite will absorb water several times its dry volume or more. , The diameter of the flock becomes large.
このフロックは、水を内部に含有しているもののフロッ
ク径がかなり大きいため、沈降速度はかなり大きくな
る。しかし、脱水性はあまり良くなく、又、後述する様
な圧密濾過槽を形成しても、間隙が大きいため、未形成
フロックが流出してしまい、処理水質不安定の原因とな
る。又、マグネタイトの様に水酸化物となかなか馴染ま
ないものは、フロックの核となりにくく、添加剤として
は不適である。Although this floc contains water inside, the floc diameter is considerably large, so that the sedimentation velocity is considerably high. However, the dewatering property is not so good, and even if a compaction filtration tank as will be described later is formed, a large gap causes the unformed flocs to flow out, which causes unstable treated water quality. Further, those which are not easily compatible with hydroxide such as magnetite are not suitable as an additive because they hardly form nuclei of flocs.
そこで、発明者らは金属水酸化物と吸着架橋化してフロ
ックを形成するための核となる物質について種々テスト
を繰返し実施した結果、鉄鋼業の高炉から副産物として
発生する水砕スラグを粉砕分級した平均粒径が約50μの
水砕微粉が、最も効果的であることを見出した。Therefore, the inventors repeatedly carried out various tests on a substance serving as a nucleus for adsorbing and cross-linking with metal hydroxide to form flocs, and as a result, crushed and classified the granulated slag generated as a by-product from the blast furnace of the steel industry. It was found that granulated fine powder having an average particle size of about 50μ is the most effective.
この平均粒径が約50μ程度の高炉水砕微粉を用いると、
水砕は容易に金属水酸化物中に取り込まれ、フロックの
核となる。この水砕は、比重が2〜3と重く、形成フロ
ックの沈降速度を高めるのにも効果的で、且つ濃縮性・
脱水性も良好となる。Using this granulated blast furnace fine powder with an average particle size of about 50μ,
Water granules are easily incorporated into the metal hydroxide and become the nuclei of flocs. This water granulation has a high specific gravity of 2-3, is effective in increasing the sedimentation rate of the formed flocs, and has a high concentration property.
The dehydration property is also good.
スラリーゾーン内で、撹拌流動させる方法としては撹拌
羽根をゆっくりと回転させ、羽根とフロック及びフロッ
ク同志を衝突させフロック中の水を追い出し、且つ転が
り運動を生起させて丸いフロックを形成させ、脱水を助
長させていく方法であれば基本的には利用できる。As a method of stirring and flowing in the slurry zone, the stirring blade is slowly rotated, the blade and the floc and the floc are collided to expel the water in the floc, and a rolling motion is caused to form a round floc, and dehydration is performed. Basically, you can use any method that encourages you.
しかしながら、プロペラ型撹拌機の様に上下に対流運動
を起こすものは、脱水作用により緻密なフロックを形成
させることは困難である。However, it is difficult for a propeller-type stirrer, such as a propeller-type stirrer, which causes a convection motion in the vertical direction to form a fine floc by the dehydration action.
発明者らは、様々な形状の撹拌羽根を作り、実験を繰返
した結果、下記の撹拌羽根に到達した。The inventors have made stirring blades of various shapes and repeated experiments, and as a result, reached the following stirring blades.
まず、乱流運動を生起させる部分と、転がり運動を生起
させる部分に機能を分けた。First, the function was divided into the part that causes turbulent motion and the part that causes rolling motion.
つまり、羽根とフロック及びフロック同志が衝突し、脱
水作用の起こる部分が乱流運動を生起させる部分であ
り、規則正しい回転により、フロックを丸い形状にして
いく部分が、転がり運動を生起させる部分である。In other words, the part where the blades and the flocs collide with each other and the dehydration occurs is the part that causes the turbulent motion, and the part that makes the flocs round by regular rotation is the part that causes the rolling motion. .
スラッジブランケットゾーンへは、上向流で下部から原
水を流入させ、下部に乱流運動を生起させる格子状の羽
根を設置した。格子状の羽根とは、平板を組み合わせ断
面が格子状になる様にしたものである。Into the sludge blanket zone, grid-like blades were installed to cause raw water to flow from the lower part in an upward flow and to cause turbulent motion in the lower part. The lattice-shaped blade is a combination of flat plates and has a lattice-shaped cross section.
又、その上部には、2枚の平板を十字状に組み合わせた
十字羽根を設置した。Moreover, a cross blade, which is a combination of two flat plates in a cross shape, is installed on the upper portion thereof.
槽の深さが深くなればこの2種類の羽根を上部と下部に
分け、何枚も重ね合わせる事で対応する。又、2種類の
羽根は同じシャフトに固定され、同一の回転速度で回転
される。又、羽根の長さは槽の外周までとどかないが、
ある程度長い方が良い。If the depth of the tank becomes deep, these two types of blades are divided into the upper part and the lower part, and multiple blades can be stacked together. Further, the two types of blades are fixed to the same shaft and are rotated at the same rotation speed. Also, the length of the blade does not reach the outer circumference of the tank,
It is better to have a certain length.
本処理方式は、更にこのスラッジブランケットゾーン内
に於て、撹拌流動部つまり乱流と転がり運動を生起させ
る部分の上部に、圧密濾過部分を設けることで大きな効
果を持たせることができる。The present treatment system can have a great effect by providing a compaction filtration portion in the sludge blanket zone, above the stirring flow portion, that is, the portion that causes turbulent flow and rolling motion.
つまり、撹拌流動部でフロック同志の衝突、フロックと
羽根の衝突を繰返し、又転がし運動により形成された緻
密で結合力の強い、径1〜3mmのペレット状のフロック
は上向流により上部に押し出されるが、このフロック群
を更に撹拌運動のない部分に固定すると、固液分離が起
こり、界面を形成する。界面より上は、清澄な水で処理
水として放流される。In other words, in the agitation flow section, the flocs collide with each other, the flocs collide with the blades repeatedly, and the dense and strong binding pellets with a diameter of 1 to 3 mm formed by rolling motion are pushed upward by upward flow. However, if this floc group is further fixed to a portion where there is no stirring motion, solid-liquid separation occurs and an interface is formed. Above the interface, clear water is discharged as treated water.
又、界面より下の部分はスラッジブランケットゾーンと
なるが、ここでは撹拌運動のない所で圧密現象が起こ
る。この圧密された層は、径1〜3mmの緻密フロック群
であり、一種の濾過機能を有する。つまり、未形成フロ
ック、溶解重金属、SS等がこのフロックの間隙に捕捉さ
れる。Further, a portion below the interface becomes a sludge blanket zone, but here, a consolidation phenomenon occurs in a place where there is no stirring motion. This consolidated layer is a dense floc group having a diameter of 1 to 3 mm and has a kind of filtration function. That is, unformed flocs, molten heavy metals, SS, etc. are trapped in the gaps of these flocs.
或は、フロックに吸着され取り込まれる。Alternatively, it is adsorbed and taken into the floc.
従って、処理は非常に安定しており、通常凝集沈殿後の
二次処理として用いられている砂濾過等のプロセスも不
要となる。Therefore, the treatment is very stable, and the process such as sand filtration, which is usually used as the secondary treatment after coagulation and sedimentation, becomes unnecessary.
又、この圧密されたゾーンから引き抜かれるスラリー
は、スラリー濃度も高く、濃縮性も良い。Further, the slurry drawn out from this consolidated zone has a high slurry concentration and a good concentration property.
場合によっては、濃縮も不要となる。In some cases, concentration is also unnecessary.
又、その後の脱水性も良い。通常、メッキ液等の廃液を
凝集沈殿させたフロックは、脱水が困難でフィルタープ
レス等で脱水しないと含水率は80%以下にならない。It also has good dehydration properties. Usually, flocs formed by coagulating sedimentation of waste liquids such as plating solutions are difficult to dehydrate, and the water content does not fall below 80% unless dehydrated by a filter press or the like.
ところが、本プロセスにより生成したフロックは脱水が
容易で、簡易なベルトプレス等でも容易に脱水ができ、
含水率を80%以下にすることが可能である。However, the flocs produced by this process are easy to dehydrate, and can be easily dehydrated with a simple belt press.
It is possible to keep the water content below 80%.
従って、本発明により金属水酸化物を含む懸濁液を安定
して、効率的に処理することができる。Therefore, according to the present invention, a suspension containing a metal hydroxide can be treated stably and efficiently.
[実 施 例] 第1図に示す様に、電気亜鉛メッキ工場から発生する亜
鉛イオン110mg/、クロムイオン67mg/、鉄イオン17m
g/を含む廃液を消石灰でpHを11にあげ、中和してでき
た金属水酸化物を含む懸濁液1にポリアクリルアミド系
のアニオン系高分子凝集剤2を4mg/、平均粒径50μの
高炉水砕スラグ3を1000mg/加え、30秒間急速撹拌
し、その後、ポリアクリルアミド系のカチオン高分子凝
集剤4を2mg/加え、固液分離槽5に上向流で流入させ
た。[Example] As shown in Fig. 1, zinc ion 110 mg /, chromium ion 67 mg /, iron ion 17 m generated from the electrogalvanizing plant.
The pH of the waste liquid containing g / was raised to 11 with slaked lime, and 4 mg / of polyacrylamide type anionic polymer flocculant 2 was added to the suspension 1 containing the metal hydroxide obtained by neutralization, and the average particle size was 50μ. 1000 mg / g of granulated blast furnace slag 3 was added and rapidly stirred for 30 seconds, and then 2 mg / g of a polyacrylamide-based cationic polymer flocculant 4 was added and allowed to flow into the solid-liquid separation tank 5 in an upward flow.
固液分離槽では、下部に格子状の羽根を数枚重ね、上部
に十字状の羽根を数枚重ねた撹拌羽根6を有し、40rpm
で回転している。The solid-liquid separation tank has a stirring blade 6 having several lattice-shaped blades stacked on the lower part and several cross-shaped blades stacked on the upper part at 40 rpm.
Is spinning at.
尚、固液分離槽は、カラム径100mmで高さ400mmの塩ビカ
ラムを用いた。A PVC column having a column diameter of 100 mm and a height of 400 mm was used as the solid-liquid separation tank.
この固液分離槽に流入したフロック7は、カラム内で脱
水現象及び転がり運動が生起され、1〜3mmのペレット
状の緻密なフロックとなる。更に撹拌羽根上部では、圧
密現象も起こり、スラッジブランケットゾーンを作る。The flocs 7 that have flowed into the solid-liquid separation tank undergo a dehydration phenomenon and rolling motion in the column, and become pellet-like dense flocs of 1 to 3 mm. Further, a compaction phenomenon also occurs at the upper part of the stirring blade to form a sludge blanket zone.
このブランケットゾーンでは、10m/HrのOFRをとる事が
可能である。In this blanket zone, it is possible to obtain an OFR of 10 m / Hr.
このカラムで固液分離された清澄水は、上部から排出さ
れ、SS3mg/、鉄イオン0.1mg/、亜鉛イオン0.2mg/
、クロムイオン0.1mg/の非常に良好な処理水8とな
る。The clear water that was solid-liquid separated by this column was discharged from the top, and SS3mg /, iron ion 0.1mg /, zinc ion 0.2mg /
, Which is a very good treated water of chromium ion 0.1 mg /.
又、圧密部分が濾過機能を有する為、処理も安定してお
り、未形成フロックが浮いてしまうこともない。Further, since the consolidated portion has a filtering function, the treatment is stable and the unformed flocs do not float.
又、圧密ゾーンより引き抜かれたスラリー9は、容易に
リーフテストにかけられ、ケーキ含水率は80%とかなり
効率良く脱水ができる。Further, the slurry 9 pulled out from the compaction zone is easily subjected to the leaf test, and the cake water content is 80%, so that the water can be dehydrated quite efficiently.
[従来例] 本発明との比較のため、従来例として沈降促進剤として
用いられているベントナイトを添加した場合を以下に示
す。[Conventional Example] For comparison with the present invention, the case where bentonite used as a precipitation accelerator is added as a conventional example is shown below.
実施例と同様に電気亜鉛メッキ工場から発生する亜鉛イ
オン110mg/、クロムイオン67mg/、鉄イオン17mg/
を含む廃液を消石灰でpHを11にあげ、中和してできた金
属水酸化物を含む懸濁液1にポリアクリルアミド系のア
ニオン系高分子凝集剤2を4mg/、ベントナイトを1000
mg/加え、30秒間急速攪拌し、その後、ポリアクリル
アミド系のカチオン系高分子凝集剤4を2mg/加え、固
液分離槽5に上向流で流入させた。As in the example, zinc ions 110 mg /, chromium ions 67 mg /, iron ions 17 mg / generated from the electrogalvanizing plant.
The pH of the waste liquid containing slag is raised to 11 with slaked lime, 4 mg of polyacrylamide-based anionic polymer flocculant 2 and 1000 of bentonite are added to the suspension 1 containing metal hydroxide formed by neutralization.
mg / addition, followed by rapid stirring for 30 seconds, and then 2 mg / addition of polyacrylamide-based cationic polymer flocculant 4 was made to flow into the solid-liquid separation tank 5 in an upward flow.
固液分離槽では、下部に格子状の羽根を数枚重ね、上部
に十字状の羽根を数枚重ねた攪拌羽根6を有し、40rpm
で回転している。The solid-liquid separation tank has a stirring blade 6 having several lattice-shaped blades stacked on the lower part and several cross-shaped blades stacked on the upper part at 40 rpm.
Is spinning at.
尚、固液分離槽は、カラム径100mmで高さ、400mmの塩ビ
カラムを用いた。As the solid-liquid separation tank, a PVC column having a column diameter of 100 mm and a height of 400 mm was used.
この固液分離槽に流入したフロックは、高炉スラグ添加
時の様にカラム内で緻密で高密度なフロックを形成する
ことはなかった。それは、ベントナイトが核として機能
せず、高分子凝集剤分子鎖の絡まりあい現象を助長でき
なかったためでもある。The flocs that flowed into this solid-liquid separation tank did not form dense and high-density flocs in the column as when adding blast furnace slag. This is also because bentonite did not function as a nucleus and could not promote the entanglement phenomenon of polymer coagulant molecular chains.
結果として、このカラム内では、OFRも5m/Hrと低い値に
しかとることができなかった。又、高炉水砕スラグ添加
時の様にOFRも10m/Hrにあげると処理水は濁り、SSが20m
g/と悪化し、SSがリークしてしまった。As a result, the OFR could be as low as 5 m / Hr in this column. Also, if the OFR is raised to 10 m / Hr as when adding granulated blast furnace slag, the treated water becomes turbid and SS is 20 m.
It deteriorated to g / and SS leaked.
又、引き抜いたスラリーをリーフテストにかけるとケー
キ含水率は85%とかなり悪化した。Further, when the extracted slurry was subjected to a leaf test, the water content of the cake was considerably deteriorated to 85%.
同様に、マグネタイトを添加した場合も、高炉水砕スラ
グ添加時の様な効果は得られなかった。Similarly, when magnetite was added, the same effect as when adding granulated blast furnace slag was not obtained.
次に、前記従来例において、ベントナイトの代りにマグ
ネタイトを用いて同様な条件で処理した。Next, in the above-mentioned conventional example, magnetite was used instead of bentonite, and the same treatment was performed.
この固液分離槽に流入したフロックは、緻密で高密度な
フロックを形成できず、カラム内では、OFRを5m/Hr程度
にしかあげることができなかった。The flocs flowing into this solid-liquid separation tank could not form dense and high-density flocs, and the OFR could only be increased to about 5 m / Hr in the column.
又、高炉水砕スラグ添加時の様にOFRを10m/Hrにあげる
とSSはリークし、処理水SSが25mg/と悪化した。Also, when OFR was raised to 10m / Hr as in the case of adding granulated blast furnace slag, SS leaked and treated water SS deteriorated to 25mg /.
[発明の効果] 本発明によれば、金属水酸化物を含む懸濁液から液中の
金属水酸化物を効率良く除去することができる。即ち、
沈降速度が非常に大きくとることができるため、固液分
離槽がコンパクトになる。[Effect of the Invention] According to the present invention, the metal hydroxide in the liquid can be efficiently removed from the suspension containing the metal hydroxide. That is,
The solid-liquid separation tank becomes compact because the sedimentation speed can be very high.
又、通常凝集沈殿の二次処理として設置される濾過機は
不要となる。Further, a filter which is usually installed as a secondary treatment for coagulating sedimentation is unnecessary.
引き抜かれたスラリーは濃縮性、脱水性が良く、濃縮槽
が不要で脱水機も簡易なベルプレスや真空濾過機等で良
い、等顕著な効果がある。The drawn-out slurry has excellent concentrating and dehydrating properties, and a concentrating tank is not necessary, and a dehydrator may be a simple bell press or a vacuum filter.
第1図は本発明の実施態様例の概要を示す説明図であ
る。 1……中和処理後のメッキ液、 2……アニオン系高分子凝集剤、 3……高炉水砕スラグ、 4……カチオン系高分子凝集剤、 5……固液分離槽、6……撹拌羽根、 7……フロック、8……処理水、 9……スラリー(排泥)。FIG. 1 is an explanatory view showing an outline of an embodiment example of the present invention. 1 ... Neutralizing plating solution, 2 ... Anionic polymer flocculant, 3 ... Granulated blast furnace slag, 4 ... Cationic polymer flocculant, 5 ... Solid-liquid separation tank, 6 ... Stirring blade, 7 ... Flock, 8 ... Treated water, 9 ... Slurry (sludge).
Claims (3)
分子凝集剤と高炉水砕スラグ微粉を同時に添加し、急速
攪拌し、次にカチオン系高分子凝集剤を添加し、該カチ
オン系高分子凝集剤と該金属水酸化物及び該高炉水砕ス
ラグ微粉を吸着架橋化した後、回転流により攪拌流動す
るスラッジブランケットゾーンに該懸濁液を上向流で流
入させ、凝集分離を行なうことを特徴とする金属水酸化
物を含む懸濁液の処理方法。1. A suspension containing a metal hydroxide, an anionic polymer flocculant and blast-furnace granulated slag fine powder are added at the same time and rapidly stirred, and then a cationic polymer flocculant is added. After adsorbing and cross-linking the system polymer flocculant, the metal hydroxide and the granulated blast furnace slag fine powder, the suspension is allowed to flow upward into the sludge blanket zone which is agitated and rotated by the rotating flow to separate the flocculation and separation. A method for treating a suspension containing a metal hydroxide, which is characterized by carrying out.
させる方法として、固液分離槽の底部に乱流運動を生起
させる格子状の回転翼を設け、且つ上部に転がり運動を
生起させる十字状の回転翼を設けることを特徴とする請
求項1記載の金属水酸化物を含む懸濁液の処理方法。2. As a method of stirring and flowing in a sludge blanket zone, a lattice-shaped rotary blade that causes turbulent motion is provided at the bottom of a solid-liquid separation tank, and a cross-shaped rotary blade that causes rolling motion is provided at the upper part. The method for treating a suspension containing a metal hydroxide according to claim 1, further comprising:
を設けないゾーンを作り、このゾーン内に形成されたフ
ロックを圧密させることにより、砂濾過と同様の機能を
持たせることを特徴とする請求項1記載の金属水酸化物
を含む懸濁液の処理方法。3. A sludge blanket zone is provided with a rotary blade-free zone above the sludge blanket zone, and the flocs formed in this zone are consolidated to provide the same function as sand filtration. A method for treating a suspension containing a metal hydroxide as described above.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63332174A JPH0696149B2 (en) | 1988-12-28 | 1988-12-28 | Method for treating suspension containing metal hydroxide |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63332174A JPH0696149B2 (en) | 1988-12-28 | 1988-12-28 | Method for treating suspension containing metal hydroxide |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH02174992A JPH02174992A (en) | 1990-07-06 |
JPH0696149B2 true JPH0696149B2 (en) | 1994-11-30 |
Family
ID=18251988
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP63332174A Expired - Lifetime JPH0696149B2 (en) | 1988-12-28 | 1988-12-28 | Method for treating suspension containing metal hydroxide |
Country Status (1)
Country | Link |
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JP (1) | JPH0696149B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1999031017A1 (en) * | 1997-12-15 | 1999-06-24 | Japan As Represented By Ministry Of International Trade And Industry, Director-General, Agency Of Industrial Science And Technology | Method of removing harmful ions and remover for use in the same |
Families Citing this family (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100307975B1 (en) * | 1998-11-18 | 2001-10-20 | 임정규 | Rapid Flocculation and Settling by the Floc Pelletization |
KR20020038222A (en) * | 2000-11-17 | 2002-05-23 | 이구택 | apparatus for detecting chrom in waste water on-line |
KR20020089762A (en) * | 2001-05-24 | 2002-11-30 | 주식회사 맑은물 | a waste water disposal plant |
JP6270608B2 (en) * | 2013-05-07 | 2018-01-31 | 新日鐵住金株式会社 | Coagulation sedimentation apparatus and coagulation sedimentation method |
JP2017064653A (en) * | 2015-09-30 | 2017-04-06 | ステラキューブ株式会社 | Aggregate composition for purifying arsenic-containing muddy water, and purification method |
JP6816292B2 (en) * | 2017-08-31 | 2021-01-20 | オルガノ株式会社 | Water treatment method and water treatment equipment |
JP7327972B2 (en) * | 2019-03-29 | 2023-08-16 | 住友重機械エンバイロメント株式会社 | Coagulation-sedimentation treatment equipment and method of operating the coagulation-sedimentation treatment equipment |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5217581A (en) * | 1975-07-31 | 1977-02-09 | Matsushita Electric Works Ltd | Manufacture of embossed decorated sheet |
JPS551807A (en) * | 1978-06-10 | 1980-01-09 | Kurita Water Ind Ltd | Flocculator |
JPS5542844A (en) * | 1978-09-25 | 1980-03-26 | Terufumi Machida | Deformation method for thermal-induced bending of thermoplastic resin sheet |
JPS62216699A (en) * | 1986-03-18 | 1987-09-24 | Nippon Kokan Kk <Nkk> | Thickening and conditioning device for sludge |
-
1988
- 1988-12-28 JP JP63332174A patent/JPH0696149B2/en not_active Expired - Lifetime
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1999031017A1 (en) * | 1997-12-15 | 1999-06-24 | Japan As Represented By Ministry Of International Trade And Industry, Director-General, Agency Of Industrial Science And Technology | Method of removing harmful ions and remover for use in the same |
Also Published As
Publication number | Publication date |
---|---|
JPH02174992A (en) | 1990-07-06 |
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