JPH02174992A - Treatment of suspension containing metal hydroxide - Google Patents

Treatment of suspension containing metal hydroxide

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Publication number
JPH02174992A
JPH02174992A JP33217488A JP33217488A JPH02174992A JP H02174992 A JPH02174992 A JP H02174992A JP 33217488 A JP33217488 A JP 33217488A JP 33217488 A JP33217488 A JP 33217488A JP H02174992 A JPH02174992 A JP H02174992A
Authority
JP
Japan
Prior art keywords
flocs
metal hydroxide
zone
high molecular
suspension
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
JP33217488A
Other languages
Japanese (ja)
Other versions
JPH0696149B2 (en
Inventor
Kazuhisa Fukunaga
和久 福永
Koji Matayoshi
康治 又吉
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.)
Nippon Steel Corp
Original Assignee
Nippon Steel Corp
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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP63332174A priority Critical patent/JPH0696149B2/en
Publication of JPH02174992A publication Critical patent/JPH02174992A/en
Publication of JPH0696149B2 publication Critical patent/JPH0696149B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PURPOSE:To increase a settling speed, to enhance the efficiency and stability of processing for flocculation and separation, an to form sludge easy to concentrate and dehydrate by adding a granular solid material simultaneously with the addition of an anionic high molecular flocculant, and adding a cationic high molecular flocculant prior to a formation of coarse flocs. CONSTITUTION:An anionic high molecular flocculant 2 and blast furnace granulated slag 3 are added to a suspension 1 (neutralized plating soln.), a cationic high molecular flocculant 4 is then allowed to flow into a solid-liquid separation tank 5 as an upward current. The inflow flocs 7 are dehydrated and rolled in a column to form a pellet-shaped dense floc. Compaction is further caused above an impeller 6. The slurry 9 drawn off from the compaction zone is easy to concentrate and dehydrate, a concentration tank is not needed, and simple press, vacuum filter, etc., are sufficiently used as the dehydrator. Such remarkable effects are produced.

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、例えばメツキ工
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・石炭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。
Detailed Description of the Invention [Industrial Field of Application] The present invention is applicable to suspensions containing metal hydroxides, such as waste water discharged from metal surface treatment factories such as Metsuki factories, electrolytic polishing factories, and alumite factories. In order to remove heavy metal ions such as zinc, nickel, aluminum, and tin contained in It relates to a solid-liquid separation process that removes metal hydroxides from liquids.

[従来の技術] 従来より、懸濁液物質を含む懸濁液から懸濁固形物を分
m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, precipitation separation methods, flotation separation methods, filtration separation methods, adsorption separation methods, etc. have been known as methods for separating suspended solids from suspensions containing suspended substances. There is.

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、9
5〜98)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 and the amount of drainage is large, such as metal hydroxide, the precipitation method (for example,
P.9 of “Solid-Liquid Separation Technology” published by Nichigihodo Publishing Co., Ltd.
5 to 98) are the cheapest and can be expected to provide stable processing, and are therefore 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、消石炭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 coal have poor sedimentation properties and are difficult to separate from solid to liquid. A method has been adopted in which the flocs are further increased in size by adding .

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
粒子径は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 flocs produced by this method have a large apparent particle size, the particles are loosely bonded to each other and contain a large amount of water, so their density is small and the apparent particle size depends on the sedimentation rate. A rise cannot be expected. Also, the concentration and dehydration properties 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 improves the conventional coagulation-sedimentation method by forming dense, highly cohesive, and high-density flocs that have fundamentally different properties from conventional coagulation-sedimentation flocs. In addition to increasing the sedimentation rate several times higher than the sedimentation rate, the processing efficiency and stability of the coagulation separation process are improved to the extent that the filtration step that is conventionally required as a finishing step after coagulation and sedimentation can be omitted, and the process is concentrated. The purpose of this invention is to provide a solid-liquid separation method that simultaneously produces sludge with good properties and dewaterability.

[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@き、フロックを形成する。
[Means and actions for solving the problem] Generally, metal hydroxides are positively charged, so the addition of an anionic polymer flocculant causes charge neutralization and adsorption crosslinking, which makes the flocs Form.

発明者らは、上記に示す8i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粒
状固形物を添加し、数十秒急速攪拌し、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 added granular solids at the same time as the addition of an anionic polymer flocculant in order to create dense, strong bonding, and high-density flocs with different properties from the conventional 8i flocs shown above. The mixture was rapidly stirred for several tens of seconds, and a cationic polymer flocculant was added before forming coarse flocs.

粒状固形物は、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。
The granular solids are incorporated into the flocs that are being formed by the action of the anionic polymer flocculant and form 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・粒状固形物は吸着架橋化
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。
In addition, due to the action of the cationic polymer flocculant, the cationic polymer flocculant and the metal hydroxide/particulate solid are adsorbed and crosslinked, and at the same time form a complex network structure with the anionic polymer flocculant.

カチオン系高分子凝集剤は、分子鎮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。
Cationic polymer flocculants have many adsorption active sites in their molecules, so they form flocs with strong binding strength.

この時、金属水酸化物とカチオン系高分イ凝集剤は、共
に正に荷電していることもあり、部に分散現象が起こり
フロックは小さくなる。
At this time, since both the metal hydroxide and the cationic polymer flocculant are positively charged, a dispersion phenomenon occurs and the flocs become smaller.

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鎮が絡まりあい、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 with extremely strong cohesion, and by gentle disturbance, the molecules become entangled, forming a dense, dense floc with strong cohesion.

この様なフロック群からなる液を更に、上向流で固液分
動[に流入ざゼる。
The liquid consisting of such a group of flocs further flows upward into the solid-liquid separator.

固液分11ft41内では、攪拌羽根がゆっくりと回転
しており、ここで攪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。
Within the solid-liquid content of 11 ft 41, the stirring blade rotates slowly, and the stirring blade and the flocs collide with each other, and the flocs collide with each other, and the water in the flocs is released. Also, due to the rolling motion, a round, tight flock is formed.

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
ものの粒状固形物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 flocs made in this way have a diameter of 1 mm to 3 mm.
It is a very well-compacted floc, and although the particle size is small, it is a dense floc with granular solids as its core.
Due to its high density, it is possible to increase the sedimentation rate by more than 10 times compared to conventional flocculation method flocs.

又、この固液分館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、連続的に弓き抜かれるが、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。
In addition, the flocs formed in this solid-liquid branch tank are intermittently or continuously extracted as slurry, and the thickening and dewatering properties of this slurry are considerably better than in conventional methods. Become.

粒状固形物としては、フロックの核になるものであれば
基本的には使用可能であるが、ベントナイトの様に高い
ユ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。
As a granular solid, it can basically be used as long as it forms the core of flocs, but those with high uloid properties, high swelling and water supply properties, such as bentonite, have a low dry volume. The flocs will absorb several times more water, increasing the diameter of the flocs.

このフロックは、水を内部に含有しているもののフロシ
フ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l、2ても、間隙が大ぎいため、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、マグナタイトの様に水酸化物となかなかNI
I染まないものは、フロックの1亥となりにくく、添加
剤としては不適である。
Although this floc contains water inside, its flocsif diameter is quite large, so the sedimentation rate is quite high. However, the dewatering properties are not very good, and even if compacted filtration tanks 1 and 2 are formed as described below, the gaps are too large, so unformed flocs flow out, causing instability in the quality of the treated water. Also, like magnetite, it is quite NI with hydroxide.
Those that do not dye are difficult to form a floc and are unsuitable as additives.

そこで、発明者らは様々な粒状固形物を使フたテストを
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 conducted tests using various granular solids, and found that granulated fine powder with an average particle size of about 50μ was obtained by crushing and classifying granulated slag, which is a byproduct of blast furnaces in the steel industry. found to be the most effective.

この平均粒径が約50μ程度の高炉水砕微粉を粒状固形
物として用いると、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。
When this granulated blast furnace granulated powder having an average particle size of about 50 μm is used as the granular solid, the granulated water is easily incorporated into the metal hydroxide and becomes the core of the floc. This granulated water has a specific gravity of 2~
3, it is effective in increasing the sedimentation rate of formed flocs, and also has good concentration and dewatering properties.

スラリーゾーン内で、攪拌流動させる方ンノ、としては
攪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。
In order to stir and flow the slurry in the slurry zone, the stirring blade is slowly rotated, the blade collides with the flocs, and the flocs collide with each other to drive out the water in the flocs, and a rolling motion is generated to form round flocs. Basically, any method that promotes dehydration can be used.

しかしながら、プロペラ型攪拌機の様に」−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 to form a dense floc by dehydration in a propeller-type stirrer that causes downward convection movement.

発明者らは、様々な形状の攪拌羽根を作り、実験を繰返
した結果、下記の攪拌羽根に到達した。
The inventors made stirring blades of various shapes and repeated experiments, and as a result, they arrived at the following stirring blade.

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, we divided the functions into a part that causes turbulent motion and a 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 blade collides with the flocs and the flocs and dehydration occurs is the part that causes turbulent motion, and the part where regular rotation makes the flocs into a round shape is the part that causes 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。
Raw water flows upward into the sludge blanket zone from the bottom, and grid-like blades were installed at the bottom to create turbulent flow. A lattice-shaped blade is a combination of flat plates so that the cross section has a lattice shape.

又、その上部には、2枚の平板を千字状に組み合わせた
十字羽根を設置した。
Moreover, a cross feather made of two flat plates arranged in a 1000-character pattern was installed on top of it.

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、何枚も重ね合せる事で対応する。又、2種類の羽
根は同しシャフトに固定さね、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 deeper, these two types of blades can be separated into upper and lower parts and stacked on top of each other. Also, the two types of blades are fixed to the same shaft and rotated at the same rotational speed. Also, although the length of the blade does not extend to the outer periphery 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、攪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。
This treatment method can also have a great effect by providing a consolidation filtration section in the sludge blanket zone above the agitation flow section, that is, the section where turbulence and rolling motion occur.

つまり、攪拌流動部でフロック同志のi突、フロックと
羽根の衝突を繰返し、又転がり運動により形成された緻
密で結合力の強い、径1〜3111mのベレット状のフ
ロックは上向流により上部に押し出されるが、このフロ
ック群を更に攪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 stirring flow section, the flocs collide with each other, the flocs repeatedly collide with the blades, and the pellet-shaped flocs, which are dense and have a strong bond and have a diameter of 1 to 3,111 m, are formed by the rolling motion and are pushed upward by the upward flow. However, if this group of flocs is further fixed in an area where there is no stirring movement, solid-liquid separation occurs and an interface is formed. The water above the interface is clear and 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、ここでは攪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1〜3IIII[lの緻密フ
ロック群であり、一種の濾過機能を有する6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。
In addition, the area below the interface becomes a sludge blanket zone, where a consolidation phenomenon occurs where there is no stirring movement. This consolidated layer is a group of dense flocs with a diameter of 1 to 3 l, and has a kind of filtration function, 6 that is, unformed flocs, dissolved heavy metals, SS, etc. are trapped in the gaps between the flocs.

或は、フロックに吸着され取り込まれる。Alternatively, it is adsorbed and taken in by flocs.

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 processes such as sand filtration, which are normally used as a secondary treatment after coagulation and precipitation, are not necessary.

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。
In addition, the slurry extracted from this compacted zone has a high slurry concentration and good concentrating properties.

場合によっては、濃縮も不要となる。In some cases, concentration may also be unnecessary.

又、その後の脱水性も良い。通常、メツキ液等の廃液を
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ttらない
In addition, subsequent dehydration is also good. Normally, it is difficult to dehydrate flocs obtained by coagulating and precipitating waste liquids such as plating liquid, and the water content cannot be reduced to 80% or less unless dehydrated using 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 using a simple belt press, etc.
It is possible to reduce the moisture content to 80% or less.

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, suspensions containing metal hydroxides can be treated stably and efficiently.

[実 jK  例] 第1図に示す様に、電気亜鉛メツキ工場から発生する亜
鉛イオンtiomg#!、 クロムイオン67 mg/
Jl、鉄イオン171g八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4 a+g/L平均粒径50μの高炉水砕スラグ3を
1000mg/F!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
2 mg/Ll加え、固液分離槽5に上向流で流入させ
た。
[Actual Example] As shown in Figure 1, zinc ions tiomg#! are generated from an electrogalvanizing factory. , chromium ion 67 mg/
Jl, a waste liquid containing 171 g of iron ions was raised to pH 11 with slaked lime, and neutralized to a suspension containing metal hydroxides, and a polyacrylamide-based anionic polymer flocculant 2 was added.
4 a+g/L 1000mg/F of granulated blast furnace slag 3 with an average particle size of 50μ! After stirring rapidly for 30 seconds, 2 mg/Ll of polyacrylamide-based cationic polymer flocculant 4 was added, and the mixture was allowed to flow into the solid-liquid separation tank 5 in an upward flow.

固液分l1iff糟では、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
、40 rpmで回転している。
The solid-liquid fraction l1iff rice cake has a stirring blade 6 consisting of several lattice-shaped blades stacked on the bottom and several cross-shaped blades stacked on the top, and rotates at 40 rpm.

尚、固液分m糟は、カラム径100n+mで高さ400
Iの塩ビカラムを用いた。
In addition, the solid-liquid fraction m has a column diameter of 100n+m and a height of 400m.
A PVC column of I was used.

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のベレッ
ト状の緻密なフロックとなる。更に攪拌羽根上部では、
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 within the column, and become dense pellet-shaped flocs of 1 to 3 mm. Furthermore, at the top of the stirring blade,
Consolidation phenomena also occur, creating 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、SS 4 mg/l、鉄イオンI ll1g#!、
亜鉛イオン1 rag/I、クロムイオン1 mg/l
の非常に良好な処理水8となる。
Clear water separated from solid and liquid by this column is discharged from the upper part, and contains SS 4 mg/l and iron ions Ill1g#! ,
Zinc ion 1 rag/I, chromium ion 1 mg/l
This results in very good treated water 8.

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。
Furthermore, since the consolidated portion has a filtration function, the processing is stable and 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 drawn out from the consolidation zone can be easily subjected to a leaf test, and the moisture content of the cake is 80%, which allows for highly efficient dewatering.

[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、
沈降速度が非常に犬きくとることができるため、固液分
11ilt41がコンパクトになる。
[Effects of the Invention] According to the present invention, metal hydroxides in the liquid can be efficiently removed from a suspension containing metal hydroxides. That is,
Since the sedimentation rate can be very low, the solid-liquid content 11ilt41 becomes compact.

又、通常凝集沈殿の二次処理として設置される濾過機は
不用となる。
In addition, a filter that is normally installed as a secondary treatment for coagulation and precipitation becomes unnecessary.

引き抜かれたスラリーは濃縮性、脱水性が良く、濃縮槽
が不用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 slurry has good concentration and dewatering properties, and has remarkable effects such as no need for a concentration tank and a simple bell press or vacuum filter can be used as a dehydrator.

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

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・・・中和処理後のメツキ液、 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・・・攪拌羽根、7・
・・フロック、    8・・・処理水、9・・・スラ
リー(排泥)、。 他4名 I、$件の表示 昭和63年 許願 第3327?十号 名(名称) 新日本製鐵株式台杆 東京都千代田区丸の内2丁目6番2号丸の内へ重洲ビル
330補正命令の日付 1も 補正の内容 別紙のとおり 補      正      書 本願明細書中下記事項を補正致します。 記 1、特許請求の範囲を別紙の如く訂正する。 2、第2頁15行目に 「石炭石」とあるを 「石灰石」と訂正する。 3゜第2頁最下行に 「懸濁液物質」とあるを 「懸濁物質」と訂正する。 4I第3頁11行目に r消石炭Jとあるを 「消石灰」と訂正する。 5、第7頁1行目に 「コロイド」とあるを 「コロイド」と訂正する。 6、第7頁11行目に 「マグネタイト」とあるを 「マグネタイト」と訂正する。 7、第13頁1ロ行に rs84■/Q、鉄イオン1■/Q、」とあるをr S
 S 3 mg/Q、 鉄イオン0 、1 mg / 
Q、」と訂正する。 8゜第13頁1ロ目に [イオン1■/Q、クロムイオン1■/QJとあるを Fイオン0.2■/Q、クロ11イオンO21■/U 
と訂正する。 9、第13頁16行目、18行目に 「不用」とあるをそれぞれ [不要Jと訂正する。 特許請求の範囲 1 金属水酸化物を含む懸濁液にアニオン系高分子凝集
剤を添加し、更に粒状固形物とカチオン系高分子凝集剤
を添加した後、回転流により撹を特徴とする金属水酸化
物を含む懸濁液の処理方法。 2 粒状固形物として、高炉水砕を用いることを特徴と
する請求項1記戦の金属水酸化物を含む61件処理方法
。 3 スラッジブランケットゾーン内で撹拌流動させる方
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i?lff
求項1記載の金属水酸化物を倉皇懸濁液の処理方法。 4 スラッジブランケットゾーン上部に回転翼を設けな
いゾーンを作り、このゾーン内に形成されたフロックを
圧密させる事により、砂濾過と同様の機能を持たせるI
tを特徴とする請求記載の金属水酸化物を含む懸濁液の
処理方法。
FIG. 1 is an explanatory diagram showing an outline of an embodiment of the present invention. 1... Plating liquid after neutralization treatment, 2... Anionic polymer flocculant, 3... Granulated blast furnace slag, 4... Cationic polymer flocculant, 5... Solid-liquid separation Tank, 6... Stirring blade, 7.
...Floc, 8. Treated water, 9. Slurry (exhaust sludge). 4 other people I, $ display 1988 Application No. 3327? Name of No. 10 (Name) Nippon Steel Co., Ltd. Taipei 2-6-2 Marunouchi, Chiyoda-ku, Tokyo To Marunouchi Shigesu Building 330 Date 1 of the amendment order is also amended as per the attached sheet with details of the amendment. We will correct the matters. Note 1: The scope of claims is amended as shown in the attached sheet. 2. On page 2, line 15, "coalstone" is corrected to "limestone." 3゜In the bottom line of page 2, the words "suspended substances" should be corrected to "suspended substances." 4I, page 3, line 11, slaked coal J is corrected to ``slaked lime''. 5. In the first line of page 7, the word "colloid" is corrected to "colloid." 6. On page 7, line 11, "magnetite" is corrected to "magnetite". 7. On page 13, line 1, it says rs84■/Q, iron ion 1■/Q,'' rS
S 3 mg/Q, iron ion 0, 1 mg/
Q,” he corrected. 8゜Page 13, 1st row [Ion 1■/Q, Chromium ion 1■/QJ and F ion 0.2■/Q, Chrome 11 ion O21■/U
I am corrected. 9. On page 13, lines 16 and 18, the words "unnecessary" are corrected to [unnecessary J]. Claim 1: A metal product characterized by adding an anionic polymer flocculant to a suspension containing a metal hydroxide, further adding granular solids and a cationic polymer flocculant, and then stirring with a rotating flow. A method for treating suspensions containing hydroxides. 2. The method for treating 61 items containing metal hydroxides according to claim 1, characterized in that blast furnace granulation is used as the granular solids. 3. As a method of stirring and fluidizing the sludge blanket zone, it is possible to provide a lattice-shaped rotor blade at the bottom of the solid-liquid separation tank to generate turbulent motion, and a cross-shaped rotor blade to generate rolling motion at the top. Characteristic i? lff
A method for treating a suspension of the metal hydroxide according to claim 1. 4 A zone without rotary blades is created above the sludge blanket zone, and the flocs formed in this zone are consolidated to provide the same function as sand filtration.I
A method for treating a suspension containing a metal hydroxide as claimed in claim t.

Claims (1)

【特許請求の範囲】 1 金属水酸化物を含む懸濁液にアニオン系高分子凝集
剤を添加し、更に粒状固形物とカチオン系高分子凝集剤
を添加した後、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。 2 粒状固形物として、高炉水砕を用いることを特徴と
する請求項1記載の金属水酸化物を含む懸濁液液の処理
方法。 3 スラッジブランケットゾーン内で攪拌流動させる方
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懸濁液の処理方法。 4 スラッジブランケットゾーン上部に回転翼を設けな
いゾーンを作り、このゾーン内に形成されたフロックを
圧密させる事により、砂濾過と同様の機能を持たせる事
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。
[Claims] 1. A sludge that is stirred and fluidized by a rotating flow after adding an anionic polymer flocculant to a suspension containing a metal hydroxide, and further adding granular solids and a cationic polymer flocculant. A method for treating a suspension containing a metal hydroxide, which comprises flowing the suspension into a blanket zone in an upward flow to perform coagulation and separation. 2. The method for treating a suspension containing metal hydroxide according to claim 1, characterized in that blast furnace granules are used as the granular solids. 3. As a method of stirring and fluidizing the sludge blanket zone, it is possible to provide a grid-shaped rotary blade that generates turbulent flow motion at the bottom of the solid-liquid separation tank, and a cross-shaped rotary blade that generates rolling motion at the top. A method for treating a suspension of metal hydroxide according to claim 1. 4. The metallic water according to claim 1, which has a function similar to that of sand filtration by creating a zone without rotary blades above the sludge blanket zone and consolidating the flocs formed within this zone. A method for treating suspensions containing oxides.
JP63332174A 1988-12-28 1988-12-28 Method for treating suspension containing metal hydroxide Expired - Lifetime JPH0696149B2 (en)

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 true JPH02174992A (en) 1990-07-06
JPH0696149B2 JPH0696149B2 (en) 1994-11-30

Family

ID=18251988

Family Applications (1)

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

Country Link
JP (1) JPH0696149B2 (en)

Cited By (7)

* Cited by examiner, † Cited by third party
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
JP2014237123A (en) * 2013-05-07 2014-12-18 新日鐵住金株式会社 Coagulation sedimentation equipment and 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
WO2019044312A1 (en) * 2017-08-31 2019-03-07 オルガノ株式会社 Water treatment method and water treatment device
JP2020163289A (en) * 2019-03-29 2020-10-08 住友重機械エンバイロメント株式会社 Flocculation sedimentation treatment apparatus, and operational method of flocculation sedimentation treatment apparatus

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
BR9814281A (en) * 1997-12-15 2000-10-03 Japan As Represented By Minist "harmful ion removal method and removal agent used for it"

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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

Patent Citations (4)

* Cited by examiner, † Cited by third party
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

Cited By (8)

* Cited by examiner, † Cited by third party
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
JP2014237123A (en) * 2013-05-07 2014-12-18 新日鐵住金株式会社 Coagulation sedimentation equipment and 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
WO2019044312A1 (en) * 2017-08-31 2019-03-07 オルガノ株式会社 Water treatment method and water treatment device
JPWO2019044312A1 (en) * 2017-08-31 2019-11-07 オルガノ株式会社 Water treatment method and water treatment apparatus
JP2020163289A (en) * 2019-03-29 2020-10-08 住友重機械エンバイロメント株式会社 Flocculation sedimentation treatment apparatus, and operational method of flocculation sedimentation treatment apparatus

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