JP2010172882A - Coagulant, and method of treating muddy effluent - Google Patents
Coagulant, and method of treating muddy effluent Download PDFInfo
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Abstract
Description
本発明は、各種汚濁廃水の水処理用凝集剤及びそれを用いる汚濁廃水の処理方法に関する。
特に、各種の建設汚泥、河川・港湾等の浚渫汚泥、浄水場汚泥、工場排水汚泥等の汚濁廃水及び各種の工事、建設現場で発生する汚濁廃水の水処理に好適に使用され、フロックの沈降清澄速度を一層早めることができる優れる水処理用凝集剤及びその凝集剤を用いる各種廃水の水処理方法に関する。
The present invention relates to a flocculant for water treatment of various types of contaminated wastewater and a method for treating contaminated wastewater using the same.
It is particularly suitable for the treatment of various types of construction sludge, dredged sludge from rivers and harbors, water purification plant sludge, industrial wastewater sludge, and other construction wastewater generated at construction sites. The present invention relates to an excellent water treatment flocculant capable of further speeding up the clarification rate and various wastewater water treatment methods using the flocculant.
下水処理場等におけうる下水の汚濁廃水、し尿及び有機性産業汚濁廃水は、高度に水処理されて河川、海等に排出されている。また、地盤改良、トンネル掘削、ビル建設現場等で発生する工事・建設汚濁(又は泥奨)廃水や、河川、港湾等の工事現場で発生する浚渫泥奨や、各種産業における工場廃水浄化設備等で発生する各種産業汚濁廃水も、それぞれ高度に水処理されてリサイクル又はリユース用水として利用又は河川、海等に排出されている。 Sewage pollution wastewater, human waste and organic industrial pollution wastewater that can be used in sewage treatment plants etc. are highly treated and discharged into rivers, seas, etc. In addition, ground improvement, tunnel excavation, construction / contamination waste (or mud award) wastewater generated at building construction sites, dredging mud aspiration at construction sites such as rivers and harbors, and factory wastewater purification equipment in various industries, etc. Various industrial polluted wastewater generated in Japan is also highly treated and used as recycled or reused water or discharged into rivers, seas, etc.
このような汚泥・汚濁廃水の終末処理に使用される水処理用凝集剤は、これら汚泥・汚濁廃水中に浮遊する混濁浮遊物を効果的に沈降させて清澄な水にさせるのに用いられている。 The flocculant for water treatment used for the final treatment of such sludge / polluted wastewater is used to effectively settle turbid suspended matter floating in the sludge / polluted wastewater into clear water. Yes.
このような水処理凝集剤には、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(ポリ鉄)等の無機系凝集剤が挙げられ、また、通常、ノニオン系、アニオン系、カチオン系の有機高分子凝集剤が組合わせて、汚濁廃水の水処理に使用されている。
そして、これらの凝集剤は、単に汚泥・汚濁廃水に添加させれば、浮遊混濁物が凝集・沈降・清澄化されるものである。
Examples of such water treatment flocculants include inorganic flocculants such as sulfate band, polyaluminum chloride (PAC), aluminum chloride, ferric chloride, and polyferric sulfate (polyiron). Nonionic, anionic, and cationic organic polymer flocculants are used in combination to treat contaminated wastewater.
And these flocculants are those which are simply added to sludge / polluted wastewater, and the suspended turbid matter is flocculated, settled and clarified.
例えば、その処理工程として、有機性汚泥に硫酸バンド、ポリ塩化アルミニウム(PAC)、塩化アルミニウム、ポリ硫酸第二鉄(ポリ鉄)等の従来から使用されている無機凝集剤の単独又は2種以上を組み合わせて添加させ、次いで、有機高分子凝集剤を添加させて脱水ろ過するに当たって、pHを4以下になるまで無機凝集剤を添加させた後、アルカリ剤を添加させてpHを4〜7に調整し、次いで両性高分子凝集剤を添加させて、浮遊汚泥汚濁物を低含水率のろ過ケーキとして処理されている(特許文献1)。 For example, as the treatment step, organic sludge such as sulfuric acid band, polyaluminum chloride (PAC), aluminum chloride, polyferric sulfate (polyiron), etc., conventionally used alone or in combination of two or more kinds Next, when adding an organic polymer flocculant and dehydrating and filtering, after adding an inorganic flocculant until the pH becomes 4 or less, an alkali agent is added to adjust the pH to 4-7. Then, the amphoteric polymer flocculant is added, and the suspended sludge is treated as a low moisture content filter cake (Patent Document 1).
汚泥・汚濁廃水を沈降清澄化させる水処理用凝集剤には、従来から、通常、凝集用主剤及び高分子凝集剤を含めての凝集助剤とを組み合わせて用いられている。すなわち、従来から硫酸第二鉄、塩化第二鉄、ポリ硫酸第二鉄(ポリ鉄)等の鉄塩系の凝集剤のみでは、十分な凝集効果が得られず、また、消石灰等を併用してpH調整を要したりする傾向にあり、また、硫酸アルミ塩・硫酸鉄塩の塩基性混和凝集剤や、ポリ塩化アルミニウム(PAC)や、珪酸アルカリ水溶液の珪酸ゾル(又はコロイダルシリカ)等の液状凝集剤も、単独使用では一長一短があって万能ではない。また、これら凝集剤は、何れも「水和反応」→「ゾル・ゲル化」→「フロック凝集化」等の作用は、廃水のpH領域に依存して、すなわち鉄イオン及びアルミイオン等のゼータ電位の調整下に凝集剤としての作用を発揮させる。従って、従来からこのような浮遊分散する汚泥・汚濁物の「凝集・フロック・沈降」化には、ゼータ電位との関連付け下に実績評価がなされている。その実績評価として、フロック化促進効果及びフロック粒径を増大化させるためから、それぞれ、アニオン性、カチオン性、ノニオン性等の高分子凝集剤を組み合わせて、架橋作用を発揮させる高分子凝集剤の併用が不可欠であることも事実である。 Conventionally, a coagulant for water treatment that settles and clarifies sludge / polluted wastewater is usually used in combination with a coagulant aid including a coagulant main agent and a polymer coagulant. In other words, conventional iron salt-type flocculants such as ferric sulfate, ferric chloride, and polyferric sulfate (polyiron) alone cannot provide a sufficient agglomeration effect. PH adjustment is required, and basic admixing flocculants such as aluminum sulfate and iron sulfate, polyaluminum chloride (PAC), and silicic acid sol (or colloidal silica) of alkaline silicate aqueous solution, etc. Liquid flocculants are not universal because of their advantages and disadvantages. In addition, all of these flocculants have an action such as “hydration reaction” → “sol / gelation” → “floc agglomeration” depending on the pH range of wastewater, that is, zeta such as iron ions and aluminum ions. It acts as a flocculant under potential adjustment. Therefore, in the past, performance evaluation has been made in association with the zeta potential for such agglomeration / floc / sedimentation of sludge and pollutants that float and disperse. As a result evaluation, in order to increase the flocking promoting effect and the floc particle size, a polymer flocculant that exhibits a crosslinking action by combining polymer flocculants such as anionic, cationic, and nonionic, respectively. It is also true that combination is essential.
本発明の目的は、各種の生活廃水、産業廃水の処理に、粗大フロック形成速度が大きく、また、最終到達フロック粒径が大きく、沈降速度を速くして、上澄み液が短時間で得られる凝集剤の提供と、それを使用する汚濁廃水の処理方法を提供することである。 The purpose of the present invention is to agglomerate a large floc formation rate, a large final floc particle size, a fast sedimentation rate, and a supernatant liquid in a short time for the treatment of various domestic wastewater and industrial wastewater. It is to provide an agent and a method for treating polluted wastewater using the agent.
すなわち、本願発明は以下の凝集剤及びそれを用いる汚濁廃水の処理方法である。
[1] 有機高分子凝集剤粉末と硫酸アルミニウム粉末と石膏粉末と炭酸ソーダ粉末と珪酸ナトリウム粉末との混合物よりなる凝集剤であって、その成分配合組成が下記のものであることを特徴とする凝集剤。
(1)有機高分子凝集剤粉末 3〜6w%
(2)石膏粉末 45〜60w%
(3)炭酸ソーダ粉末 15〜30w%
(4)硫酸アルミニウム粉末 12〜20w%
(5)珪酸ナトリウム粉末 4〜10w%
[2] 有機高分子凝集剤粉末がアクリルアミドであり、石膏粉末が半水石膏粉末であり、珪酸ナトリウムが水ガラスの乾燥物であることを特徴とする[1]記載の凝集剤。
[3] 前記高分子凝集剤粉末が、平均粒子径60〜200μmであることを特徴とする[1]又は[2]に記載の凝集剤。
[4] 懸濁物(SS)濃度が50〜20,000mg/リットルの汚濁廃水1000ml当たり、高速攪拌下に[1]〜[3] のいずれか1項に記載の凝集剤を100〜30,000ppmの範囲で添加・混合させ、静置して懸濁物(SS)をフロックとして沈降分離して清澄水を得ることを特徴とする汚濁廃水の処理方法。
That is, this invention is the processing method of the following flocculants and the polluted wastewater using the same.
[1] A flocculant composed of a mixture of organic polymer flocculant powder, aluminum sulfate powder, gypsum powder, sodium carbonate powder and sodium silicate powder, and its component composition is as follows: Flocculant.
(1) Organic polymer flocculant powder 3-6w%
(2) Gypsum powder 45-60w%
(3) Sodium carbonate powder 15-30w%
(4) Aluminum sulfate powder 12-20w%
(5) Sodium silicate powder 4-10w%
[2] The flocculant according to [1], wherein the organic polymer flocculant powder is acrylamide, the gypsum powder is hemihydrate gypsum powder, and the sodium silicate is a dried product of water glass.
[3] The flocculant according to [1] or [2], wherein the polymer flocculant powder has an average particle size of 60 to 200 μm.
[4] 100 to 30 of the flocculant according to any one of [1] to [3] under high-speed stirring per 1000 ml of contaminated wastewater having a suspension (SS) concentration of 50 to 20,000 mg / liter. A method for treating polluted wastewater, comprising adding and mixing within a range of 000 ppm, and allowing to settle and separate the suspension (SS) as floc to obtain clarified water.
本発明の水処理用凝集剤において、
(1)有機高分子凝集剤粉末は、公知のものが使用されるが、特にアクリルアミド系のものが好ましい。その配合量は3〜6w%が好ましい。粉末状の高分子凝集剤としては、アニオン系又はノニオン系で、例えば、アニオン系;ポリアクリル酸ソーダ、ポリスルホメチル化ポリアクリドアミド、また、ノニオン系;ポリアクリドアミド、ポリエチレンpキサイドが挙げられる。
(2)石膏粉末としては、半水石膏が好ましく、その配合量は45〜60w%が好ましい。
(3)炭酸ソーダ粉末としては、市販のものでよいが、その配合量は15〜30w%が好ましい。
(4)硫酸アルミニウム粉末としては、市販のものでよいが、その配合量は12〜20w%が好ましい。
(5) 珪酸ナトリウム粉末としては、水ガラスの乾燥物が好ましく、その配合量は4〜10w%が好ましい。
特にこの水ガラスの乾燥物は、液状水ガラスを乾燥・脱水して得られるものであり、本願発明の凝集剤中の重要な成分であり、フロックの生成及びサイズの増大化に寄与するものである。水ガラスの乾燥物である、水ガラス粉末は、例えば1号〜3号の水ガラスを、例えばスプレードライ法で乾燥することにより得ることできる。
In the water treatment flocculant of the present invention,
(1) Known organic polymer flocculant powders are used, but acrylamide type powders are particularly preferred. The blending amount is preferably 3 to 6% by weight. Examples of the powdery polymer flocculant include anionic and nonionic types such as anionic type; sodium polyacrylate, polysulfomethylated polyacylamide, and nonionic type: polyacryamide, polyethylene poxide. Can be mentioned.
(2) As gypsum powder, hemihydrate gypsum is preferable, and the blending amount is preferably 45 to 60 w%.
(3) Although a commercially available sodium carbonate powder may be used, the blending amount is preferably 15 to 30 w%.
(4) The aluminum sulfate powder may be commercially available, but the blending amount is preferably 12 to 20 w%.
(5) As a sodium silicate powder, the dried material of water glass is preferable, and the compounding quantity has preferable 4-10 w%.
In particular, this dried water glass is obtained by drying and dehydrating liquid water glass, which is an important component in the flocculant of the present invention, and contributes to generation of flocs and increase in size. is there. Water glass powder, which is a dried product of water glass, can be obtained, for example, by drying water glass of No. 1 to No. 3 by, for example, a spray drying method.
本願発明によれば、高速攪拌下で懸濁物(SS)を急速にフロック化及び沈降分離することができる。 According to the present invention, the suspension (SS) can be rapidly flocculated and separated by settling under high-speed stirring.
本願発明の水処理凝集剤は、従来の凝集剤に比較して、急速なフロックの生成及びサイズの増大化ができ、より完全に懸濁物をフロック化して清澄な処理水を取得することができる。 Compared with conventional flocculants, the water treatment flocculant of the present invention can rapidly generate flocs and increase in size, and more completely floculate the suspension to obtain clear treated water. it can.
以下に、本願発明による凝集剤について、その実施に係わる最良形態を更に説明する。 Below, the best mode concerning the implementation is further demonstrated about the coagulant | flocculant by this invention.
本願発明の凝集剤の実施例の成分配合組成は、下記のとおりである。
(1)有機高分子凝集剤粉末 0.4kg
(2)半水石膏粉末 5.0kg
(3)炭酸ソーダ粉末 2.5kg
(4)硫酸アルミニウム粉末 1.5kg
(5)珪酸ナトリウム粉末 0.6kg
上記(1)〜(5)の各粉末を秤量し、それらを攪拌機にて混合して本願発明の凝集剤を製造した。
次に、前記実施例で得られた凝集剤を、懸濁物(SS)濃度が50〜20,000mg/リットルの汚濁廃水に、高速攪拌下に凝集剤を100〜30,000ppmの範囲で添加・混合させ、静置した。
高速攪拌をすると直ちに、懸濁物(SS)が大きなフロックとなって生成した。
攪拌を停止すると、それらのフロックは数秒間で下底に沈降し、その上に懸濁物(SS)濃度が10〜50ppm以下の透明な清澄水が生成した。
以上のように、本願発明の凝集剤は、懸濁物中に強撹拌下で添加・混合することで、懸濁物のフロック化とその沈降分離が迅速に実行できる。
The component blend composition of the examples of the flocculant of the present invention is as follows.
(1) Organic polymer flocculant powder 0.4kg
(2) Hemihydrate gypsum powder 5.0kg
(3) Sodium carbonate powder 2.5kg
(4) Aluminum sulfate powder 1.5kg
(5) Sodium silicate powder 0.6kg
Each powder of said (1)-(5) was weighed, and they were mixed with the stirrer, and the flocculant of this invention was manufactured.
Next, the flocculant obtained in the above example is added to the polluted waste water having a suspension (SS) concentration of 50 to 20,000 mg / liter in the range of 100 to 30,000 ppm with high-speed stirring.・ Mixed and allowed to stand.
Immediately after high-speed stirring, a suspension (SS) was formed as a large floc.
When the stirring was stopped, the flocs settled to the bottom in a few seconds, and transparent clear water having a suspension (SS) concentration of 10 to 50 ppm or less was formed thereon.
As described above, the flocculant of the present invention can be rapidly flocculated and settled and separated by adding and mixing the suspension with vigorous stirring.
なお、上記高速攪拌下とは、120rpm以上の撹拌速度が好ましく、このような処理方法で各種の汚濁廃水を処理することができる。
The high-speed stirring is preferably a stirring speed of 120 rpm or higher, and various types of contaminated wastewater can be treated by such a treatment method.
Claims (5)
(1)有機高分子凝集剤粉末 3〜6w%
(2)石膏粉末 45〜60w%
(3)炭酸ソーダ粉末 15〜30w%
(4)硫酸アルミニウム粉末 12〜20w%
(5)無水珪酸ナトリウム粉末 4〜10w% A flocculant comprising a mixture of organic polymer flocculant powder, aluminum sulfate powder, gypsum powder, sodium carbonate powder, and anhydrous sodium silicate powder, and the composition of the components is as follows: .
(1) Organic polymer flocculant powder 3-6w%
(2) Gypsum powder 45-60w%
(3) Sodium carbonate powder 15-30w%
(4) Aluminum sulfate powder 12-20w%
(5) Anhydrous sodium silicate powder 4-10w%
The flocculant according to any one of claims 1 to 4 is added in a range of 100 to 30,000 ppm under high-speed stirring to contaminated wastewater having a suspension (SS) concentration of 50 to 20,000 mg / 1 liter. A method for treating contaminated wastewater, characterized in that after mixing, the mixture is allowed to stand to settle and separate the suspension (SS) as floc to obtain clear water.
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Cited By (4)
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JP5852276B1 (en) * | 2015-03-04 | 2016-02-03 | 有限会社谷田建設 | Method for producing soil amendment |
CN106430487A (en) * | 2016-11-01 | 2017-02-22 | 吉林化工学院 | Preparation method of environment-friendly aluminum zinc polysilicate-cellulose compound flocculating agent |
CN107381745A (en) * | 2017-08-23 | 2017-11-24 | 钟传新 | A kind of environmental protection flocculant and preparation method thereof |
JP7357746B1 (en) | 2022-09-28 | 2023-10-06 | 健二 篠原 | New seabed improvement agent 3 that promotes the binding of marine plastic debris and radioactive pollutants and heavy metal substances in seawater |
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2009
- 2009-02-02 JP JP2009021850A patent/JP2010172882A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
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JP5852276B1 (en) * | 2015-03-04 | 2016-02-03 | 有限会社谷田建設 | Method for producing soil amendment |
CN106430487A (en) * | 2016-11-01 | 2017-02-22 | 吉林化工学院 | Preparation method of environment-friendly aluminum zinc polysilicate-cellulose compound flocculating agent |
CN107381745A (en) * | 2017-08-23 | 2017-11-24 | 钟传新 | A kind of environmental protection flocculant and preparation method thereof |
JP7357746B1 (en) | 2022-09-28 | 2023-10-06 | 健二 篠原 | New seabed improvement agent 3 that promotes the binding of marine plastic debris and radioactive pollutants and heavy metal substances in seawater |
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