JP2001137865A - Method for separating insolubilized matter - Google Patents

Method for separating insolubilized matter

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Publication number
JP2001137865A
JP2001137865A JP32015499A JP32015499A JP2001137865A JP 2001137865 A JP2001137865 A JP 2001137865A JP 32015499 A JP32015499 A JP 32015499A JP 32015499 A JP32015499 A JP 32015499A JP 2001137865 A JP2001137865 A JP 2001137865A
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JP
Japan
Prior art keywords
insolubilized
liquid
separation
treatment
filtration
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
JP32015499A
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Japanese (ja)
Other versions
JP4239326B2 (en
Inventor
Isamu Kato
勇 加藤
Fumitaka Yoshimura
二三隆 吉村
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Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Priority to JP32015499A priority Critical patent/JP4239326B2/en
Publication of JP2001137865A publication Critical patent/JP2001137865A/en
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Publication of JP4239326B2 publication Critical patent/JP4239326B2/en
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  • Removal Of Specific Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for separating insolubilized matter which is capable of obtaining clean filtrate for a long period by improving the affinity of the inorganic insolubilized matter precipitated by an insolubilization treatment of liquid to be treated to a filter medium, thereby enhancing the capturability by the filter medium and preventing the leakage of the insolubilized matter from the filter medium to execute filtration and separation efficiently. SOLUTION: The liquid 5 to be treated is introduced into an insolubilization vessel 1 where a flocculating agent or insolubilizing agent is added thereto to precipitate the inorganic insolubilized matter. The precipitated insolubilized matter is partly subjected to a separation of solid from the liquid in a settling vessel 3 or floating vessel 4 and thereafter or without subjecting the insolubilized matter to the separation of the solid from the liquid, an alkali metal salt 10 of a higher fatty acid is added thereto and the insolubilized matter is subjected to a filtration and separation treatment in a filter vessel 2.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、被処理液を不溶化
処理して無機質の不溶化物を析出させ、この不溶化物を
濾過分離する不溶化物分離方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an insolubilized material separation method for insolubilizing a liquid to be treated, thereby precipitating an inorganic insoluble material, and filtering and separating the insoluble material.

【0002】[0002]

【従来の技術】用排液処理では、被処理液中に含まれる
濁質やコロイド状物質等の不純物を除去するために、凝
集処理が行われる。この凝集処理には、被処理液に無機
凝集剤を添加し、必要によりpH調整剤を添加してpH
調整することにより、凝集剤成分を不溶化物として析出
させ、このとき不溶化物に不純物を抱き込ませて除去す
る方法がある。こうして析出した不溶化物は沈降分離、
浮上分離等の固液分離により分離したのち、あるいは分
離することなく、濾過により分離することが行われる。
2. Description of the Related Art In waste water treatment, coagulation treatment is performed to remove impurities such as turbid and colloidal substances contained in a liquid to be treated. In this coagulation treatment, an inorganic coagulant is added to the liquid to be treated, and if necessary, a pH adjuster is added to adjust the pH.
There is a method in which the coagulant component is precipitated as an insolubilized substance by adjusting the concentration, and at this time, impurities are embodied in the insolubilized substance and removed. The insolubilized material thus precipitated is separated by settling,
After separation by solid-liquid separation such as flotation separation, or separation without filtration, separation is performed.

【0003】このような凝集処理とは別に、被処理液中
に重金属イオンが含まれる場合、アルカリを加えて中和
し、重金属イオンを不溶化する中和処理法がある。アル
カリの他に硫化物、リン酸塩等の不溶化剤を加えて重金
属イオンを不溶化処理し、不溶化物を固液分離により分
離したのち、あるいは分離することなく濾過分離する方
法がある。
[0003] Apart from such agglomeration treatment, there is a neutralization treatment method in which when a liquid to be treated contains heavy metal ions, the solution is neutralized by adding an alkali to make the heavy metal ions insoluble. There is a method in which a heavy metal ion is insolubilized by adding an insolubilizing agent such as a sulfide or a phosphate in addition to the alkali, and the insolubilized material is separated by solid-liquid separation or by filtration without separation.

【0004】このような無機質の不溶化物の濾過分離に
用いる濾過装置としては、砂、アンスラサイトのような
粒状濾材を充填した濾層を有する濾過装置が用いられて
おり、通常は砂とアンスラサイトを二層に積層した濾過
装置が用いられている。このような通常の二層濾過装置
では、上層に充填されるアンスラサイトは粒径0.7〜
1.4mm、充填高さが300〜500mmであり、下
層の砂層は粒径0.35〜0.7mm、充填高さ300
〜500mmであるが、出来るだけ清澄な処理水を得る
ためには粒径の小さな濾材が使用される。濁質は濾材粒
子間の空隙部に捕捉されるが、濾材が小さくなると空隙
部が狭くなるため、濁質捕捉が少なくなって、早期に閉
塞が起き、逆洗をたえず行う必要がある。その結果、運
転時間が減り、所期計画の水量が得られない場合があっ
た。このため、一般的には粒径0.45mmの砂と粒径
0.7mmのアンスラサイトの組合せが適用される場合
が多い。
[0004] As a filtration device used for filtration and separation of such inorganic insolubilized materials, a filtration device having a filter layer filled with a particulate filter material such as sand or anthracite is used. Are used in two layers. In such a usual two-layer filtration device, the anthracite filled in the upper layer has a particle size of 0.7 to 0.7.
1.4 mm, the filling height is 300 to 500 mm, the lower sand layer has a particle size of 0.35 to 0.7 mm, and the filling height is 300
Although it is about 500 mm, a filter medium having a small particle size is used in order to obtain treated water as clear as possible. The suspended matter is trapped in the gap between the filter medium particles. However, when the filter medium is small, the gap is narrowed. Therefore, the suspended matter is reduced, the clogging occurs early, and the backwashing must be constantly performed. As a result, the operation time was reduced, and the intended water volume could not be obtained in some cases. Therefore, in general, a combination of sand having a particle size of 0.45 mm and anthracite having a particle size of 0.7 mm is often applied.

【0005】しかし、捕捉される濁質と濾材との親和性
がない場合は、濁質は濾材間隙に捕捉されないで、濾材
を通り抜け、目的とする清澄な処理水が得られない場合
がある。このような場合には濾材粒径を小さくすれば解
決される場合もあるが、上記したように捕捉量は少なく
なるという問題がある。また濾材粒径を小さくしても、
濁質の濾材との親和性が低い場合は、微少の圧力変化、
流量変化でも濾材間隙を抜けていくようになり、濁質の
物性が大きく影響する場合がある。
However, when there is no affinity between the trapped turbid substance and the filter medium, the turbid substance may not pass through the filter medium but pass through the filter medium, and the target clear treated water may not be obtained. In such a case, the problem may be solved by reducing the particle size of the filter medium, but there is a problem that the trapped amount is reduced as described above. Also, even if the filter media particle size is reduced,
If the affinity of the turbid filter media is low, slight pressure changes,
Even if the flow rate changes, the liquid will pass through the filter medium gap, and the physical properties of the turbid substance may have a significant effect.

【0006】従来、濾過分離においては、濾材と被濾過
物との親和性については考慮されていなかった。一方、
無機凝集剤を添加して凝集処理を行い、析出物を加圧浮
上分離で分離する方法において、高級脂肪酸のアルカリ
金属塩を添加してフロックの安定性を高め、加圧浮上分
離を効率よく行う方法が提案されている(特開平2−3
6313号)。しかしこの方法では、高級脂肪酸アルカ
リ金属塩は加圧浮上分離におけるフロックの安定性を高
めるために用いられており、その後の濾過分離における
親和性については考慮されていない。
Hitherto, in the filtration separation, no consideration has been given to the affinity between the filter medium and the material to be filtered. on the other hand,
In a method of adding an inorganic coagulant to perform coagulation treatment and separating precipitates by pressure flotation, an alkali metal salt of a higher fatty acid is added to increase the stability of flocs and efficiently perform pressure flotation. A method has been proposed (Japanese Unexamined Patent Publication No.
No. 6313). However, in this method, the higher fatty acid alkali metal salt is used to increase the stability of the floc in the flotation under pressure, and the affinity in the subsequent filtration separation is not considered.

【0007】[0007]

【発明が解決しようとする課題】本発明の課題は、被処
理液を不溶化処理して析出する無機質の不溶化物の濾材
に対する親和性を改善して濾材による捕捉性を大きく
し、不溶化物の濾材からの漏出を防止して効率よく濾過
分離を行い清澄な濾過液を長期にわたって得ることが可
能な不溶化物分離方法を提案することである。
SUMMARY OF THE INVENTION An object of the present invention is to improve the affinity of an inorganic insolubilized substance precipitated by insolubilizing a liquid to be treated with a filter medium to increase the trapping property of the filter medium, and to improve the insolubilized filter medium. The present invention proposes a method for separating an insolubilized substance capable of preventing leakage from water and efficiently performing filtration separation to obtain a clear filtrate over a long period of time.

【0008】[0008]

【課題を解決するための手段】本発明は次の不溶化物分
離方法である。 (1) 被処理液を不溶化処理して無機質の不溶化物を
析出させ、析出した不溶化物の一部を固液分離したの
ち、または固液分離することなく、高級脂肪酸アルカリ
金属塩を添加して濾過分離を行うことを特徴とする不溶
化物分離方法。 (2) 被処理液の不溶化処理が、凝集剤の添加により
不溶化物を析出させる凝集処理である上記(1)記載の
方法。 (3) 被処理液の不溶化処理が、不溶化剤の添加によ
り被処理液中の成分を不溶化する処理である上記(1)
記載の方法。
The present invention relates to the following method for separating insolubles. (1) The solution to be treated is insolubilized to precipitate an inorganic insolubilized substance, and after a part of the precipitated insolubilized substance is subjected to solid-liquid separation or without solid-liquid separation, a higher fatty acid alkali metal salt is added. A method for separating an insolubilized substance, comprising performing filtration separation. (2) The method according to the above (1), wherein the insolubilization treatment of the liquid to be treated is an aggregation treatment in which an insolubilized substance is precipitated by adding an aggregating agent. (3) The insolubilization treatment of the liquid to be treated is a treatment for insolubilizing the components in the liquid to be treated by adding an insolubilizing agent.
The described method.

【0009】本発明において処理の対象となる被処理液
は、凝集処理、中和処理等の不溶化処理の対象となる液
である。凝集処理の対象となる被処理液としては、懸濁
物、コロイド、有機物など、無機凝集剤による凝集処理
により除去される不純物を含む液である。また中和処理
等の対象となる被処理液としては、重金属イオン等の不
純物イオンを含み、アルカリ等の不溶化剤の添加により
これらの不純物イオンが不溶化物として析出するような
液である。アルカリ以外に、硫化物、リン酸塩等の他の
不溶化剤の添加により不溶化する不純物イオン等を含む
液であってもよい。
In the present invention, the liquid to be treated is a liquid to be subjected to an insolubilization treatment such as an aggregation treatment and a neutralization treatment. The liquid to be treated to be subjected to the coagulation treatment is a liquid containing impurities, such as suspensions, colloids, and organic substances, which are removed by the coagulation treatment with an inorganic coagulant. The liquid to be treated to be subjected to the neutralization treatment or the like is a liquid which contains impurity ions such as heavy metal ions and which precipitates as insolubilized substances by the addition of an insolubilizing agent such as an alkali. In addition to the alkali, a liquid containing impurity ions or the like which are insolubilized by the addition of another insolubilizing agent such as sulfide or phosphate may be used.

【0010】本発明において、不溶化処理としては、凝
集処理のように添加した薬剤が不溶化物として析出する
処理のほか、中和処理等のように被処理液に含まれるア
ルミニウム、鉄、マンガン、銅、亜鉛等の重金属イオン
等の不純物(錯体を含む)が不溶化剤の添加により不溶
化物として析出する処理などがある。不溶化剤の添加に
より不溶化する処理にはアルカリ剤の添加による中和処
理のほかに、硫化物の添加により不溶性硫化物として析
出させる処理、リン酸または塩の添加により不溶性リン
酸塩として析出させる処理などがあげられる。
In the present invention, the insolubilization treatment includes, in addition to a treatment such as a coagulation treatment in which an added chemical is precipitated as an insolubilized material, and a treatment such as neutralization treatment in which aluminum, iron, manganese, and copper contained in the liquid to be treated are contained. In addition, there is a treatment in which impurities (including a complex) such as heavy metal ions such as zinc precipitate as insolubilized substances by adding an insolubilizing agent. The treatment for insolubilization by the addition of an insolubilizing agent is, in addition to the neutralization treatment by the addition of an alkali agent, the treatment of precipitation as an insoluble sulfide by the addition of sulfide, and the treatment of precipitation as an insoluble phosphate by the addition of phosphoric acid or a salt. And so on.

【0011】凝集処理に使用する無機凝集剤は、硫酸バ
ンド、塩基性塩化アルミニウム(PAC)、塩化鉄、硫
酸鉄などがあげられる。またこれらの無機凝集剤ととも
に用いるpH調整剤としては水酸化ナトリウム、水酸化
カリウム、水酸化カルシウム等のアルカリ剤、塩酸、硫
酸等の酸があげられる。凝集処理は被処理液に無機凝集
剤を添加し、必要によりpH調整剤を添加して最適pH
に調整し、急速攪拌および緩速攪拌を行う。これにより
凝集剤の成分は水酸化物等の不溶化物となって析出し、
フロックが形成される。
The inorganic flocculant used in the flocculation treatment includes a sulfuric acid band, basic aluminum chloride (PAC), iron chloride, iron sulfate and the like. Examples of the pH adjusting agent used together with these inorganic coagulants include alkali agents such as sodium hydroxide, potassium hydroxide and calcium hydroxide, and acids such as hydrochloric acid and sulfuric acid. In the coagulation treatment, an inorganic coagulant is added to the liquid to be treated, and if necessary, a pH adjuster is added to optimize the pH.
And stir rapidly and slowly. This causes the components of the flocculant to precipitate as insolubilized substances such as hydroxides,
Flock is formed.

【0012】中和処理に使用するアルカリ剤としては、
水酸化ナトリウム、水酸化カリウム、水酸化カルシウ
ム、炭酸ナトリウム等があげられる。また他の不溶化剤
としては硫化水素、硫化ナトリウム等の硫化物、リン酸
ナトリウム、リン酸カリウム等のリン酸塩などがあげら
れる。このほか酸化剤や無機凝集剤などを用いて不溶化
することもできる。
As the alkaline agent used for the neutralization treatment,
Examples include sodium hydroxide, potassium hydroxide, calcium hydroxide, and sodium carbonate. Other insolubilizing agents include sulfides such as hydrogen sulfide and sodium sulfide, and phosphates such as sodium phosphate and potassium phosphate. In addition, it can be insolubilized using an oxidizing agent or an inorganic coagulant.

【0013】これらの不溶化剤を用いる不溶化処理は、
被処理液に不溶化剤を添加して反応させることにより、
被処理液に含まれる重金属イオン等の不純物が水酸化
物、硫化物、リン酸塩等の不溶化物となって析出する。
錯イオンの場合には酸化剤等を併用して分解することに
より不溶化する場合もある。また無機凝集剤を併用して
凝集を行うこともできる。
[0013] The insolubilization treatment using these insolubilizing agents includes:
By adding an insolubilizer to the liquid to be treated and reacting,
Impurities such as heavy metal ions contained in the liquid to be treated are precipitated as insolubilized substances such as hydroxides, sulfides and phosphates.
In the case of a complex ion, it may be insolubilized by being decomposed in combination with an oxidizing agent or the like. Aggregation can also be performed using an inorganic coagulant in combination.

【0014】上記の凝集処理および中和処理等の不溶化
処理は化学反応のみによることもできるが、加熱、光照
射、超音波処理等の操作を加えることにより、不溶化を
促進することもできる。これらの不溶化処理により不溶
化物を析出させる場合、フロックを成長させて、大型の
フロックを形成するのが好ましいが、必ずしもフロック
を成長させなくてもよい。また有機高分子凝集剤を添加
してもよいが、添加しなくてもよい。
The insolubilization treatment such as the above-mentioned coagulation treatment and neutralization treatment can be performed only by a chemical reaction, but the insolubilization can be promoted by adding operations such as heating, light irradiation, and ultrasonic treatment. When the insolubilized substance is precipitated by these insolubilization treatments, it is preferable to grow flocs to form large flocs, but it is not always necessary to grow flocs. An organic polymer flocculant may be added, but need not be added.

【0015】上記により無機質の不溶化物を析出させた
不溶化処理液はそのまま高級脂肪酸アルカリ金属塩を添
加して濾過分離を行ってもよいが、これに先立って沈降
分離、浮上分離等の他の固液分離手段により不溶化物を
分離したのち、高級脂肪酸アルカリ金属塩を添加して濾
過分離を行うと、濾過分離における負荷を少なくするこ
とができる。沈降分離は沈降槽に滞留させて自然沈降に
より分離を行う。浮上分離は通常は起泡剤等を用いて不
溶化物に微細な気泡を付着させ、浮上させて分離する方
法であり、加圧水を用いる加圧浮上方法が好ましい。こ
のほか遠心分離等の固液分離手段を用いてもよい。
The insolubilized solution in which the inorganic insolubilized substance has been precipitated as described above may be added to the alkali metal salt of a higher fatty acid as it is and subjected to filtration and separation. However, prior to this, other solidification such as sedimentation separation and flotation separation may be performed. After separating the insolubilized product by the liquid separating means, the higher fatty acid alkali metal salt is added to perform the filtration separation, whereby the load in the filtration separation can be reduced. In the sedimentation separation, separation is performed by natural sedimentation by staying in a sedimentation tank. Floating separation is a method in which fine bubbles are usually attached to an insolubilized substance using a foaming agent or the like to separate them by floating, and a pressurized floating method using pressurized water is preferable. In addition, solid-liquid separation means such as centrifugation may be used.

【0016】本発明ではこのように不溶化物の一部を固
液分離したのち、または固液分離することなく、不溶化
処理液に高級脂肪酸アルカリ金属塩を添加して濾過分離
を行う。高級脂肪酸としてはC8〜C22、好ましくはC
12〜C20の飽和または不飽和の高級脂肪酸があげられ
る。そのアルカリ金属塩としてはナトリウム塩、カリウ
ム塩があげられる。このような高級脂肪酸アルカリ金属
塩の添加量は重量比で不溶化物量の1/5〜1/10
0、好ましくは1/10〜1/30程度とすることがで
きる。このような高級脂肪酸アルカリ金属塩は不溶化処
理前に添加すると不溶化物中に取込まれてしまうが、不
溶化処理後に添加することにより、不溶化物の表面を改
質して濾材に対する親和性を付与することができる。ま
た濾過分離の前に不溶化物の一部を固液分離する場合
は、固液分離前に添加すると高級脂肪酸アルカリ金属塩
も分離されてしまうので、固液分離後に高級脂肪酸アル
カリ金属塩を添加することにより不溶化物の表面を改質
することができる。
In the present invention, after a part of the insolubilized product is subjected to solid-liquid separation or without the solid-liquid separation, a higher fatty acid alkali metal salt is added to the insolubilized solution to carry out filtration separation. As higher fatty acids, C 8 -C 22 , preferably C
Higher fatty acids, saturated or unsaturated 12 -C 20 and the like. Examples of the alkali metal salt include a sodium salt and a potassium salt. Such higher fatty acid alkali metal salt is added in an amount of 1/5 to 1/10 of the insolubilized amount by weight.
0, preferably about 1/10 to 1/30. If such higher fatty acid alkali metal salt is added before the insolubilization treatment, it will be taken into the insolubilized material.By adding it after the insolubilization treatment, the surface of the insolubilized material is modified to impart affinity to the filter medium. be able to. When a part of the insolubilized product is subjected to solid-liquid separation before filtration and separation, if added before solid-liquid separation, the higher fatty acid alkali metal salt is also separated. Therefore, the higher fatty acid alkali metal salt is added after solid-liquid separation. Thereby, the surface of the insolubilized material can be modified.

【0017】濾過分離に用いる濾過装置は特に制限はな
いが粒状の濾材を用いるものが好ましい。粒状の濾材と
しては砂、アンスラサイトなど、従来より用いられてい
るものが用いられるが、特に砂およびアンスラサイトを
積層する二層濾過が好ましい。この場合上層に充填する
アンスラサイトは平均粒径0.7〜1.4mm、充填高
さ300〜500mm、下層の砂層は平均粒径0.35
〜0.7mm、充填高さ300〜500mmとするのが
好ましい。
There is no particular limitation on the filtration device used for the filtration separation, but a filtration device using a particulate filter medium is preferred. As the granular filter media, those conventionally used, such as sand and anthracite, are used. In particular, two-layer filtration in which sand and anthracite are laminated is preferable. In this case, the anthracite filled in the upper layer has an average particle size of 0.7 to 1.4 mm, the filling height is 300 to 500 mm, and the lower sand layer has an average particle size of 0.35.
It is preferable that the filling height is 0.7 mm and the filling height is 300 mm to 500 mm.

【0018】不溶化処理液またはその固液分離液に高級
脂肪酸アルカリ金属塩を添加して濾過分離を行うことに
より、不溶化物の濾材に対する親和性が改善されるた
め、不溶化物は濾材に捕捉されやすくなる。このため濾
材の粒径を小さくしなくても不溶化物を効率よく捕捉し
て漏出する不溶化物量を少なくし清澄な分離液を得るこ
とができる。
By adding a higher fatty acid alkali metal salt to the insolubilized liquid or the solid-liquid separation liquid and performing filtration separation, the affinity of the insolubilized substance with the filter medium is improved, so that the insoluble substance is easily captured by the filter medium. Become. For this reason, even if the particle size of the filter medium is not reduced, the insolubles can be efficiently captured and the amount of the insolubles leaking out can be reduced, and a clear separated solution can be obtained.

【0019】砂、アンスラサイト等の濾材は疎水性の濁
質に対する親和力が高いため、疎水性物質の代表的な油
を含む排水を濾過した場合、油分は濾材に強く吸着さ
れ、濾材の逆洗操作を行っても排除できない。やがては
マッドボールという現象で知られる濾材の固化が起き
る。本発明では、不溶化物の表面を疎水性にして濾材に
対する親和性を高めるという発想に基づき疎水基を持つ
有機物を吸着させる。本発明で濾過分離の対象とする不
溶化物は金属を含むものであるため、添加する有機物は
一方の端が疎水性、他端が金属との親和性を有する直鎖
状有機物が適切である。濁質の金属部分に上記の官能基
が反応し、あるいは吸着されれば、他端の疎水基は液側
に残るため、不溶化物は疎水性物質のような挙動を示し
て濾材にも吸着されやすくなるものと推測される。
Since filter media such as sand and anthracite have a high affinity for hydrophobic turbidity, when a wastewater containing oil, which is a typical hydrophobic substance, is filtered, the oil is strongly adsorbed to the filter media, and the filter media is backwashed. It cannot be ruled out by performing operations. Eventually, the solidification of the filter media, known as the mudball phenomenon, occurs. In the present invention, an organic substance having a hydrophobic group is adsorbed based on the idea that the surface of the insolubilized substance is made hydrophobic to increase the affinity for the filter medium. Since the insolubilized substance to be separated by filtration in the present invention contains a metal, the organic substance to be added is preferably a linear organic substance having one end hydrophobic and the other end having an affinity for the metal. If the above functional group reacts with or is adsorbed to the turbid metal part, the hydrophobic group at the other end remains on the liquid side, so that the insolubilized substance behaves like a hydrophobic substance and is also adsorbed to the filter medium. It is presumed that it will be easier.

【0020】[0020]

【発明の効果】以上の通り本発明によれば、不溶化物を
析出させ、高級脂肪酸アルカリ金属塩を添加して濾過分
離を行うようにしたので、被処理液を不溶化処理して析
出する無機質の不溶化物の濾材に対する親和性を改善し
て濾材による捕捉性を大きくし、不溶化物の濾材からの
漏出を防止して効率よく濾過分離を行い清澄な濾過液を
長期にわたって得ることができる。
As described above, according to the present invention, the insolubilized substance is precipitated, and the higher fatty acid alkali metal salt is added to carry out the filtration and separation. The affinity of the insolubilized substance with the filter medium is improved to enhance the trapping property of the filter medium, and the insoluble substance is prevented from leaking out of the filter medium, and is efficiently separated by filtration to obtain a clear filtrate over a long period of time.

【0021】[0021]

【発明の実施の形態】以下、本発明の実施の形態を図面
により説明する。図1(a)〜(c)は実施形態の不溶
化物分離方法を示すフロー図である。図1(a)〜
(c)において、1は不溶化槽、2は濾過槽、3は沈殿
槽、4は浮上槽である。
Embodiments of the present invention will be described below with reference to the drawings. FIGS. 1A to 1C are flowcharts showing an insolubilized matter separation method according to an embodiment. FIG. 1 (a)-
In (c), 1 is an insolubilization tank, 2 is a filtration tank, 3 is a sedimentation tank, and 4 is a floating tank.

【0022】図1(a)では不溶化槽1に被処理液路5
から被処理液を導入し、薬注路6から凝集剤または不溶
化剤を注入し、必要により薬注路7からpH調整剤その
他の薬剤を注入し、攪拌機8により攪拌して凝集処理、
中和処理等の不溶化を行う。凝集処理の場合は薬注路6
から凝集剤を注入し、薬注路7からpH調整剤を注入し
て反応させることより、凝集剤成分である無機塩の水酸
化物を主体とする不溶化物を析出させ、被処理液中の懸
濁物、コロイド、有機物等の不純物を抱き込んでフロッ
クを形成させる。中和処理その他の不溶化処理の場合
は、薬注路6からアルカリ、硫化物、リン酸塩等の不溶
化剤を注入し、必要により薬注路7から凝集剤その他の
薬剤を注入して、被処理液中の重金属イオン等と反応さ
せ、不溶化物を析出させる。
In FIG. 1A, the liquid passage 5 to be treated is
, A coagulant or an insolubilizing agent is injected from the chemical injection path 6, and a pH adjuster or other chemicals are injected from the chemical injection path 7 if necessary, and the mixture is stirred by the stirrer 8 to perform an aggregation treatment.
Perform insolubilization such as neutralization. Chemical injection route 6 for coagulation treatment
By injecting a coagulant from the solution and injecting a pH adjuster from the chemical injection path 7 to cause a reaction, thereby precipitating an insolubilized substance mainly composed of a hydroxide of an inorganic salt as a coagulant component, and Flocs are formed by incorporating impurities such as suspensions, colloids, and organic substances. In the case of the neutralization treatment or other insolubilization treatment, an insolubilizing agent such as an alkali, a sulfide, a phosphate, or the like is injected from the chemical injection path 6, and a coagulant or other chemical is injected from the chemical injection path 7 if necessary. It reacts with heavy metal ions and the like in the treatment liquid to precipitate insolubles.

【0023】不溶化処理液は移送路9から濾過槽2に送
る間に薬注路10から高級脂肪酸アルカリ金属塩を添加
して混合し、濾過槽2に導入して濾過分離を行う。濾過
槽2は上層に大粒径濾材層11としてアンスラサイトが
充填され、下層に小粒径濾材層12として砂が充填され
た2層濾過槽である。高級脂肪酸アルカリ金属塩を添加
した不溶化処理液はまず大粒径濾材層11において不溶
化物の大部分を除去され、さらに小粒径濾材層12にお
いて残留する不溶化物を除去する。このとき不溶化物は
高級脂肪酸アルカリ金属塩と結合して濾材に対する親和
性が高くなっているので、粒径の大きい濾材を使用して
も不溶化物の捕捉性は大きく、濾材層からの漏出を防止
して効率よく濾過分離を行い、清澄な濾過液を得ること
ができる。濾過分離液は処理水路13から処理水として
排出される。
The insolubilized solution is added and mixed with a higher fatty acid alkali metal salt from the chemical injection line 10 while being sent from the transfer passage 9 to the filtration tank 2, introduced into the filtration tank 2, and subjected to filtration and separation. The filtration tank 2 is a two-layer filtration tank in which an upper layer is filled with anthracite as a large-diameter filter medium layer 11 and a lower layer is filled with sand as a small-diameter filter medium layer 12. The insolubilized solution to which the higher fatty acid alkali metal salt is added first removes most of the insolubilized substance in the large-diameter filter medium layer 11 and further removes the remaining insoluble substance in the small-diameter filter medium layer 12. At this time, since the insolubilized substance binds to the higher fatty acid alkali metal salt and has a high affinity for the filter medium, even if a filter medium having a large particle size is used, the insolubilized substance is highly trapped, preventing leakage from the filter medium layer. As a result, filtration and separation can be performed efficiently, and a clear filtrate can be obtained. The filtrate is discharged from the treatment water channel 13 as treated water.

【0024】図1(b)では、不溶化槽1の不溶化処理
液は沈殿槽3で沈降分離を行った後、濾過槽2において
濾過分離を行う。この場合移送路9aから沈殿槽3に入
った不溶化処理液は自然沈降により不溶化物を沈殿させ
て、汚泥を排泥路14から排出し、分離液は移送路9b
から濾過槽2に送る間に薬注路10から高級脂肪酸アル
カリ金属塩を添加して濾過分離を行う。移送路9aに薬
注路15から高級脂肪酸アルカリ金属塩を注入すると、
大部分の高級脂肪酸アルカリ金属塩が沈殿槽3で失われ
るが、薬注路10から注入することにより濾過槽2に流
入する不溶化物の親和性の改善を効率よく行うことがで
きる。
In FIG. 1B, the insolubilized solution in the insolubilization tank 1 is settled and separated in the settling tank 3 and then filtered and separated in the filtration tank 2. In this case, the insolubilized liquid that has entered the sedimentation tank 3 from the transfer path 9a precipitates the insolubilized matter by natural settling, the sludge is discharged from the sludge discharge path 14, and the separated liquid is transferred to the transfer path 9b.
, The higher fatty acid alkali metal salt is added from the chemical injection path 10 during filtration to the filtration tank 2 to carry out filtration separation. When the higher fatty acid alkali metal salt is injected into the transfer path 9a from the chemical injection path 15,
Most of the higher fatty acid alkali metal salt is lost in the precipitation tank 3, but by injecting it from the chemical injection path 10, the affinity of the insolubilized substance flowing into the filtration tank 2 can be efficiently improved.

【0025】図1(c)では、不溶化槽1の不溶化処理
液は浮上槽4で加圧浮上分離を行った後、濾過槽2にお
いて濾過分離を行う。この場合移送路9aに加圧水路1
6から加圧水を注入して混合した不溶化処理液は浮上槽
4に入ると、減圧により発生する微細な気泡が不溶化物
に付着して浮上し、浮上分離が行われる。浮上した汚泥
は集泥部17に集められて排泥路14から排出される。
分離液は移送路9bから濾過槽2に送る間に薬注路10
から高級脂肪酸アルカリ金属塩を添加して濾過分離を行
う。移送路9aに薬注路18から高級脂肪酸アルカリ金
属塩を注入すると、大部分の高級脂肪酸アルカリ金属塩
が浮上槽4で失われるが、薬注路10から注入すること
により濾過槽2に注入する不溶化物の親和性の改善を効
率よく行うことができる。
In FIG. 1C, the insolubilized solution in the insolubilization tank 1 is subjected to pressure flotation in the flotation tank 4 and then filtered and separated in the filtration tank 2. In this case, the pressurized water channel 1
When the insolubilized solution mixed by injecting pressurized water from 6 into the floating tank 4, fine bubbles generated by depressurization adhere to the insolubilized material and float to perform floating separation. The sludge that has floated is collected in the sludge collecting section 17 and discharged from the sludge passage 14.
While the separated liquid is sent from the transfer path 9b to the filtration tank 2, the chemical injection path 10
, A higher fatty acid alkali metal salt is added thereto, followed by filtration. When the higher fatty acid alkali metal salt is injected from the chemical injection path 18 into the transfer path 9a, most of the higher fatty acid alkali metal salt is lost in the floating tank 4, but is injected into the filtration tank 2 by injection from the chemical injection path 10. The affinity of the insolubilized substance can be efficiently improved.

【0026】上記の図1(a)の処理は不溶化物の少な
い場合に適し、図1(b)の処理は重質の不溶化物が多
く生成する場合に適し、図1(c)の処理は軽質の不溶
化物が多く生成する場合に適する。濾過処理水を回収利
用する場合、さらに後段に、活性炭処理あるいは精密濾
過等を設置することができる。また純水として回収する
場合は、イオン交換樹脂、逆浸透膜装置等を設置するこ
とができる。これらの場合はファウリングを防止するた
めに濾過処理水はできるだけ清澄な方が良い。
The above-described processing of FIG. 1A is suitable for a case where the amount of insoluble matter is small, the processing of FIG. 1B is suitable for a case where a large amount of heavy insoluble matter is generated, and the processing of FIG. Suitable when a lot of light insolubilized substances are produced. When the filtered water is recovered and used, an activated carbon treatment or a microfiltration can be further provided at a later stage. When collecting as pure water, an ion exchange resin, a reverse osmosis membrane device, or the like can be installed. In these cases, the filtered water should be as clear as possible to prevent fouling.

【0027】図1(a)〜(c)の処理では、いずれの
場合も濾過分離を行う前の不溶化処理液に高級脂肪酸ア
ルカリ金属塩を添加するため、被処理液を不溶化処理に
析出する無機質の不溶化物の濾材に対する親和性を改善
して濾材による捕捉性を大きくし、不溶化物の濾材から
の漏出を防止して効率よく濾過分離を行い、清澄な濾過
液を長期にわたって得ることができる。
In any of the treatments shown in FIGS. 1 (a) to 1 (c), since the higher fatty acid alkali metal salt is added to the insolubilized solution before filtration and separation, the liquid to be treated is separated from the inorganic solution precipitated in the insolubilization process. The affinity of the insolubilized substance with the filter medium is improved to increase the trapping property of the filter medium, the insoluble substance is prevented from leaking out of the filter medium, and the filtration is efficiently performed, whereby a clear filtrate can be obtained over a long period of time.

【0028】[0028]

【実施例】以下、本発明の実施例について説明する。実
施例における処理液の清澄性は、MFチェック法により
ミリポア社製の孔径0.45μmの精密濾過膜を用い試
料水1literを濾過し、濾過時間をMF時間(単位
〔分:秒〕)で表示した。
Embodiments of the present invention will be described below. In the examples, the clarity of the processing solution was determined by the MF check method using a microfiltration membrane having a pore size of 0.45 μm manufactured by Millipore to filter 1 liter of sample water, and the filtration time was indicated in MF time (unit: [minute: second]). did.

【0029】実施例1、比較例1 被処理液として地下水(pH7.5、電気伝導度:21
mS/m、Mアルカリ度:95mg/l(CaCO3
して)、濁度:1.8度、色度:12度、Fe:0.6
mg/l)を用い図1(a)の方法で処理を行った。不
溶化槽では塩素2mg/lと液体硫酸バンド10mg/
lを添加して、処理水量110m3/hr、反応時間1
0分間で凝集処理を行った。この不溶化処理液に高級脂
肪酸アルカリ金属塩としてオレイン酸系複合石ケンを
0.2mg/l添加した場合(実施例1)と、添加しな
かった場合(比較例1)について、濾過槽で濾過分離を
行った。濾過槽は粒径0.9mmのアンスラサイトを3
50mmの高さに充填した上層と、粒径0.45mmの
砂を350mmの高さに充填した下層の二層濾過であ
り、LV6.5m/hrで濾過を行った。処理液のMF
時間(液温12℃、真空度67kPa、ブランクとして
蒸留水1literの濾過時間は2分04秒である)による
濾過時間を表1に示す。
Example 1, Comparative Example 1 Groundwater (pH 7.5, electric conductivity: 21) was used as the liquid to be treated.
mS / m, M alkalinity: 95 mg / l (as CaCO 3 ), turbidity: 1.8 degrees, chromaticity: 12 degrees, Fe: 0.6
mg / l) and the treatment was performed by the method shown in FIG. In the insolubilization tank, chlorine 2 mg / l and liquid sulfuric acid band 10 mg /
l, and the treated water amount is 110 m 3 / hr, and the reaction time is 1
Aggregation treatment was performed for 0 minutes. In the insolubilized solution, 0.2 mg / l of an oleic acid-based complex soap was added as a higher fatty acid alkali metal salt (Example 1), and the case where it was not added (Comparative Example 1) was separated by filtration in a filtration tank. Was done. The filtration tank contains 3 anthracite particles with a particle size of 0.9 mm.
This was a two-layer filtration of an upper layer filled to a height of 50 mm and a lower layer filled to a height of 350 mm with sand having a particle size of 0.45 mm. Filtration was performed at LV 6.5 m / hr. MF of treatment liquid
Table 1 shows the filtration time by time (liquid temperature: 12 ° C., degree of vacuum: 67 kPa, filtration time of 1 liter of distilled water as a blank is 2 minutes and 04 seconds).

【0030】[0030]

【表1】 [Table 1]

【0031】実施例2、比較例2 図1(c)に示す方法において脂肪酸石ケンの添加位置
の効果と検討した。被処理液は湖沼水(pH7.8、電
気伝導度:12mS/m、Mアルカリ度:40mg/l
(CaCO3として)、濁度:4.5度、色度:20
度、SS:6.0mg/l)であり、不溶化槽において
ポリ塩化アルミニウムを25mg/lで添加し、処理水
量80m3/hr、反応時間10分で、凝集処理を行っ
た後、浮上槽において加圧浮上処理を行った。加圧浮上
処理は加圧水(350kPa・・・ゲージ圧)を原水/加
圧水=10/2の割合で注入し、浮上LV7m/hrで
浮上分離した。濾過槽は砂層0.45mm、充填高さ3
50mm、アンスラサイト部0.9mm、充填高さ35
0mm、LV5m/hrである。脂肪酸石ケン(オレイ
ン酸系複合石ケン)の添加位置を薬注路10にした場合
(実施例2)と薬注路18にした場合(比較例2)とに
ついて処理水の添加量によるMF時間(液温15℃、真
空度67kPa、ブランクとして蒸留水1 literの濾過
時間は2分01秒である)の差を表2に示す。
Example 2, Comparative Example 2 The effect of the addition position of the fatty acid soap in the method shown in FIG. The liquid to be treated is lake water (pH 7.8, electric conductivity: 12 mS / m, M alkalinity: 40 mg / l)
(As CaCO 3 ), turbidity: 4.5 degrees, chromaticity: 20
(SS, 6.0 mg / l), polyaluminum chloride was added at 25 mg / l in the insolubilization tank, and the coagulation treatment was performed at a treatment water volume of 80 m 3 / hr for a reaction time of 10 minutes. A pressure levitation treatment was performed. In the pressure levitation treatment, pressurized water (350 kPa... Gauge pressure) was injected at a ratio of raw water / pressurized water = 10/2, and levitation separation was performed at a levitation LV of 7 m / hr. Filtration tank is sand layer 0.45mm, filling height 3
50mm, anthracite part 0.9mm, filling height 35
0 mm and LV 5 m / hr. The MF time depending on the amount of treated water when the fatty acid soap (oleic acid-based complex soap) is added at the chemical injection route 10 (Example 2) and when the fatty acid soap is added at the chemical injection route 18 (Comparative Example 2). Table 2 shows the difference between the liquid temperature of 15 ° C., the degree of vacuum of 67 kPa, and the filtration time of 1 liter of distilled water as a blank is 2 minutes 01 seconds.

【0032】[0032]

【表2】 [Table 2]

【0033】表1の結果より高級脂肪酸塩を添加した実
施例1では蒸留水レベルの水質を12時間にわたって確
保できたが、高級脂肪酸塩を添加しない比較例1では、
3時間以下であった。また表2の結果より、浮上槽の入
口側に高級脂肪酸塩を添加する比較例2よりも、浮上槽
の出口側に高級脂肪酸塩を添加する実施例2の方が少な
い薬剤量で長時間にわたって濾過分離の優れた効果を得
られることがわかる。
From the results shown in Table 1, in Example 1 in which the higher fatty acid salt was added, the water quality at the level of distilled water could be ensured for 12 hours. In Comparative Example 1 in which the higher fatty acid salt was not added,
3 hours or less. Also, from the results in Table 2, Example 2 in which the higher fatty acid salt is added to the outlet side of the floating tank has a smaller amount of drug for a longer time than Comparative Example 2 in which the higher fatty acid salt is added to the inlet side of the floating tank. It can be seen that an excellent effect of filtration separation can be obtained.

【図面の簡単な説明】[Brief description of the drawings]

【図1】(a)−(c)はそれぞれ別の実施形態の不溶
化物分離方法を示すフロー図である。
1 (a) to 1 (c) are flow charts showing an insolubilized matter separation method according to another embodiment.

【符号の説明】[Explanation of symbols]

1 不溶化槽 2 濾過槽 3 沈澱槽 4 浮上槽 5 被処理液路 6、7、10、15、18 薬注路 8 攪拌機 9、9a、9b 移送路 11 大粒径濾材層 12 小粒径濾材層 13 処理水路 14 排泥路 16 加圧水路 DESCRIPTION OF SYMBOLS 1 Insolubilization tank 2 Filtration tank 3 Precipitation tank 4 Floating tank 5 Liquid path to be processed 6, 7, 10, 15, 18 Chemical injection path 8 Agitator 9, 9a, 9b Transfer path 11 Large-diameter filter medium layer 12 Small-diameter filter medium layer 13 Treatment water passage 14 Drainage passage 16 Pressurized water passage

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D037 AA01 AB08 BA02 BB07 CA02 CA08 CA14 4D038 AA02 AB60 AB66 AB68 AB69 AB79 AB80 BB01 BB04 BB07 BB13 BB17 BB18  ──────────────────────────────────────────────────続 き Continued on the front page F term (reference) 4D037 AA01 AB08 BA02 BB07 CA02 CA08 CA14 4D038 AA02 AB60 AB66 AB68 AB69 AB79 AB80 BB01 BB04 BB07 BB13 BB17 BB18

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 被処理液を不溶化処理して無機質の不溶
化物を析出させ、析出した不溶化物の一部を固液分離し
たのち、または固液分離することなく、高級脂肪酸アル
カリ金属塩を添加して濾過分離を行うことを特徴とする
不溶化物分離方法。
1. An insolubilizing treatment of a liquid to be treated to precipitate an inorganic insolubilized substance, and after adding a solid-liquid separation to a part of the precipitated insolubilized substance, or adding a higher fatty acid alkali metal salt without solid-liquid separation. And separating the solution by filtration.
【請求項2】 被処理液の不溶化処理が、凝集剤の添加
により不溶化物を析出させる凝集処理である請求項1記
載の方法。
2. The method according to claim 1, wherein the insolubilization treatment of the liquid to be treated is a coagulation treatment in which an insolubilized substance is precipitated by adding a coagulant.
【請求項3】 被処理液の不溶化処理が、不溶化剤の添
加により被処理液中の成分を不溶化する処理である請求
項1記載の方法。
3. The method according to claim 1, wherein the insolubilizing treatment of the liquid to be treated is a treatment for insolubilizing components in the liquid to be treated by adding an insolubilizing agent.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005224686A (en) * 2004-02-12 2005-08-25 Maezawa Ind Inc Arsenic removal method
JP2013031810A (en) * 2011-08-02 2013-02-14 Kobelco Eco-Maintenance Co Ltd Method and apparatus for treating zinc-containing wastewater

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005224686A (en) * 2004-02-12 2005-08-25 Maezawa Ind Inc Arsenic removal method
JP4567344B2 (en) * 2004-02-12 2010-10-20 前澤工業株式会社 How to remove arsenic
JP2013031810A (en) * 2011-08-02 2013-02-14 Kobelco Eco-Maintenance Co Ltd Method and apparatus for treating zinc-containing wastewater

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