JP3751779B2 - Production method of flocculant for water treatment - Google Patents
Production method of flocculant for water treatment Download PDFInfo
- Publication number
- JP3751779B2 JP3751779B2 JP28464499A JP28464499A JP3751779B2 JP 3751779 B2 JP3751779 B2 JP 3751779B2 JP 28464499 A JP28464499 A JP 28464499A JP 28464499 A JP28464499 A JP 28464499A JP 3751779 B2 JP3751779 B2 JP 3751779B2
- Authority
- JP
- Japan
- Prior art keywords
- flocculant
- water treatment
- water
- silicic acid
- concentration
- 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
Links
Images
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Description
【0001】
【発明の属する技術分野】
本発明は、水中から不純物を除去するための水処理用凝集剤の製造方法に関する。
【0002】
【従来の技術】
近年、上水道水源の有機物汚染などが進行しているため、汚染物質の凝集除去のための高性能の凝集剤が要望されているが、日本で広く使われているポリ塩化アルミニウム(PAC)や硫酸アルミニウムなどのアルミニウム系凝集剤は、処理水中に残留すると、アルツハイマー症などの神経系疾患を引き起こす懸念があることが指摘されている。また、塩化第二鉄や硫酸第二鉄などのアルミニウム以外の金属を含む無機系凝集剤の使用も期待されているが、凝集効果がPACより劣る等の難点がある。
【0003】
一方、ポリアクリルアミドなどの合成有機高分子凝集剤を鉄塩凝集剤と併用して凝集効果の改善を図る方法も考えられているが、合成有機高分子凝集剤に含まれるモノマーは毒性を有しているため、現在日本では上水道関係での使用は許可されていない。
【0004】
本出願人は、すでに、安全性に懸念が無く、かつ、凝集効果の高い無機高分子凝集剤として、重合ケイ酸と鉄塩を含む凝集剤を提案しており(特許第1783473号、特許第2732067号及び特許第2759853号)、これらの特許にかかる技術については、地球上の随所で入手しえるケイ素含有資源を利用しうる利点の観点からも、大きな関心が寄せられている。
【0005】
【発明が解決しようとする課題】
上記の各特許で提案されている技術については、その凝集剤が本来的に不安定な状態となりがちであるため、製造場所と使用場所との間の輸送や貯蔵の観点、或いは大量生産上の観点から、なお問題が残されている。
【0006】
すなわち、凝集剤の凝集効果をPACと同じ程度にするためにSi濃度等の有効成分濃度を高くすると、安定状態で保管しうる期間が比較的短くなるため、水処理現場での使用の都度、遠隔地の製造工場で製造して直ちに水処理現場まで運搬しなければならなくなるおそれがあった。一方、水処理現場で比較的長期間保存できるように有効成分濃度を低くすると、製造凝集剤の量が著しく増加し、輸送コストが嵩んだり、水処理現場に著しく大容量の貯蔵タンクを建設しておく必要が生じるおそれがあった。
【0007】
前記第2759853号特許では、高濃度でしかも安定性の高い凝集剤が提案されているが、製造過程でイオン交換樹脂を用いる処理を行う必要があるため、製造コストの上昇を招くおそれがあった。また、大量生産上の問題として、一般に、ケイ酸溶液を用いる凝集剤製造中に原料がゲル化しないように重合処理を行うためには、常に適切なpH値を維持する必要があるが、大量生産の場合には、pH値の厳密なコントロールが必ずしも容易ではない場合もある。
【0008】
さらに、重合ケイ酸と鉄塩からなる凝集剤中における両者(ケイ素と鉄分)の含有比率は、処理対象水の性状、性質等により最適値が変化する。したがって、製造工場で両者の比率を一定にして製造した凝集剤が、使用現場での処理対象水には必ずしも最善の凝集効果を生じない場合がある。
【0009】
本発明は、従来技術における上記のような難点を回避し、使用現場においても、使用対象水に対して最善の効果を有する凝集剤が得られるような、水処理用凝集剤の製造方法を提供することを目的とする。
【0010】
【課題を解決するための手段】
本発明においては、通常は非重合帯域として扱われている低いpH値を有する、pH1ないし2の強酸性のものとしたケイ酸溶液を、常温よりも著しく高い50℃ないし80℃に加熱し、その状態で撹拌することによって重合させる手段が用いられる。すなわち、本発明の方法は、pH値が約1.0ないし2.0の酸性ケイ酸溶液を、約50℃ないし80℃に加熱した状態下において撹拌して重合ケイ酸とした後、これに塩化第2鉄を添加することからなる、水処理用凝集剤の製造方法であり(請求項1)、また、上記の製記方法において、酸性ケイ酸溶液中のケイ素(Si)濃度を約2.5ないし3.5重量%とする、水処理用凝集剤製造方法(請求項2)である。
【0011】
【発明の実施の形態】
従来、ケイ酸溶液を重合させて凝集剤とする際には、常温下で、Si濃度とpH値をどのように設定して重合操作を行うかという点にとらわれていたが、本発明においては、あえて重合処理には適しないと考えられていた低いpH値を維持したまま、それを常温よりも著しく高い温度に加熱した状態で重合を行うという、従来の先入観からすれば意外な手段を用いたことにより、重合操作が容易な製造装置を、水処理現場に設置することを可能にし、それにより、常に最適な仕様の凝集剤を製造して直ちに使用することを可能にする。
【0012】
【実施例】
図1のフローシートに示す装置を用いて凝集剤を製造した。図1において、1は水ガラス貯留槽(100l)、2は塩酸貯留槽(50l)、3は塩化第二鉄貯留槽(100l)、4は希釈用水貯留槽(100l)、5は凝集剤希釈貯留槽(300l)、6は撹拌重合反応槽(内容積75l)である。初期段階では、バルブV1ないしV9は全て閉、定量ポンプP1〜P6は停止、撹拌機7及び8は停止、ヒーター10は停止状態で、凝集剤希釈貯留槽5以外の槽類には、所定の薬品又は水道水が満たされている。
【0013】
▲1▼バルブV1およびV4を開き、定量ポンプP1およびP4の吐出量を、それぞれ605ml/minおよび1140ml/minで同時に10分間運転し、インラインミキサー9で撹拌・混合された希塩酸溶液を撹拌重合反応槽6に移送する。移送後、バルブV1およびV4を閉にし、撹拌重合反応槽6の撹拌機7を運転開始する。
【0014】
▲2▼次いで、バルブV2およびV5を開き、定量ポンプP2およびP4の吐出量を、それぞれ110ml/minおよび292ml/minで運転し、インラインミキサー10で撹拌・混合してSi濃度を4.6%に調整した水ガラス希釈溶液を402ml/minの割合で撹拌重合反応槽6中で撹拌されている10%塩酸に120分間滴下する。滴下後、定量ポンプP2およびP4の運転を停止し、バルブV2およびV5を閉にする。滴下終了後の内容物は、pH1.3〜1.5、Si濃度約3.4%の酸性ケイ酸溶液であった。
【0015】
▲3▼次いで、撹拌重合反応槽6の撹拌を継続しつつヒーター11で60℃まで加熱し、そのままの状態を90分間継続して重合を促進し、重合ケイ酸を調製した。
【0016】
▲4▼重合終了後、ヒーター11での加熱を停止し、バルブV3を開き定量ポンプP3を用いて、塩化第二鉄溶9.38lを撹拌重合反応槽6中に投入する。塩化第二鉄溶投入終了後、定量ポンプP3を停止し、バルブV3を閉にして、重合ケイ酸溶液と塩化第二鉄水溶液を十分に撹拌、混合して凝集剤を得、凝集剤製造終了後、撹拌機を運転停止した。ここで製造された凝集剤は、Si濃度2.9%、鉄濃度1.9%(as Fe)、モル比が3:1(Si:Fe)、極限粘度数は0.38(100ml/g)で、高い凝集性能を有していた。
【0017】
▲5▼製造された凝集剤をそのまま使用する場合は、バルブV6を開けて定量注入ポンプP5で所定量原水に注入して凝集処理する。また、製造した凝集剤を一時貯留しておく場合は、バルブV7を開けて定量注入ポンプP5で凝集剤を凝集剤希釈貯留槽5に移送する。次いで、バルブ8を開け定量注入ポンプ4で、凝集剤の2倍量の水道水を注入して撹拌して凝集剤を1/3の濃度に希釈し、必要に応じてバルブV9を開けて定量注入ポンプP6で所定量処理対象原水に注入する。
【0018】
【発明の効果】
本発明の製造方法によれば、重合ケイ酸と鉄塩を含有する、安全性と凝集効果が高く、しかも原料の入手が容易な水処理用凝集剤を、pH値の厳密なコントロールという煩わしい操作を避けて大量に製造することができるので、凝集剤を、水処理現場に設置する簡便な装置によって製造することができ、それにより、常に処理対象水に適した成分仕様を有する必要量の凝集剤の製造を可能にするものである。
【図面の簡単な説明】
【図1】 本発明方法の一実施例のフローシート。
【符号の説明】
1・・・・・ 水ガラス貯留槽
2・・・・・ 塩酸貯留槽
3・・・・・ 塩化第二鉄貯留槽
4・・・・・ 希釈用水貯留槽
5・・・・・ 凝集剤希釈貯留槽
6・・・・・ 撹拌重合反応槽
7.8・・・ 撹拌機
9.10・・・ インラインミキサー
11・・・・・ ヒーター
V1〜V9‥‥バルブ
P1〜P6‥‥定量ポンプ
M1.M2‥‥‥モーター[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for producing a flocculant for water treatment for removing impurities from water.
[0002]
[Prior art]
In recent years, due to the progress of organic pollution in water supply sources, high-performance flocculants for coagulation removal of pollutants are required. Polyaluminum chloride (PAC) and sulfuric acid widely used in Japan It has been pointed out that aluminum flocculants such as aluminum may cause neurological diseases such as Alzheimer's disease if they remain in the treated water. In addition, the use of inorganic flocculants containing metals other than aluminum, such as ferric chloride and ferric sulfate, is also expected, but there are drawbacks such that the agglomeration effect is inferior to PAC.
[0003]
On the other hand, a method of improving the aggregation effect by using a synthetic organic polymer flocculant such as polyacrylamide in combination with an iron salt flocculant is also considered, but the monomer contained in the synthetic organic polymer flocculant has toxicity. Therefore, in Japan, it is not permitted to use in waterworks.
[0004]
The present applicant has already proposed a flocculant containing polymerized silicic acid and an iron salt as an inorganic polymer flocculant having no concern about safety and having a high flocculation effect (Japanese Patent No. 1783473, Patent No. 1). No. 2732067 and Japanese Patent No. 2,759,853), and the technology related to these patents is also of great interest from the viewpoint of the advantage of utilizing silicon-containing resources available everywhere on the earth.
[0005]
[Problems to be solved by the invention]
Regarding the technologies proposed in the above patents, the flocculant tends to be inherently unstable, so that it can be transported and stored between the production site and the use location, or in mass production. From the point of view, problems still remain.
[0006]
That is, when the active ingredient concentration such as Si concentration is increased in order to make the flocculating effect of flocculating agent the same as PAC, the period of storage in a stable state is relatively short. There was a risk that it would have to be manufactured at a remote manufacturing plant and transported immediately to the water treatment site. On the other hand, if the concentration of the active ingredient is lowered so that it can be stored for a relatively long period of time at the water treatment site, the amount of the production flocculant increases significantly, transportation costs increase, and a remarkably large storage tank is constructed at the water treatment site. It may be necessary to keep it.
[0007]
In the aforementioned 2775953 patent, a high concentration and high stability flocculant is proposed, but it is necessary to perform treatment using an ion exchange resin in the production process, which may cause an increase in production cost. . Further, as a problem in mass production, in general, in order to perform polymerization treatment so that the raw material does not gel during the production of the flocculant using a silicic acid solution, it is necessary to always maintain an appropriate pH value. In the case of production, strict control of the pH value may not always be easy.
[0008]
Furthermore, the optimum value of the content ratio of both (silicon and iron) in the flocculant composed of polymerized silicic acid and iron salt varies depending on the properties and properties of the water to be treated. Therefore, a coagulant produced at a manufacturing factory with a constant ratio may not always produce the best coagulation effect for water to be treated at the site of use.
[0009]
The present invention provides a method for producing a coagulant for water treatment that avoids the above-mentioned difficulties in the prior art and that provides a coagulant having the best effect on the water to be used even at the site of use. The purpose is to do.
[0010]
[Means for Solving the Problems]
In the present invention, a silicic acid solution having a low pH value, usually treated as a non-polymerization zone, and having a strongly acidic pH of 1 to 2, is heated to 50 ° C. to 80 ° C., which is significantly higher than room temperature, A means for polymerizing by stirring in that state is used. That is, in the method of the present invention, an acidic silicic acid solution having a pH value of about 1.0 to 2.0 is stirred in a state heated to about 50 ° C. to 80 ° C. to obtain polymerized silicic acid. A method for producing a flocculant for water treatment comprising adding ferric chloride (Claim 1). In the above-mentioned production method, the concentration of silicon (Si) in the acidic silicic acid solution is about 2 A method for producing a flocculant for water treatment, wherein the content is from 5 to 3.5% by weight (Claim 2).
[0011]
DETAILED DESCRIPTION OF THE INVENTION
Conventionally, when a silicic acid solution is polymerized to form a flocculant, it has been constrained by how to set the Si concentration and pH value at room temperature to perform the polymerization operation. In view of the conventional preconception that polymerization is carried out while maintaining a low pH value, which was thought to be unsuitable for polymerization treatment, while being heated to a temperature significantly higher than room temperature, an unexpected means is used. Therefore, it is possible to install a production apparatus that can be easily polymerized at a water treatment site, thereby always allowing an optimum specification of the flocculant to be produced and used immediately.
[0012]
【Example】
The flocculant was manufactured using the apparatus shown in the flow sheet of FIG. In FIG. 1, 1 is a water glass reservoir (100 l), 2 is a hydrochloric acid reservoir (50 l), 3 is a ferric chloride reservoir (100 l), 4 is a dilution water reservoir (100 l), and 5 is a flocculant dilution. A storage tank (300 l) and 6 are stirring polymerization reaction tanks (internal volume 75 l). In the initial stage, all the valves V1 to V9 are closed, the metering pumps P1 to P6 are stopped, the
[0013]
(1) Valves V1 and V4 are opened, and the discharge rates of metering pumps P1 and P4 are simultaneously operated at 605 ml / min and 1140 ml / min for 10 minutes, respectively, and the dilute hydrochloric acid solution stirred and mixed by in-
[0014]
(2) Next, the valves V2 and V5 are opened, the discharge rates of the metering pumps P2 and P4 are respectively operated at 110 ml / min and 292 ml / min, and stirred and mixed by the in-
[0015]
(3) Next, while stirring in the
[0016]
(4) After completion of the polymerization, the heating in the heater 11 is stopped, the valve V3 is opened, and 9.38 l of ferric chloride is introduced into the
[0017]
{Circle around (5)} When the produced flocculant is used as it is, the valve V6 is opened, and a predetermined amount is injected into the raw water by the metering injection pump P5 to agglomerate. When the produced flocculant is temporarily stored, the valve V7 is opened and the flocculant is transferred to the flocculant
[0018]
【The invention's effect】
According to the production method of the present invention, a water treatment flocculant containing polymerized silicic acid and an iron salt, which has high safety and agglomeration effect and is easily available for raw materials, is a troublesome operation of strict control of pH value. The flocculant can be produced by a simple device installed at the water treatment site, so that the required amount of coagulation that always has the component specifications suitable for the water to be treated can be produced. This makes it possible to produce an agent.
[Brief description of the drawings]
FIG. 1 is a flow sheet of an embodiment of the method of the present invention.
[Explanation of symbols]
DESCRIPTION OF
Claims (1)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP28464499A JP3751779B2 (en) | 1999-08-31 | 1999-08-31 | Production method of flocculant for water treatment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP28464499A JP3751779B2 (en) | 1999-08-31 | 1999-08-31 | Production method of flocculant for water treatment |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2001070708A JP2001070708A (en) | 2001-03-21 |
JP3751779B2 true JP3751779B2 (en) | 2006-03-01 |
Family
ID=17681146
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP28464499A Expired - Lifetime JP3751779B2 (en) | 1999-08-31 | 1999-08-31 | Production method of flocculant for water treatment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3751779B2 (en) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP4014896B2 (en) | 2001-05-25 | 2007-11-28 | 株式会社トクヤマ | Method for producing flocculant for water treatment |
JP4537365B2 (en) * | 2006-10-12 | 2010-09-01 | 水道機工株式会社 | Method and apparatus for producing water treatment flocculant |
KR20090024711A (en) * | 2007-05-11 | 2009-03-09 | 가부시끼가이샤 도꾸야마 | Processes for production of iron-silica coagulants for water treatment |
-
1999
- 1999-08-31 JP JP28464499A patent/JP3751779B2/en not_active Expired - Lifetime
Also Published As
Publication number | Publication date |
---|---|
JP2001070708A (en) | 2001-03-21 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP4014896B2 (en) | Method for producing flocculant for water treatment | |
CN103588272B (en) | A kind of preparation method of inorganic flocculating agent and utilize the enhanced coagulation method of its process low-temperature and low turbidity height organism water body | |
US7959800B2 (en) | Method for preparing acidic solutions of activated silica for water treatment | |
JP3751779B2 (en) | Production method of flocculant for water treatment | |
CN104098164B (en) | The synchronous silica removal of a kind of refinery waste water is except the method for COD | |
JP4410221B2 (en) | Method and apparatus for producing water treatment flocculant | |
CN107324466A (en) | Method is prepared in situ in a kind of river course water treatment coagulant | |
JP2003170174A (en) | Coagulating filtration method and system | |
CN105565453B (en) | A kind of preparation method and application of compound coagulant for Treatment of Wastewater With Manganese | |
JP4353983B2 (en) | Water treatment flocculant manufacturing equipment | |
CN100375712C (en) | Double-formulation polysilicate coagulant preparation method | |
JP3700892B2 (en) | Method for producing flocculant | |
KR102017114B1 (en) | Manufacturing method of polyaluminum chloride | |
KR101920987B1 (en) | Polyaluminium chloride coagulants having low basicity and manufacturing method thereof | |
KR101938467B1 (en) | Polyaluminium chloride coagulants having neutral basicity and manufacturing method thereof | |
KR101695677B1 (en) | Polyaluminium chloride coagulants having neutral basicity and manufacturing method thereof | |
JP2001293483A (en) | Water treating method | |
CN105601771B (en) | Microwave radiation technology prepares polyacrylamide glutathione aluminium chloride method and application | |
KR102086419B1 (en) | Manufacturing apparatus of polyaluminum chloride | |
CN108249537A (en) | A kind of sewage disposal precipitating reagent and its processing method | |
KR102017116B1 (en) | Polyaluminum chloride and water treatment method using same | |
KR100497104B1 (en) | Powdery Coagulant Composition | |
JPS62294489A (en) | Treatment of aqueous suspension and flocculant treatment apparatus | |
AU2006235901B2 (en) | Method for Preparing Acidic Solutions of Activated Silica and Polyvalent Metal Salt for Water Treatment | |
CN105645546A (en) | Efficient coagulant special for emulsified oil wastewater and preparation method thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20050830 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20050913 |
|
A521 | Written amendment |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20051109 |
|
TRDD | Decision of grant or rejection written | ||
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20051206 |
|
A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20051208 |
|
R150 | Certificate of patent or registration of utility model |
Ref document number: 3751779 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20081216 Year of fee payment: 3 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20091216 Year of fee payment: 4 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20091216 Year of fee payment: 4 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20101216 Year of fee payment: 5 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20101216 Year of fee payment: 5 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20111216 Year of fee payment: 6 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20121216 Year of fee payment: 7 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20121216 Year of fee payment: 7 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20131216 Year of fee payment: 8 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
EXPY | Cancellation because of completion of term |