JP2607543Y2 - Hardness component and soluble metal removal device with permeable membrane - Google Patents
Hardness component and soluble metal removal device with permeable membraneInfo
- Publication number
- JP2607543Y2 JP2607543Y2 JP1993021170U JP2117093U JP2607543Y2 JP 2607543 Y2 JP2607543 Y2 JP 2607543Y2 JP 1993021170 U JP1993021170 U JP 1993021170U JP 2117093 U JP2117093 U JP 2117093U JP 2607543 Y2 JP2607543 Y2 JP 2607543Y2
- Authority
- JP
- Japan
- Prior art keywords
- water
- raw water
- soluble metal
- hardness
- membrane
- 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 - Fee Related
Links
Description
【0001】[0001]
【産業上の利用分野】この考案は、精密ろ過膜もしくは
限外ろ過膜の透過膜により、飲料水を製造する装置に関
するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for producing drinking water by means of a microfiltration membrane or an ultrafiltration membrane.
【0002】[0002]
【従来の技術】従来、精密ろ過膜もしくは限外ろ過膜を
利用した、ろ過操作は行なわれてきた。これらの透過膜
によれば、非溶解性物質はほぼ100%除去できるが、
硬度成分やマンガン等の溶解性金属は除去できないとい
う欠点があり、そのため硬度成分やマンガン等の溶解性
成分を含んだ原水は、これらの透過膜では水質基準に適
合した水処理ができないという欠点があつた。2. Description of the Related Art Conventionally, filtration operations using a microfiltration membrane or an ultrafiltration membrane have been performed. According to these permeable membranes, almost 100% of insoluble substances can be removed.
There is a drawback that soluble components such as hardness components and manganese cannot be removed.Therefore, raw water containing soluble components such as hardness components and manganese cannot be subjected to water treatment that conforms to water quality standards with these permeable membranes. Atsuta.
【0003】一方、水中の硬度成分や溶解性金属は、p
Hを上昇させると析出するという性質を利用し、原水の
pHを上げ、凝集沈澱や砂ろ過により除去する方法があ
つたが、凝集沈澱や砂ろ過では析出した物質の完全除去
ができなかつたため、pHを中和したときに残留してい
る析出物質が再度溶解してしまい、硬度成分や金属類の
除去率が低いという欠点があつた。On the other hand, the hardness component and soluble metal in water are p
Utilizing the property of precipitation when H is raised, there was a method of raising the pH of raw water and removing it by coagulation sedimentation or sand filtration. When the pH was neutralized, the remaining precipitates were redissolved again, resulting in a low removal rate of hardness components and metals.
【0004】[0004]
【考案が解決しようとする課題】透過膜は、非溶解性物
質をほぼ100%除去できる。このため、硬度成分や一
部金属類などの溶解性成分は、析出さえさせられればほ
ぼ完璧に除去できる。The permeable membrane can remove almost 100% of insoluble substances. For this reason, soluble components such as hardness components and some metals can be almost completely removed as long as they are precipitated.
【0005】[0005]
【課題を解決するための手段】ここにおいてこの考案
は、硬度成分及び溶解性金属を含んだ原水に、消石灰、
カセイソーダもしくはソーダ灰等のアルカリ剤を注入
し、又は石灰系粒子を充填した水槽もしくは消石灰を溶
解した水槽を通過させて、原水のpHを上昇させること
により、原水中の硬度成分及び溶解性金属を析出させ、
これを限外ろ過膜もしくは精密ろ過膜で透過し、透過水
を炭酸ガスもしくは酸性薬品で再度pHを中性付近まで
中和させることを特徴とする、上水道における透過膜に
よる硬度成分及び溶解性金属除去装置を提案するもので
ある。SUMMARY OF THE INVENTION Here, the present invention relates to a method of adding slaked lime to raw water containing a hardness component and a soluble metal.
By injecting an alkaline agent such as caustic soda or soda ash, or passing through a water tank filled with lime-based particles or a water tank in which slaked lime is dissolved, the pH of the raw water is increased, and the hardness components and soluble metals in the raw water are reduced. Precipitate,
This is permeated through an ultrafiltration membrane or a microfiltration membrane, and the pH of the permeated water is neutralized again with carbon dioxide or an acidic chemical to near neutrality. The present invention proposes a removing device.
【0006】水中に溶解している重金属成分は、一般
に、溶解しているイオンをアルカリ剤によりpHを上げ
ると、その金属に応じたpHのところで析出し、懸濁物
となる。代表的な硬度成分であるカルシウムは、pH1
2〜13程度でなければ析出しないが、消石灰でpHを
上げると、pH10.8程度で炭酸カルシウムとして析
出する。この場合、水中の溶解性カルシウム分は若干残
るが、上水道として必要なレベルを下回る。[0006] When the pH of dissolved ions is increased by an alkaline agent, the heavy metal component dissolved in water is generally precipitated at a pH corresponding to the metal and becomes a suspension. Calcium, a typical hardness component, has a pH of 1
If it is not about 2 to 13, it will not precipitate, but if the pH is raised with slaked lime, it will precipitate as calcium carbonate at about pH 10.8. In this case, some soluble calcium in the water remains, but below the level required for water supply.
【0007】したがつて、析出した物質をほぼ完璧に除
去した後に、再度pHを中性に戻せば、飲料水として必
要な水質レベルまで硬度を下げることができる。さら
に、マンガンや鉄などの溶解性金属もpHを10.8程
度まで上昇させると、大部分が析出するので、透過膜に
より硬度成分と同様に除去できる。水道水とするには、
これを炭酸ガスもしくは酸性薬品でpH調整し、飲料水
として適当な中性付近まで下げればよい。[0007] Therefore, if the pH is returned to neutral again after the precipitated substances are almost completely removed, the hardness can be reduced to the level required for drinking water. Further, when the pH is raised to about 10.8, most of soluble metals such as manganese and iron are also precipitated, and thus can be removed by the permeable membrane in the same manner as the hardness component. To make tap water,
The pH may be adjusted with carbon dioxide or an acidic chemical to lower the pH to around neutral suitable for drinking water.
【0008】[0008]
【実施例】図1はこの考案の第一実施例を示すもので、
この実施例では、原水は原水管1に消石灰溶解液2を注
入ポンプ3でpHを10.8以上になるように適量注入
し、調整槽4で滞留させることにより、原水中の溶解性
カルシウムや溶解性金属を析出させた後、循環槽5及び
循環ポンプ6により、限外ろ過膜7に送水し、この限外
ろ過膜7で析出物質を除去したのち、ろ過水槽8に流出
させる。FIG. 1 shows a first embodiment of the present invention.
In this embodiment, raw water is supplied to a raw water pipe 1 by injecting a suitable amount of slaked lime solution 2 by an injection pump 3 so that the pH becomes 10.8 or more, and keeping it in an adjusting tank 4 to dissolve soluble calcium in raw water. After depositing the soluble metal, water is sent to the ultrafiltration membrane 7 by the circulation tank 5 and the circulation pump 6, and after the precipitated substances are removed by the ultrafiltration membrane 7, the water is discharged to the filtration water tank 8.
【0009】なお前記限外ろ過膜7では、当然のことな
がら原水中の濁質や細菌類も除去する。The ultrafiltration membrane 7 naturally removes turbidity and bacteria in the raw water.
【0010】ろ過水槽8で、処理水に炭酸ガスボンベ9
から流量調節弁10を経由して炭酸ガスを吹き込み、p
Hを中性に戻し、更に次亜塩素酸ナトリウム11を注入
装置12で注入し残留塩素分を持たせ、飲料水とする。In the filtration water tank 8, the treated water is supplied with a carbon dioxide gas cylinder 9
, A carbon dioxide gas is blown through the flow control valve 10 from
The H is returned to neutral, and sodium hypochlorite 11 is further injected by the injection device 12 so as to have a residual chlorine content, thereby obtaining drinking water.
【0011】次に図2に示す第二実施例では、原水管2
1を経由して、消石灰溶解槽22に原水を流入させる。
この消石灰溶解槽22には、消石灰補給槽23から適時
消石灰24が補給されている。Next, in a second embodiment shown in FIG.
Raw water flows into the slaked lime dissolving tank 22 via 1.
The slaked lime dissolving tank 22 is supplied with slaked lime 24 from a slaked lime replenishing tank 23 as needed.
【0012】前記消石灰溶解槽22内を原水が上昇する
ことにより、原水中の溶解性カルシウムや溶解性金属を
析出させた後、循環槽25及び循環ポンプ26により限
外ろ過膜27に送水し、この限外ろ過膜27で析出物質
を除去したのち、ろ過水槽8に流出させる。[0013] The raw water rises in the slaked lime dissolving tank 22 to precipitate soluble calcium and soluble metal in the raw water, and is then sent to the ultrafiltration membrane 27 by the circulation tank 25 and the circulation pump 26. After removing the deposited substance by the ultrafiltration membrane 27, the substance is discharged into the filtration water tank 8.
【0013】限外ろ過膜27では、当然のことながら原
水中の濁質や細菌類も除去する。前記ろ過水槽8で、処
理水に炭酸ガスボンベ9から流量調節弁10を経由して
炭酸ガスを吹き込み、pHを中性に戻し、更に次亜塩素
酸ナトリウム11を注入装置12で注入し、残留塩素分
を持たせ、飲料水とする。The ultrafiltration membrane 27 naturally removes turbidity and bacteria in the raw water. In the filtered water tank 8, carbon dioxide gas is blown into the treated water from the carbon dioxide gas cylinder 9 via the flow control valve 10, the pH is returned to neutral, and sodium hypochlorite 11 is further injected by the injection device 12, and residual chlorine is injected. Allow for drinking water.
【0014】更に図3に示す第三実施例では、原水管3
1を経由して、消石灰充填槽32に原水を流入させる。
この消石灰充填槽32には、微細な消石灰粒子33が充
填されている。Further, in the third embodiment shown in FIG.
Raw water flows into slaked lime filling tank 32 via 1.
The slaked lime filling tank 32 is filled with fine slaked lime particles 33.
【0015】また、前記消石灰充填槽32には、消石灰
補給槽34から適時消石灰粒子が補給されている。前記
消石灰充填槽32内を原水が上昇することにより、原水
中の溶解性カルシウムや溶解性金属を析出させた後、循
環槽35及び循環ポンプ36により限外ろ過膜37に送
水し、この限外ろ過膜37で析出物質を除去したのち、
ろ過水槽38に流出する。The slaked lime filling tank 32 is replenished with slaked lime particles from a slaked lime replenishing tank 34 as needed. After the raw water rises in the slaked lime filling tank 32 to precipitate soluble calcium and soluble metal in the raw water, the water is sent to the ultrafiltration membrane 37 by the circulation tank 35 and the circulation pump 36, After removing the deposited substance by the filtration membrane 37,
It flows out to the filtration water tank 38.
【0016】限外ろ過膜37では、当然のことながら原
水中の濁質や細菌類も除去する。ろ過水槽38で、処理
水に炭酸ガスボンベ39から流量調節弁40を経由して
炭酸ガスを吹き込み、pHを中性に戻し、更に次亜塩素
酸ナトリウム41を注入装置42で注入し、残留塩素分
を持たせ、飲料水とする。The ultrafiltration membrane 37 naturally also removes turbidity and bacteria in raw water. In the filtered water tank 38, carbon dioxide gas is blown into the treated water from the carbon dioxide gas cylinder 39 via the flow rate control valve 40 to return the pH to neutral, and sodium hypochlorite 41 is further injected by the injection device 42 to remove residual chlorine. And make it drinking water.
【0017】[0017]
【考案の効果】この考案の上述の構造の装置によれば、
原水中に含まれる硬度成分や溶解性金属を高能率で除去
することができるので水質基準に適合した水処理を行な
うに当つて極めて有用なものである。According to the device having the above structure according to the present invention,
It is very useful for performing water treatment conforming to the water quality standard, because it can remove the hardness component and soluble metal contained in the raw water with high efficiency.
【図1】この考案の第一実施例の構成図である。FIG. 1 is a configuration diagram of a first embodiment of the present invention.
【図2】この考案の第二実施例の構成図である。FIG. 2 is a configuration diagram of a second embodiment of the present invention.
【図3】この考案の第三実施例の構成図である。FIG. 3 is a configuration diagram of a third embodiment of the present invention.
1,21,31 原水管 6,26,36 循環ポンプ 7,27,37 限外ろ過膜 8,38 ろ過水槽 11,41 次亜塩素酸ナトリウム 1,21,31 Raw water pipe 6,26,36 Circulation pump 7,27,37 Ultrafiltration membrane 8,38 Filtration water tank 11,41 Sodium hypochlorite
フロントページの続き (56)参考文献 特開 昭57−4204(JP,A) 特開 昭62−121694(JP,A) 特開 昭61−220793(JP,A) 特開 昭63−28486(JP,A) 特開 平2−157090(JP,A) 実開 昭62−43696(JP,U) 特公 昭35−3832(JP,B1) (58)調査した分野(Int.Cl.7,DB名) C02F 1/44 B01D 61/16 C02F 1/58 C02F 1/64 Continuation of the front page (56) References JP-A-57-4204 (JP, A) JP-A-62-121694 (JP, A) JP-A-61-220793 (JP, A) JP-A-63-28486 (JP) JP-A-2-157090 (JP, A) JP-A-64-243696 (JP, U) JP-B-35-3833 (JP, B1) (58) Fields investigated (Int. Cl. 7 , DB Name) C02F 1/44 B01D 61/16 C02F 1/58 C02F 1/64
Claims (2)
水に消石灰、カセイソーダもしくはソーダ灰等のアルカ
リ剤を注入し、原水のpHを上昇させることにより、原
水中の硬度成分及び溶解性金属を析出させ、これを限外
ろ過膜もしくは精密ろ過膜で透過し、透過水を炭酸ガス
もしくは酸性薬品で再度pHを中性付近まで中和させる
ことを特徴とする、上水道における透過膜による硬度成
分及び溶解性金属除去装置。An alkaline agent such as slaked lime, caustic soda or soda ash is injected into raw water containing a hardness component and a soluble metal component to raise the pH of the raw water, thereby reducing the hardness component and the soluble metal in the raw water. precipitate, which was transmitted through the ultrafiltration membrane or microfiltration membrane, the permeate, characterized in that to neutralize the re pH with carbon dioxide gas or acid chemicals to near neutrality, and hardness components by permeation membrane in water supply Dissolvable metal removal equipment.
水を、石灰系粒子を充填した水槽もしくは消石灰を溶解
した水槽を通過させ、原水のpHを上昇させることによ
り、原水中の硬度成分及び溶解性金属を析出させ、これ
を限外ろ過膜もしくは精密ろ過膜で透過し、透過水を炭
酸ガスもしくは酸性薬品で再度pHを中性付近まで中和
させることを特徴とする、上水道における透過膜による
硬度成分及び溶解性金属除去装置。2. The raw water containing the hardness component and the soluble metal component is passed through a water tank filled with lime-based particles or a water tank in which slaked lime is dissolved, and the pH of the raw water is raised, whereby the hardness component in the raw water and A permeable membrane for water supply, characterized by precipitating a soluble metal, permeating it through an ultrafiltration membrane or a microfiltration membrane, and neutralizing the permeated water again to near neutrality with carbon dioxide or an acidic chemical. Device for removing hardness components and soluble metals.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1993021170U JP2607543Y2 (en) | 1993-04-01 | 1993-04-01 | Hardness component and soluble metal removal device with permeable membrane |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1993021170U JP2607543Y2 (en) | 1993-04-01 | 1993-04-01 | Hardness component and soluble metal removal device with permeable membrane |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0672691U JPH0672691U (en) | 1994-10-11 |
JP2607543Y2 true JP2607543Y2 (en) | 2001-11-12 |
Family
ID=12047454
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP1993021170U Expired - Fee Related JP2607543Y2 (en) | 1993-04-01 | 1993-04-01 | Hardness component and soluble metal removal device with permeable membrane |
Country Status (1)
Country | Link |
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JP (1) | JP2607543Y2 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006016267A (en) * | 2004-07-02 | 2006-01-19 | Asahi Kasei Chemicals Corp | Removal of organic material contained in salt water by means of filtration |
-
1993
- 1993-04-01 JP JP1993021170U patent/JP2607543Y2/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
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JPH0672691U (en) | 1994-10-11 |
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LAPS | Cancellation because of no payment of annual fees |