Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP3473472B2 - Treatment method for fluorine-containing water - Google Patents
[go: Go Back, main page]

JP3473472B2 - Treatment method for fluorine-containing water - Google Patents

Treatment method for fluorine-containing water

Info

Publication number
JP3473472B2
JP3473472B2 JP02895499A JP2895499A JP3473472B2 JP 3473472 B2 JP3473472 B2 JP 3473472B2 JP 02895499 A JP02895499 A JP 02895499A JP 2895499 A JP2895499 A JP 2895499A JP 3473472 B2 JP3473472 B2 JP 3473472B2
Authority
JP
Japan
Prior art keywords
water
fluorine
electric desalination
concentration
desalination apparatus
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
Application number
JP02895499A
Other languages
Japanese (ja)
Other versions
JP2000229289A (en
Inventor
伸 佐藤
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP02895499A priority Critical patent/JP3473472B2/en
Publication of JP2000229289A publication Critical patent/JP2000229289A/en
Application granted granted Critical
Publication of JP3473472B2 publication Critical patent/JP3473472B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)
  • Treatment Of Water By Ion Exchange (AREA)
  • Removal Of Specific Substances (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

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】本発明はフッ素含有水を電気
脱塩装置で処理する方法に係り、特に、電子産業分野等
の純水製造装置において、フッ素イオンを含む回収水を
混合した原水を電気脱塩装置で処理するに当り、電気脱
塩装置の濃縮室におけるフッ化カルシウム(CaF2
スケールの生成を防止して長期に亘り安定に処理を行う
方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating fluorine-containing water with an electric desalination apparatus, and in particular, in a pure water producing apparatus in the field of electronics industry, raw water mixed with recovered water containing fluorine ions Calcium fluoride (CaF 2 ) in the concentrating chamber of the electric desalination equipment when processing with the desalination equipment
The present invention relates to a method of preventing scale formation and performing stable treatment over a long period of time.

【0002】[0002]

【従来の技術】従来、半導体、レンズ、液晶等の洗浄用
水、医薬用水等に用いられる脱塩水の製造には、電極の
間に複数のアニオン交換膜及びカチオン交換膜を交互に
配列して濃縮室と脱塩室とを交互に形成した電気脱塩装
置が多用されている。電気脱塩装置は効率的な脱塩処理
が可能であり、イオン交換樹脂のような再生を必要とせ
ず、完全な連続採水が可能で、極めて高純度の水が得ら
れるという優れた効果を奏する。なお、電気脱塩装置に
は、脱塩室にアニオン交換樹脂とカチオン交換樹脂とが
混合して充填されているものと、脱塩室にイオン交換樹
脂が充填されていないものとがあるが、処理水の水質向
上の点では、脱塩室にイオン交換樹脂が充填されたもの
の方が効果的である。
2. Description of the Related Art Conventionally, in the production of demineralized water used for washing water for semiconductors, lenses, liquid crystals, etc., medical water, etc., a plurality of anion exchange membranes and cation exchange membranes are alternately arranged between electrodes and concentrated. An electric desalination apparatus in which chambers and desalting chambers are alternately formed is often used. The electric desalination equipment is capable of efficient desalination treatment, does not require regeneration like ion exchange resin, allows complete continuous water sampling, and has the excellent effect of obtaining extremely high-purity water. Play. In the electric desalination apparatus, there are a desalting chamber filled with a mixture of anion exchange resin and a cation exchange resin, and a desalting chamber not filled with an ion exchange resin. In terms of improving the quality of treated water, it is more effective to use a desalting chamber filled with an ion exchange resin.

【0003】電気脱塩装置では、脱塩室に流入した原水
中のイオンが親和力、濃度及び移動度に基いて電位をか
けた電極の方向(被処理水の流れに対して直角方向)に
移動し、更に、脱塩室と濃縮室とを仕切るカチオン交換
膜又はアニオン交換膜を横切って移動し、すべての室に
おいて電荷の中和が保たれるようになる。そして、イオ
ン交換膜の半浸透特性及び電位により、原水のイオンは
脱塩室では減少し、隣りの濃縮室では濃縮されることに
なる。このため、脱塩室から脱塩水が回収される。
In the electric desalination apparatus, the ions in the raw water flowing into the desalination chamber move in the direction of the electrode (a direction perpendicular to the flow of the water to be treated) to which an electric potential is applied based on the affinity, the concentration and the mobility. In addition, it moves across the cation exchange membrane or the anion exchange membrane that separates the desalting chamber and the concentration chamber, and the charge neutralization is maintained in all the chambers. Then, due to the semi-permeation property and potential of the ion exchange membrane, the ions of the raw water are reduced in the desalting chamber and concentrated in the adjacent concentration chamber. Therefore, demineralized water is recovered from the desalination chamber.

【0004】このような電気脱塩装置におけるスケール
発生の要因として、硬度成分があることは知られてい
る。しかし、一般的に、電気脱塩装置の原水としては、
水道水、工水等が供給されるため、電気脱塩装置に流入
する供給水にフッ素イオンが含まれていることは殆どな
く、このため、従来においては電気脱塩装置でCaF2
のスケールが問題になることはなかった。
It is known that there is a hardness component as a factor of scale generation in such an electric desalination apparatus. However, in general, as raw water for an electric desalination device,
Since tap water, industrial water, etc. are supplied, the supplied water that flows into the electric desalination apparatus rarely contains fluoride ions. Therefore, in the conventional case, the electric desalination apparatus used CaF 2
The scale of was never a problem.

【0005】[0005]

【発明が解決しようとする課題】しかし、近年、電子産
業分野等の純水製造装置への電気脱塩装置の適用が進む
一方で、水の有効利用を目的として、工場の回収水を原
水に混合して処理するケースが多くなってきている。こ
のようなケースでは、回収水中に含まれるフッ素イオン
が電気脱塩装置で濃縮される際に、CaF2のスケール
を生成し、スケール障害を引き起こす。
However, in recent years, while the application of an electric desalination apparatus to a pure water producing apparatus in the field of electronics industry has been progressing, the recovered water of a factory is used as raw water for the purpose of effective use of water. There are many cases of mixing and processing. In such a case, when the fluoride ions contained in the recovered water are concentrated by the electric desalting apparatus, CaF 2 scale is generated, which causes scale failure.

【0006】本発明は上記従来の問題点を解決し、フッ
素含有水を電気脱塩装置で処理するに当り、電気脱塩装
置の濃縮室におけるCaF2スケールの生成を防止して
長期に亘り安定な処理を行うことができるフッ素含有水
の処理方法を提供することを目的とする。
The present invention solves the above-mentioned conventional problems and prevents the formation of CaF 2 scale in the concentrating chamber of the electric desalination apparatus when treating the fluorine-containing water with the electric desalination apparatus, and stabilizes it for a long time. An object of the present invention is to provide a method for treating fluorine-containing water that can perform various treatments.

【0007】[0007]

【課題を解決するための手段】本発明のフッ素含有水の
処理方法は、フッ素含有水を電気脱塩装置に供給して処
理する方法において、電気脱塩装置に供給される水のカ
ルシウム濃度[Ca](mg/L)及びフッ素濃度
[F](mg/L)と電気脱塩装置の水回収率(生産水
量/供給水量)[R]の関係が、下記式を満たすよう
、水回収率を小さくする、供給水のカルシウムイオン
濃度を低減する、供給水のフッ素イオン濃度を低減す
る、のいずれか少なくとも一つの処理を行うとともに水
回収率[R]を0.8以上に維持することを特徴とす
る。
A method for treating fluorine-containing water according to the present invention is a method for treating fluorine-containing water by supplying it to an electric desalination apparatus. Water recovery such that the relationship between Ca] (mg / L) and fluorine concentration [F] (mg / L) and the water recovery rate (production water amount / supply water amount) [R] of the electric desalination device satisfies the following formula: Calcium ion in feed water that reduces the rate
Reduce the concentration, reduce the fluorine ion concentration of the feed water
, At least one of which is treated with water
The recovery rate [R] is maintained at 0.8 or more .

【0008】 [Ca]×[F]2/{1−[R]}<50 即ち、本発明者は、フッ素イオンを含む供給水を電気脱
塩装置において処理する様々なケースについて、CaF
2スケール障害の有無と供給水の条件及び運転条件を比
較検討した結果、これらに一定の関連性があり、上記式
を満たすように処理を行った場合には、CaF2のスケ
ール障害を防止できることを見出し、本発明を完成させ
た。
[Ca] × [F] 2 / {1- [R]} <50 That is, the present inventor has investigated CaF in various cases in which feed water containing fluoride ions is treated in an electric desalination apparatus.
2 As a result of a comparative examination of the presence or absence of scale disturbance and the conditions of supply water and operating conditions, these have a certain relationship, and if treatment is performed so as to satisfy the above formula, scale failure of CaF 2 can be prevented. Then, the present invention has been completed.

【0009】なお、供給水条件が上記式を満たし難い場
合、上記式を満足するための手段としては、水回収率
[R]を小さくすることが最も簡単な手段であるが、こ
の場合には、生産水量が少なく、濃縮水の量が多くなり
生産性が低下するため、水の有効利用の面で望ましくな
い。
When it is difficult to satisfy the above equation under the condition of water supply, the simplest means to satisfy the above equation is to reduce the water recovery rate [R]. In this case, However, since the amount of produced water is small and the amount of concentrated water is large and the productivity is reduced, it is not desirable in terms of effective use of water.

【0010】従って、この場合には、フッ素含有水をイ
オン交換樹脂で処理して、スケール成分のフッ素イオン
又はカルシウムイオンを予め除去し、[R]を小さくす
ることなく上記式を満たすようにすることが好ましい。
Therefore, in this case, the fluorine-containing water is treated with an ion exchange resin to previously remove the fluorine ion or calcium ion of the scale component so as to satisfy the above formula without reducing [R]. It is preferable.

【0011】[0011]

【発明の実施の形態】以下に本発明の実施の形態を詳細
に説明する。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described in detail below.

【0012】本発明の方法は、フッ素含有水を電気脱塩
装置で処理するに当り、電気脱塩装置の供給水のカルシ
ウム濃度(mg/L)を[Ca]とし、及びフッ素濃度
(mg/L)を[F]とし、電気脱塩装置の水回収率
(生産水量/供給水量)を[R]としたときに、これら
の関係が、下記式を満たすように、水回収率を小さくす
る、供給水のカルシウムイオン濃度を低減する、供給水
のフッ素イオン濃度を低減する、のいずれか少なくとも
一つの処理を行うとともに水回収率[R]を0.8以上
に維持するものである。
According to the method of the present invention, in treating fluorine-containing water with an electric desalination apparatus, the calcium concentration (mg / L) of the water supplied to the electric desalination apparatus is set to [Ca], and the fluorine concentration (mg / L) When L) is [F] and the water recovery rate (production water amount / supply water amount) of the electric desalination apparatus is [R] , the water recovery rate is made small so that these relationships satisfy the following formula .
Supply water that reduces the calcium ion concentration of the supply water
Reduce the fluorine ion concentration of at least one of
Water recovery rate [R] is 0.8 or more with one treatment
To maintain .

【0013】 [Ca]×[F]2/{1−[R]}<50 上記関係式の[Ca]×[F]2/{1−[R]}の値
が50以上であると、電気脱塩装置の濃縮室においてC
aF2スケールが生成し、スケール障害が発生する。こ
の値は、特に40以下、とりわけ30以下となるよう
に、供給水の条件や運転条件を調整するのが好ましい。
[Ca] × [F] 2 / {1- [R]} <50 When the value of [Ca] × [F] 2 / {1- [R]} in the above relational expression is 50 or more, C in the concentration chamber of the electric desalination equipment
The aF 2 scale is generated and scale failure occurs. It is preferable to adjust the conditions of the supply water and the operating conditions so that this value is 40 or less, particularly 30 or less.

【0014】上記の関係式を満たすためには、電気脱塩
装置の水回収率(供給水量に対する生産水量の比)
[R]を小さくすることが最も容易な方法であるが、水
回収率[R]を過度に小さくすることは、前述の如く、
生産性の面で好ましくない。従って、本発明では、好ま
しくは下記の(1)又は(2)の方法を採用して供給水
のフッ素イオン濃度又はカルシウムイオン濃度を低減
し、水回収率[R]を0.8以上、好ましくは0.9〜
0.95に維持した上で上記関係式を満たすようにす
る。
In order to satisfy the above relational expression, the water recovery rate of the electric desalination device (ratio of the amount of produced water to the amount of supplied water)
Although it is the easiest method to reduce [R], it is necessary to reduce the water recovery rate [R] excessively as described above.
It is not preferable in terms of productivity. Accordingly, in the present invention, preferred
Specifically, the following method (1) or (2) is adopted to reduce the fluorine ion concentration or calcium ion concentration of the feed water, and the water recovery rate [R] is 0.8 or more, preferably 0.9 to
Keep the above relational expression while maintaining 0.95
It

【0015】(1)供給水中のフッ素イオン濃度を低減
させるために、アニオン交換樹脂を充填した非再生式イ
オン交換装置で前処理する。ただし、アニオン交換樹脂
によるフッ素イオンの除去では、定期的な樹脂の入れ替
えが必要となる。このような定期的なメンテナンスを少
なくするためには、アニオン交換樹脂として弱塩基性の
アニオン交換樹脂を用いることが望ましい。弱塩基性ア
ニオン交換樹脂は強塩基性アニオン交換樹脂よりも若干
イオン交換性能が不足するが、半導体工場等の回収水中
に含まれるフッ素イオンはHFの形態が主体であり、中
性塩(NaF等)は少ないので、弱塩基性のアニオン交
換樹脂でも十分に除去できる。
(1) In order to reduce the concentration of fluorine ions in the feed water, pretreatment is performed with a non-regeneration type ion exchange device filled with an anion exchange resin. However, the removal of fluorine ions by the anion exchange resin requires periodic replacement of the resin. In order to reduce such regular maintenance, it is desirable to use a weakly basic anion exchange resin as the anion exchange resin. Weakly basic anion exchange resins are slightly inferior in ion exchange performance to strongly basic anion exchange resins, but the fluorine ions contained in the recovered water of semiconductor factories are mainly in the form of HF, and neutral salts (such as NaF) are used. ) Is small, it is possible to sufficiently remove even a weakly basic anion exchange resin.

【0016】この場合、弱塩基性アニオン交換樹脂は、
単独で用いても良いが、原水のF形態によっては、強塩
基性アニオン交換樹脂と混合して用いても良い。
In this case, the weakly basic anion exchange resin is
Although it may be used alone, it may be used as a mixture with a strongly basic anion exchange resin depending on the F form of the raw water.

【0017】(2)供給水中のカルシウムイオン濃度を
低減させるために、カチオン交換樹脂を充填した非再生
式イオン交換装置で前処理する。この場合においても、
カチオン交換樹脂によるカルシウムイオンの除去で、定
期的な樹脂の入れ替えが必要となることから、このよう
な定期的なメンテナンスを少なくするために、カチオン
交換樹脂として弱酸性のカチオン交換樹脂を用いること
が望ましい。弱酸性カチオン交換樹脂は、強酸性カチオ
ン交換樹脂よりも若干イオン交換性能が不足するが、供
給水中に含まれるカルシウムイオンはCa(HCO
の形態が主体であり、中性塩(CaCl等)は少ない
ので、弱酸性のカチオン交換樹脂も十分に除去できる。
(2) In order to reduce the calcium ion concentration in the feed water, pretreatment is performed with a non-regeneration type ion exchange device filled with a cation exchange resin. Even in this case,
Since removal of calcium ions by cation exchange resin requires periodic replacement of the resin, it is necessary to use a weakly acidic cation exchange resin as the cation exchange resin in order to reduce such regular maintenance. desirable. The weakly acidic cation exchange resin is slightly inferior in ion exchange performance to the strongly acidic cation exchange resin, but the calcium ions contained in the feed water are Ca (HCO 3 )
Since the form 2 is mainly used and the amount of neutral salts (CaCl etc.) is small, the weakly acidic cation exchange resin can be sufficiently removed.

【0018】この場合、弱酸性カチオン交換樹脂は、単
独で用いても良いが、原水のCa形態によっては、強酸
性カチオン交換樹脂と混合して用いても良い。
In this case, the weakly acidic cation exchange resin may be used alone, or may be mixed with the strongly acidic cation exchange resin depending on the Ca form of the raw water.

【0019】上記(1)(2)を共に採用することも
可能であるが、本発明では前記関係式を満たしていれば
よく、一般的には、(1)(2)のいずれか一方を採
用するのみで十分であり、設備の簡略化の面からも、
(1)(2)のいずれか一方を採用するのが経済的で
有利である。
Although it is possible to adopt both of the above (1) and (2) , it is sufficient in the present invention that the above relational expression is satisfied, and in general, either (1) or (2) is used. It is enough to adopt only one, and from the aspect of facility simplification,
It is economical and advantageous to adopt either one of (1) and (2) .

【0020】なお、フッ素イオン濃度又はカルシウムイ
オン濃度の低減のための手段は上記(1)(2)に何
ら制限されず、逆浸透(RO)膜分離装置や薬品再生型
イオン交換樹脂塔などを採用しても良い。一般に、電気
脱塩装置の前処理手段としてRO膜分離装置が設けられ
ていることから、このような場合においてRO膜分離装
置でフッ素イオン濃度又はカルシウムイオン濃度を低減
するためには、2機以上のRO膜分離装置を直列に配置
して多段RO処理を行うことになる。ただし、設備や運
転の簡便性の面からは、上記(1)又は(2)の手段を
採用するのが有利である。
The means for reducing the fluorine ion concentration or the calcium ion concentration is not limited to the above (1) and (2) , and a reverse osmosis (RO) membrane separation device, a chemical regeneration type ion exchange resin tower, etc. May be adopted. Generally, since an RO membrane separator is provided as a pretreatment means for the electric desalination apparatus, in such a case, in order to reduce the fluorine ion concentration or the calcium ion concentration in the RO membrane separator, two or more machines are used. The RO membrane separators of 1 are arranged in series to perform multi-stage RO treatment. However, it is advantageous to adopt the above-mentioned means (1) or (2) from the viewpoint of facility and ease of operation.

【0021】本発明において用いる電気脱塩装置は、複
数のアニオン交換膜及びカチオン交換膜を交互に配列し
て濃縮室と脱塩室とを交互に形成した一般的なものであ
り、脱塩室にアニオン交換樹脂とカチオン交換樹脂との
混合樹脂が充填されたものであっても、充填されていな
いものであっても良いが、処理水(生産水)の水質の向
上の面からは、脱塩室にアニオン交換樹脂とカチオン交
換樹脂の混合樹脂が充填されているものが好ましい。
The electric desalination apparatus used in the present invention is a general one in which a plurality of anion exchange membranes and cation exchange membranes are alternately arranged to alternately form a concentration chamber and a desalination chamber. May be filled with a mixed resin of an anion exchange resin and a cation exchange resin, or may not be filled with it, but from the viewpoint of improving the quality of treated water (production water), It is preferable that the salt chamber is filled with a mixed resin of an anion exchange resin and a cation exchange resin.

【0022】このような本発明のフッ素含有水の処理方
法は、電子産業分野等の純水製造装置における、フッ素
イオンを含む回収水を混合した原水の処理に極めて有効
である。
The method for treating fluorine-containing water of the present invention as described above is extremely effective for treating raw water mixed with recovered water containing fluorine ions in a pure water producing apparatus in the field of electronics industry and the like.

【0023】[0023]

【実施例】以下に実施例及び比較例を挙げて本発明をよ
り具体的に説明する。
EXAMPLES The present invention will be described more specifically with reference to Examples and Comparative Examples below.

【0024】なお、実施例及び比較例で用いた電気脱塩
装置は、(栗田工業(株)製「ピュアエース」)(処理
水量1000L/hr)であり、この電気脱塩装置は、
脱塩室に強塩基性アニオン交換樹脂と強酸性カチオン交
換樹脂とが35:65(容量比)で充填されたものであ
る。
The electric desalination apparatus used in the examples and comparative examples is (Pure Ace manufactured by Kurita Water Industries Ltd.) (treated water amount 1000 L / hr).
A strongly basic anion-exchange resins in the desalting compartment and a strongly acidic cation exchange resins are those filled with 35:65 (volume ratio).

【0025】実施例1 半導体工場の回収水と市水とを混合した原水を、図1に
示すフローに従って、活性炭塔1、RO膜分離装置2で
順次処理し、次いで弱塩基性アニオン交換樹脂を充填し
た非再生式アニオン交換装置3で処理した後電気脱塩装
置4の供給水として水回収率[R]=0.95で処理し
た。
Example 1 Raw water obtained by mixing recovered water of a semiconductor factory and city water was sequentially treated with an activated carbon tower 1 and an RO membrane separator 2 according to the flow shown in FIG. After the treatment with the filled non-regeneration type anion exchange device 3, it was treated with the water recovery rate [R] = 0.95 as the feed water of the electric desalination device 4.

【0026】このとき電気脱塩装置4の供給水のCa濃
度は0.3mg/L、F濃度は0.1mg/L以下で、
[Ca]×[F]2/{1−[R]}=0.3×(0.
1)2/(1−0.95)=0.06であった。
At this time, the Ca concentration of the feed water of the electric desalination apparatus 4 is 0.3 mg / L, the F concentration is 0.1 mg / L or less,
[Ca] × [F] 2 /{1-[R]}=0.3×(0.
1) 2 /(1-0.95)=0.06.

【0027】電気脱塩装置4を3ヶ月間連続運転した
後、電気脱塩装置4を解体して濃縮室におけるCaF2
スケールの有無を調べたところ、CaF2スケールは全
く生成していなかった。
After the electric desalination apparatus 4 was continuously operated for 3 months, the electric desalination apparatus 4 was disassembled to remove CaF 2 in the concentration chamber.
When the presence or absence of scale was examined, no CaF 2 scale was formed.

【0028】実施例2 半導体工場の回収水と市水とを混合した原水を、図2に
示すフローに従って、活性炭塔1、RO膜分離装置2で
順次処理し、次いで弱酸性カチオン交換樹脂を充填した
非再生式カチオン交換装置5で処理した後電気脱塩装置
4の供給水として水回収率[R]=0.95で処理し
た。
Example 2 Raw water obtained by mixing recovered water of a semiconductor factory and city water was sequentially treated with an activated carbon tower 1 and an RO membrane separation device 2 according to the flow shown in FIG. The treated water was treated with the non-regeneration type cation exchange device 5 and treated with water recovery rate [R] = 0.95 as the feed water of the electric desalination device 4.

【0029】このとき電気脱塩装置4の供給水のCa濃
度は0.1mg/L以下、F濃度は3mg/Lで、[C
a]×[F]2/{1−[R]}=0.1×(3)2
(1−0.95)=18であった。
At this time, the Ca concentration of the feed water of the electric desalination apparatus 4 is 0.1 mg / L or less, the F concentration is 3 mg / L, and [C
a] × [F] 2 /{1-[R]}=0.1×(3) 2 /
(1-0.95) = 18.

【0030】電気脱塩装置4を3ヶ月間連続運転した
後、電気脱塩装置4を解体して濃縮室におけるCaF2
スケールの有無を調べたところ、CaF2スケールは全
く生成していなかった。
After the electric desalination apparatus 4 was continuously operated for 3 months, the electric desalination apparatus 4 was disassembled and CaF 2 in the concentration chamber was removed.
When the presence or absence of scale was examined, no CaF 2 scale was formed.

【0031】比較例1 半導体工場の回収水と市水とを混合した原水を、図3に
示すフローに従って、活性炭塔1、RO膜分離装置2で
順次処理した後電気脱塩装置4の供給水として水回収率
[R]=0.95で処理した。
Comparative Example 1 Raw water obtained by mixing recovered water of a semiconductor factory and city water was sequentially treated with an activated carbon tower 1 and an RO membrane separator 2 according to the flow shown in FIG. Was treated with a water recovery rate [R] = 0.95.

【0032】このとき電気脱塩装置4の供給水のCa濃
度は0.3mg/L、F濃度は3mg/Lで、[Ca]
×[F]2/{1−[R]}=0.3×(3)2/(1−
0.95)=54であった。
At this time, the Ca concentration of the feed water of the electric desalination apparatus 4 was 0.3 mg / L, the F concentration was 3 mg / L, and [Ca]
× [F] 2 /{1-[R]}=0.3×(3) 2 / (1-
0.95) = 54.

【0033】電気脱塩装置4を3ヶ月間連続運転した
後、電気脱塩装置4を解体して濃縮室におけるCaF2
スケールの有無を調べたところ、CaF2スケールの生
成が認められた。
After the electric desalination apparatus 4 was continuously operated for 3 months, the electric desalination apparatus 4 was disassembled and CaF 2 in the concentration chamber was removed.
When the presence or absence of scale was examined, formation of CaF 2 scale was confirmed.

【0034】比較例2 実施例2において、電気脱塩装置4の水回収率[R]を
上げて0.99としたこと以外は同様にして処理を行っ
た。このときの運転条件は[Ca]×[F]2/{1−
[R]}=0.1×(3)2/(1−0.99)=90
であった。
Comparative Example 2 The same treatment as in Example 2 was carried out except that the water recovery rate [R] of the electric desalination apparatus 4 was increased to 0.99. The operating condition at this time is [Ca] × [F] 2 / {1-
[R]} = 0.1 × (3) 2 /(1-0.99)=90
Met.

【0035】電気脱塩装置4を3ヶ月間連続運転した
後、電気脱塩装置4を解体して濃縮室におけるCaF2
スケールの有無を調べたところ、CaF2スケールの生
成が認められた。
After the electric desalination apparatus 4 was continuously operated for 3 months, the electric desalination apparatus 4 was disassembled to remove CaF 2 in the concentration chamber.
When the presence or absence of scale was examined, formation of CaF 2 scale was confirmed.

【0036】実施例3 比較例1において、電気脱塩装置4の水回収率[R]を
下げて0.90としたこと以外は同様にして処理を行っ
た。このときの運転条件は[Ca]×[F]2/{1−
[R]}=0.3×(3)2/(1−0.90)=27
であった。
Example 3 The same treatment as in Comparative Example 1 was carried out except that the water recovery rate [R] of the electric desalination apparatus 4 was lowered to 0.90. The operating condition at this time is [Ca] × [F] 2 / {1-
[R]} = 0.3 × (3) 2 /(1−0.90)=27
Met.

【0037】電気脱塩装置4を3ヶ月間連続運転した
後、電気脱塩装置4を解体して濃縮室におけるCaF2
スケールの有無を調べたところ、CaF2スケールは全
く生成していなかった。
After the electric desalination apparatus 4 was continuously operated for 3 months, the electric desalination apparatus 4 was disassembled and CaF 2 in the concentration chamber was removed.
When the presence or absence of scale was examined, no CaF 2 scale was formed.

【0038】なお、上記実施例1〜3及び比較例1,2
のいずれにおいても得られた処理水(生産水)の比抵抗
は16〜18MΩ・cmであり、処理水の水質には差異
はなかった。
The above Examples 1 to 3 and Comparative Examples 1 and 2
In all cases, the specific resistance of the treated water (produced water) obtained was 16 to 18 MΩ · cm, and there was no difference in the water quality of the treated water.

【0039】[0039]

【発明の効果】以上詳述した通り、本発明のフッ素含有
水の処理方法によれば、電子産業分野等の純水製造装置
等において、フッ素イオンを含む回収水を混合した原水
のようなフッ素含有水を電気脱塩装置で処理するに当
り、電気脱塩装置の濃縮室におけるフッ化カルシウムス
ケールの生成を防止して長期に亘り安定に処理を行うこ
とができる。
As described above in detail, according to the method for treating fluorine-containing water of the present invention, in a pure water production apparatus in the field of electronics, etc., fluorine such as raw water mixed with recovered water containing fluorine ions is mixed. When the contained water is treated with the electric desalination apparatus, it is possible to prevent the generation of calcium fluoride scale in the concentration chamber of the electric desalination apparatus and perform the treatment stably for a long period of time.

【0040】請求項2の方法によれば、脱塩水の生産性
を落とすことなく、フッ化カルシウムのスケール障害を
有効に防止することができる。
According to the method of claim 2, it is possible to effectively prevent the scale failure of calcium fluoride without lowering the productivity of demineralized water.

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

【図1】実施例1における処理方法を示す系統図であ
る。
FIG. 1 is a system diagram showing a processing method according to a first embodiment.

【図2】実施例2における処理方法を示す系統図であ
る。
FIG. 2 is a system diagram showing a processing method according to a second embodiment.

【図3】比較例1における処理方法を示す系統図であ
る。
FIG. 3 is a system diagram showing a processing method in Comparative Example 1.

【符号の説明】[Explanation of symbols]

1 活性炭塔 2 RO膜分離装置 3 非再生式アニオン交換装置 4 電気脱塩装置 5 非再生式カチオン交換装置 1 activated carbon tower 2 RO membrane separator 3 Non-regenerative anion exchanger 4 Electric desalination equipment 5 Non-regenerative cation exchanger

フロントページの続き (56)参考文献 特開2000−176457(JP,A) 特開 平9−262588(JP,A) 特開 平9−10557(JP,A) 特開 平7−171574(JP,A) 特開 平7−265864(JP,A) 特開 平7−214068(JP,A) 特開 平7−195071(JP,A) 特開 平1−130783(JP,A) 特開 昭52−8987(JP,A) 特開 平1−130782(JP,A) (58)調査した分野(Int.Cl.7,DB名) C02F 1/46 B01D 61/44 C02F 1/42 C02F 1/58 Continuation of the front page (56) References JP 2000-176457 (JP, A) JP 9-262588 (JP, A) JP 9-10557 (JP, A) JP 7-171574 (JP, A) JP 7-265864 (JP, A) JP 7-214068 (JP, A) JP 7-195071 (JP, A) JP 1-130783 (JP, A) JP 52 -8987 (JP, A) JP-A-1-130782 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) C02F 1/46 B01D 61/44 C02F 1/42 C02F 1/58

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 フッ素含有水を電気脱塩装置に供給して
処理する方法において、電気脱塩装置に供給される水の
カルシウム濃度[Ca](mg/L)及びフッ素濃度
[F](mg/L)と電気脱塩装置の水回収率(生産水
量/供給水量)[R]の関係が、下記式を満たすよう
、水回収率を小さくする、供給水のカルシウムイオン
濃度を低減する、供給水のフッ素イオン濃度を低減す
る、のいずれか少なくとも一つの処理を行うとともに水
回収率[R]を0.8以上に維持することを特徴とする
フッ素含有水の処理方法。 [Ca]×[F]/{1−[R]}<50
1. A method of supplying fluorine-containing water to an electric desalination apparatus for treatment, wherein the water supplied to the electric desalination apparatus has a calcium concentration [Ca] (mg / L) and a fluorine concentration [F] (mg). / L) and the water recovery rate (production water amount / supply water amount) [R] of the electric desalination device , the water recovery ratio is made small so that the following formula is satisfied.
Reduce the concentration, reduce the fluorine ion concentration of the feed water
, At least one of which is treated with water
A method for treating fluorine-containing water, characterized in that the recovery rate [R] is maintained at 0.8 or more . [Ca] × [F] 2 / {1- [R]} <50
【請求項2】 請求項1において、フッ素含有水をイオ
ン交換樹脂で予めカルシウムイオン又はフッ素イオンを
除去した後、電気脱塩装置に供給することを特徴とする
フッ素含有水の処理方法。
2. The method according to claim 1, wherein the fluorine-containing water is preliminarily charged with calcium ions or fluorine ions with an ion exchange resin.
A method for treating fluorine-containing water, characterized in that the water is supplied to an electric desalination apparatus after being removed .
JP02895499A 1999-02-05 1999-02-05 Treatment method for fluorine-containing water Expired - Fee Related JP3473472B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP02895499A JP3473472B2 (en) 1999-02-05 1999-02-05 Treatment method for fluorine-containing water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP02895499A JP3473472B2 (en) 1999-02-05 1999-02-05 Treatment method for fluorine-containing water

Publications (2)

Publication Number Publication Date
JP2000229289A JP2000229289A (en) 2000-08-22
JP3473472B2 true JP3473472B2 (en) 2003-12-02

Family

ID=12262822

Family Applications (1)

Application Number Title Priority Date Filing Date
JP02895499A Expired - Fee Related JP3473472B2 (en) 1999-02-05 1999-02-05 Treatment method for fluorine-containing water

Country Status (1)

Country Link
JP (1) JP3473472B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2570467C2 (en) * 2014-04-16 2015-12-10 Федеральное государственное бюджетное образовательное учреждение высшего профессионального образования "Башкирский государственный университет" Method of purifying waste water from fluorine

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4697758B2 (en) * 2000-09-27 2011-06-08 オルガノ株式会社 Desalination wastewater treatment method and apparatus
JP4631148B2 (en) * 2000-10-12 2011-02-16 栗田工業株式会社 Pure water production method
JP5901288B2 (en) * 2011-12-28 2016-04-06 三菱重工メカトロシステムズ株式会社 Wastewater treatment equipment
JP6040789B2 (en) * 2013-01-31 2016-12-07 栗田工業株式会社 Pure water production method and apparatus

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000176457A (en) 1998-12-18 2000-06-27 Hitachi Ltd Waste liquid treatment equipment for semiconductor manufacturing plants

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000176457A (en) 1998-12-18 2000-06-27 Hitachi Ltd Waste liquid treatment equipment for semiconductor manufacturing plants

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2570467C2 (en) * 2014-04-16 2015-12-10 Федеральное государственное бюджетное образовательное учреждение высшего профессионального образования "Башкирский государственный университет" Method of purifying waste water from fluorine

Also Published As

Publication number Publication date
JP2000229289A (en) 2000-08-22

Similar Documents

Publication Publication Date Title
US4969983A (en) Apparatus and process for the removal of acidic and basic gases from fluid mixtures using bipolar membranes
JP4648307B2 (en) Continuous electrodeionization apparatus and method
US5116509A (en) Electrodeionization and ultraviolet light treatment method for purifying water
TWI468346B (en) Method for recovering iodine from waste liquid from polarized thin film
JP4115815B2 (en) Method and apparatus for treating fluorine-containing wastewater
US20090152117A1 (en) Electrodialysis apparatus, waste water treatment method and fluorine treatment system
JPH03207487A (en) Water purification
CN108751523A (en) High-salt wastewater is except firmly except silicon and concentration method and system
JP4403621B2 (en) Electrodeionization equipment
JP3473472B2 (en) Treatment method for fluorine-containing water
JP3656458B2 (en) Pure water production method
JP2000051665A (en) Desalting method
JP3773187B2 (en) Desalination wastewater treatment method and apparatus
JP3695338B2 (en) Method for producing deionized water
JP6924300B1 (en) Wastewater treatment method, ultrapure water production method and wastewater treatment equipment
JPH0649190B2 (en) High-purity water manufacturing equipment
JPH0240220A (en) Pure water producing device
JP2003001258A (en) Electrodeionization equipment
JP4277491B2 (en) Circulation utilization system of fluorine aqueous solution or hydrofluoric acid aqueous solution and its circulation utilization method
JP3884407B2 (en) Method and apparatus for treating fluorine-containing water
JP4505965B2 (en) Pure water production method
JP3714076B2 (en) Fluorine-containing wastewater treatment apparatus and treatment method
JP3501339B2 (en) Electric deionized water production equipment
JPH05309398A (en) Apparatus for producing pure water
JPH06296966A (en) Decarbonating device and pure water producer assembled with the device

Legal Events

Date Code Title Description
FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080919

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090919

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090919

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100919

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110919

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120919

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130919

Year of fee payment: 10

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140919

Year of fee payment: 11

LAPS Cancellation because of no payment of annual fees