JPH05253578A - Treatment of fluorine-containing water - Google Patents
Treatment of fluorine-containing waterInfo
- Publication number
- JPH05253578A JPH05253578A JP4087618A JP8761892A JPH05253578A JP H05253578 A JPH05253578 A JP H05253578A JP 4087618 A JP4087618 A JP 4087618A JP 8761892 A JP8761892 A JP 8761892A JP H05253578 A JPH05253578 A JP H05253578A
- Authority
- JP
- Japan
- Prior art keywords
- fluorine
- reaction tower
- stage reaction
- liquid
- water
- 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
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Landscapes
- Removal Of Specific Substances (AREA)
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明はフッ素含有水の処理方法
の改良に関するものである。さらに詳しくいえば、本発
明は、フッ素系エッチング剤の廃液などからフッ素を高
純度のフッ化カルシウムとして効率よく回収するフッ素
含有水の処理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 improvement of a method for treating fluorine-containing water. More specifically, the present invention relates to a method for treating fluorine-containing water for efficiently recovering fluorine as high-purity calcium fluoride from waste liquid of a fluorine-based etching agent.
【0002】[0002]
【従来の技術】近年、半導体製造分野やその関連分野、
あるいは各種金属材料、単結晶材料、光学系材料などの
表面処理分野などにおいては、多量のエッチング剤が使
用されており、そして、このエッチング剤としては、主
にフッ化水素や、フッ化水素とフッ化アンモニウムを主
成分とするエッチング剤が用いられている。フッ化水素
を主成分とするエッチング剤は、通常フッ素をHFとし
て0.9重量%程度を含む薬剤であって大量に用いられ
ており、一方、フッ化水素及びフッ化アンモニウムを主
成分として含むエッチング剤(バッファードフッ酸)
は、その使用量は少ないものの、フッ素をHFとして通
常7重量%程度含有していることから、これらのエッチ
ング剤は廃水系統へ移行した際、高濃度フッ素含有廃液
となる。一方、エッチング途中やエッチング終了時に
は、これらのエッチング剤で処理された材料を大量の洗
浄水で洗浄するため、その洗浄工程からは、大量の低濃
度フッ素含有廃液が排出される。従来、これらの高濃度
フッ素含有廃液及び低濃度フッ素含有廃液は混合されて
一括処理されている。このフッ素含有廃液の処理には、
一般に水酸化カルシウム[Ca(OH)2]などのカルシ
ウム化合物を添加してフッ化カルシウム(CaF2)と
して沈殿除去する方法が用いられている。しかしなが
ら、このようなフッ化カルシウムとして沈殿除去する方
法においては、フッ素含有水中に含まれるSiO2も、
そのほとんどが不溶化して沈殿するため、回収されたフ
ッ化カルシウムは純度が低いものとなって、再利用価値
が低減するのを免れないという問題がある。他方、炭酸
カルシウムを用いたフッ素処理方法が知られており、こ
の処理方法においては粉状や粒状の炭酸カルシウムが用
いられている。粉状の炭酸カルシウムの場合は、単に中
和剤として利用しているので、過剰に添加されることか
ら、沈殿物中に未反応の炭酸カルシウムが残存し、沈殿
物のフッ化カルシウム純度が低くなるのを免れない。ま
た、粒状の炭酸カルシウムを用いる場合も、これまで炭
酸カルシウム粒子のフッ化カルシウムへの転換率を予測
する手段がなく、回収物のフッ化カルシウム純度は不安
定であった。2. Description of the Related Art In recent years, semiconductor manufacturing fields and related fields,
Alternatively, a large amount of etching agents are used in the field of surface treatment of various metal materials, single crystal materials, optical system materials, etc., and as the etching agents, hydrogen fluoride and hydrogen fluoride are mainly used. An etching agent whose main component is ammonium fluoride is used. An etching agent containing hydrogen fluoride as a main component is usually used in a large amount because it contains fluorine as HF in an amount of about 0.9% by weight, while it contains hydrogen fluoride and ammonium fluoride as main components. Etching agent (buffered hydrofluoric acid)
Although it is used in a small amount, since it usually contains about 7% by weight of fluorine as HF, these etching agents become a high-concentration fluorine-containing waste liquid when transferred to the wastewater system. On the other hand, during or after the etching, the materials treated with these etching agents are washed with a large amount of washing water, so that a large amount of low-concentration fluorine-containing waste liquid is discharged from the washing step. Conventionally, these high-concentration fluorine-containing waste liquids and low-concentration fluorine-containing waste liquids are mixed and collectively processed. For the treatment of this fluorine-containing waste liquid,
Generally, a method is used in which a calcium compound such as calcium hydroxide [Ca (OH) 2 ] is added and precipitated as calcium fluoride (CaF 2 ) to be removed. However, in such a method of removing precipitates as calcium fluoride, SiO 2 contained in the fluorine-containing water is also
Since most of the calcium fluoride is insolubilized and precipitates, the recovered calcium fluoride has a low purity, and there is a problem that the reuse value is unavoidably reduced. On the other hand, a fluorine treatment method using calcium carbonate is known, and powdery or granular calcium carbonate is used in this treatment method. In the case of powdery calcium carbonate, since it is simply used as a neutralizing agent, it is added in excess, so unreacted calcium carbonate remains in the precipitate, and the calcium fluoride purity of the precipitate is low. I cannot help becoming. Also, when granular calcium carbonate is used, there is no means for predicting the conversion rate of calcium carbonate particles to calcium fluoride, and the purity of calcium fluoride in the recovered product is unstable.
【0003】[0003]
【発明が解決しようとする課題】本発明は、このような
従来のフッ素含有水の処理方法が有する欠点を克服し、
炭酸カルシウムによるフッ素含有水の処理方法におい
て、高純度のフッ化カルシウムを安定して回収する方法
を提供することを目的としてなされたものである。DISCLOSURE OF THE INVENTION The present invention overcomes the drawbacks of the conventional method for treating fluorine-containing water,
The object of the present invention is to provide a method for stably recovering high-purity calcium fluoride in a method for treating fluorine-containing water with calcium carbonate.
【0004】[0004]
【課題を解決するための手段】本発明者らは、前記目的
を達成するために鋭意研究を重ねた結果、フッ素含有水
を炭酸カルシウム充填層に上向流で通水して処理する
際、該充填層の入口液と出口液のフッ素濃度又はpHがほ
ぼ同一になるまで通水処理することにより、ほぼ100
%近い純度のフッ化カルシウムを回収しうることを見い
出し、この知見に基づいて本発明を完成するに至った。
すなわち、本発明は、フッ素含有水を炭酸カルシウム充
填層に上向流で通水して、該フッ素含有水中のフッ素を
除去するとともにフッ化カルシウムを回収するに当た
り、前記炭酸カルシウム充填層の入口液と出口液のフッ
素濃度又はpHがほぼ同一になるまで通水処理することを
特徴とするフッ素含有水の処理方法を提供するものであ
る。Means for Solving the Problems As a result of intensive studies to achieve the above object, the present inventors have found that when fluorine-containing water is treated by passing water through a calcium carbonate packed bed in an upward flow, Approximately 100 is obtained by performing water treatment until the fluorine concentration or pH of the inlet liquid and the outlet liquid of the packed bed becomes approximately the same.
It has been found that calcium fluoride with a purity close to 100% can be recovered, and the present invention has been completed based on this finding.
That is, the present invention is to pass the fluorine-containing water through the calcium carbonate packed bed in an upward flow to remove the fluorine in the fluorine-containing water and to recover the calcium fluoride, the inlet liquid of the calcium carbonate packed layer. The present invention provides a method for treating fluorine-containing water, characterized in that water treatment is carried out until the fluorine concentration or pH of the outlet liquid becomes substantially the same.
【0005】以下、本発明を添付図面に従って詳細に説
明する。図1は、本発明方法を実施するための1例の説
明図であって、まずエッチング廃水等のフッ素含有水
(被処理液)1はNo.1被処理液タンク2又はNo.2
被処理液タンク3に移送される。このタンクは被処理液
の均一化及び安定化のために設置され、2基以上あると
都合がよい。被処理液は、例えばNo.1タンク2に移
送され、満水になったら混合して均一化し、ポンプ4に
より、径0.1〜0.5mm程度の粒状炭酸カルシウムが充
填された1段目の反応塔5へ供給する。一方、新たに排
出される被処理液はNo.2タンク3に入れ貯留する。
被処理液タンク2及び3の容量は反応塔容量の3倍以上
が望ましい。The present invention will be described in detail below with reference to the accompanying drawings. FIG. 1 is an explanatory diagram of an example for carrying out the method of the present invention. First, fluorine-containing water (processing liquid) 1 such as etching wastewater is No. 1 processing liquid tank 2 or No. 2
It is transferred to the liquid tank 3 to be treated. This tank is installed for homogenization and stabilization of the liquid to be treated, and it is convenient to have two or more tanks. The liquid to be treated is transferred to, for example, No. 1 tank 2, and when it becomes full, it is mixed and homogenized, and the first stage filled with granular calcium carbonate having a diameter of about 0.1 to 0.5 mm by a pump 4. Supply to the reaction tower 5. On the other hand, the liquid to be newly discharged is put in the No. 2 tank 3 and stored.
It is desirable that the volumes of the liquid tanks 2 and 3 to be treated be at least three times the volume of the reaction tower.
【0006】被処理液はポンプ4によって1段目の反応
塔5に上向流で供給される。上記エッチング廃水等の中
には、通常フッ化水素又はフッ化水素とフッ化アンモニ
ウムとが含まれており、フッ化水素によって二酸化炭素
ガスが発生するので、被処理液を下向流で供給すると、
塔内はガス流によって水切れ現象が生じ、供給液の偏流
をもたらし、反応が阻害されるという好ましくない事態
を招来する。本発明においては、該被処理液の供給は、
ポンプ4により間欠的に行うのが望ましい。この間欠的
な通水により、前記したように発生する二酸化炭素ガス
の作用と相俟って、炭酸カルシウムのかたまりを効果的
にほぐすことができ、炭酸カルシウムは効率よくフッ化
カルシウムに変換される。運転−停止の流量、時間につ
いては、被処理液中のフッ素濃度、充填炭酸カルシウム
の粒度や充填高さ、被処理液温度などにより影響を受け
るので、それらに応じて最適条件を適宜選ぶのがよい。The liquid to be treated is supplied by the pump 4 to the first-stage reaction tower 5 in an upward flow. The etching wastewater or the like usually contains hydrogen fluoride or hydrogen fluoride and ammonium fluoride, and since carbon dioxide gas is generated by the hydrogen fluoride, if the liquid to be treated is supplied in a downward flow. ,
The gas flow causes a water drainage phenomenon in the column, which causes an unbalanced flow of the feed liquid, resulting in an unfavorable situation in which the reaction is hindered. In the present invention, the supply of the liquid to be treated is
It is desirable to intermittently perform by the pump 4. Due to this intermittent flow of water, in combination with the action of carbon dioxide gas generated as described above, the lumps of calcium carbonate can be effectively loosened, and calcium carbonate is efficiently converted to calcium fluoride. .. The flow rate and time of operation-stop are influenced by the fluorine concentration in the liquid to be treated, the particle size and filling height of the filled calcium carbonate, the temperature of the liquid to be treated, etc. Good.
【0007】本発明においては、フッ化水素含有量の極
めて少ない被処理液を処理する場合には、所望により、
空気を反応塔内に連続的又は間欠的にバブリングさせて
もよいし、該被処理液に塩化水素などの酸を添加しても
よい。なお、被処理液のpHは4〜6の範囲が好ましく、
必要ならばアルカリや酸を添加してpH調整を行ってもよ
い。1段目の反応塔5から出た処理液は、全量第2段目
の反応塔8に流入されるとともに、1段目の反応塔5で
発生したガスも分離することなく、2段目の反応塔8に
導入される。In the present invention, when treating a liquid to be treated having an extremely low hydrogen fluoride content, if desired,
Air may be bubbled into the reaction column continuously or intermittently, or an acid such as hydrogen chloride may be added to the liquid to be treated. The pH of the liquid to be treated is preferably in the range of 4 to 6,
If necessary, alkali or acid may be added to adjust the pH. The entire amount of the treatment liquid discharged from the first-stage reaction tower 5 flows into the second-stage reaction tower 8, and the gas generated in the first-stage reaction tower 5 is not separated, and the second-stage reaction tower 5 is not separated. It is introduced into the reaction tower 8.
【0008】本発明においては、炭酸カルシウム充填層
の入口液及び出口液のpH又はフッ素濃度を監視すること
が必要であるので、1段目反応塔5の入口及び出口ライ
ンの適当な場所にpH計やフッ素濃度計6及び7が設けら
れる。1段目反応塔5の処理液は2段目反応塔8に供給
されるが、1段目反応塔の入口液及び出口液のpHやフッ
素濃度がほぼ一致したら、ポンプ4の運転を止めて通水
を停止し、1段目反応塔内の充填物を抜き出してフッ化
カルシウムを回収する。この際、該充填物に付着する被
処理液の水切り及び水洗を行ってから抜き出しする方が
フッ化カルシウムの純度が向上するとともに、移送時の
危険対策にもなるので有利である。2段目反応塔8の処
理液9はpH計やフッ素濃度計10によって処理効果を確
認し、処理水として排出する。In the present invention, since it is necessary to monitor the pH or the fluorine concentration of the inlet liquid and the outlet liquid of the calcium carbonate packed bed, it is necessary to monitor the pH at appropriate places in the inlet and outlet lines of the first stage reaction tower 5. And a fluorine concentration meter 6 and 7 are provided. The treatment liquid of the first-stage reaction tower 5 is supplied to the second-stage reaction tower 8, but if the pH and the fluorine concentration of the inlet liquid and the outlet liquid of the first-stage reaction tower are almost the same, stop the operation of the pump 4. The water flow is stopped, and the packing material in the first reaction column is extracted to recover calcium fluoride. At this time, it is advantageous to drain the liquid to be treated adhering to the filling material, to wash it, and then to withdraw it, because the purity of calcium fluoride is improved and it becomes a countermeasure against danger during transfer. The treatment effect of the treatment liquid 9 in the second-stage reaction tower 8 is confirmed by a pH meter and a fluorine concentration meter 10, and the treated liquid 9 is discharged as treated water.
【0009】1段目反応塔5の入口液及び出口液のpH又
はフッ素濃度がほぼ一致して、1段目反応塔5の充填材
を抜き出した後は、新たな炭酸カルシウムを充填する
が、その場合、被処理水の通水は反応塔8→反応塔5の
方向に行うメリーゴーランド方式とする。この場合、pH
計やフッ素濃度計の役割もそれに応じて変わることにな
る。また、本発明方法においては反応塔の入口及び出口
のフッ素濃度から、フッ素の除去量を算出することによ
って、塔内の充填材のフッ化カルシウムへの転換率を知
ることが可能であり、その結果、充填材の取り替え日を
予測することができる。このような処理によって、ほぼ
100%に近い純度のフッ化カルシウムを回収すること
ができる。After the pH or fluorine concentration of the inlet liquid and the outlet liquid of the first-stage reaction tower 5 are almost the same, and after the filler of the first-stage reaction tower 5 is extracted, new calcium carbonate is charged. In that case, the water to be treated is passed through the merry-go-round system in the direction of the reaction tower 8 → the reaction tower 5. In this case, the pH
The role of the meter and fluorine concentration meter will change accordingly. Further, in the method of the present invention, from the fluorine concentration at the inlet and the outlet of the reaction column, by calculating the amount of fluorine removed, it is possible to know the conversion rate of the filler in the column to calcium fluoride, As a result, the replacement date of the filler can be predicted. By such a treatment, it is possible to recover calcium fluoride having a purity of almost 100%.
【0010】[0010]
【実施例】次に実施例により本発明をさらに詳細に説明
するが、本発明はこれらの例によってなんら限定される
ものではない。The present invention will be described in more detail by way of examples, which should not be construed as limiting the invention thereto.
【0011】実施例1 径0.25mmの粒状炭酸カルシウム100ミリリットル
を内径30mmのカラムに充填した。このカラム2本をシ
リーズに連結し、1段目カラムに被処理液をSV1hr
-1の流速で通水し、2段目カラムから処理液を抜き出し
た。被処理液として、NH4F、HF及びH2SiF6を
混合して純水に加え、HF/全Fモル比0.13、フッ
素濃度22〜25g・F/リットル、SiO2濃度0〜2
g/リットルのものを調製して用いた。48時間通水
後、運転を止めて、カラム入口液及び1段目カラム出口
液と2段目カラム出口液のフッ素濃度及びpHを測定する
とともに、各カラムの充填物を水洗後に抜き出し、フッ
化カルシウムの純度を測定した。なお、フッ化カルシウ
ムの純度はJIS K-1468のウインラード/ウイン
ター法に準じて求めた。結果を第1表に示す。Example 1 100 ml of granular calcium carbonate having a diameter of 0.25 mm was packed in a column having an inner diameter of 30 mm. These two columns are connected in series, and the solution to be treated is SV1hr in the first column.
Water was passed at a flow rate of -1 , and the treatment liquid was extracted from the second column. As the liquid to be treated, NH 4 F, HF and H 2 SiF 6 were mixed and added to pure water to obtain a HF / total F molar ratio of 0.13, a fluorine concentration of 22 to 25 g · F / liter, and a SiO 2 concentration of 0 to 2
A g / l product was prepared and used. After passing water for 48 hours, stop the operation, measure the fluorine concentration and pH of the column inlet liquid, the first-stage column outlet liquid, and the second-stage column outlet liquid, extract the packing of each column after washing with water, and fluorinate. The purity of calcium was measured. The purity of calcium fluoride was determined according to the Winrad / Winter method of JIS K-1468. The results are shown in Table 1.
【0012】[0012]
【表1】 [Table 1]
【0013】第1表から、被処理液と1段目カラム処理
液のフッ素濃度がほぼ同一になるとフッ化カルシウムの
純度が100%近くなることが分かる。またpHについて
も同様なことが言える。1段目カラムでのフッ素除去率
が高い(未飽和)とその処理液中にNH4CO3が多量に
含まれpHが上昇する。しかし、pH10以下ではpHを調整
することなく、2段目カラムにてフッ素が除去される。
フッ化カルシウム純度とフッ素除去率との関係及びフッ
化カルシウム純度とpH比(処理液pH/被処理pH)との関
係を、それぞれ図1及び図2にグラフで示す。It can be seen from Table 1 that the purity of calcium fluoride becomes close to 100% when the fluorine concentration of the liquid to be treated and that of the liquid to be treated in the first column are almost the same. The same applies to pH. If the removal rate of fluorine in the first-stage column is high (unsaturated), a large amount of NH 4 CO 3 is contained in the treatment liquid and the pH rises. However, below pH 10, fluorine is removed in the second column without adjusting the pH.
The relationship between the calcium fluoride purity and the fluorine removal rate and the relationship between the calcium fluoride purity and the pH ratio (treatment solution pH / treatment pH) are shown in FIGS. 1 and 2, respectively.
【0014】[0014]
【発明の効果】本発明のフッ素含有水の処理方法による
とほぼ100%に近い純度のフッ化カルシウムが回収さ
れるので再資源化が容易になる。また充填材の取替頻度
が予測でき、計画的な運転操作が可能になる。According to the method for treating fluorine-containing water of the present invention, since calcium fluoride having a purity of nearly 100% is recovered, recycling can be facilitated. Moreover, the frequency of replacement of the filler can be predicted, and the planned operation can be performed.
【図1】図1は本発明方法を実施するための1例の説明
図である。FIG. 1 is an illustration of an example for carrying out the method of the present invention.
【図2】図2は実施例において、フッ化カルシウム純度
とフッ素除去率との関係を示すグラフである。FIG. 2 is a graph showing the relationship between the calcium fluoride purity and the fluorine removal rate in the examples.
【図3】図3は実施例において、フッ化カルシウム純度
とpH比(処理液pH/被処理液pH)との関係を示すグラフ
である。FIG. 3 is a graph showing the relationship between calcium fluoride purity and pH ratio (treatment liquid pH / treatment liquid pH) in Examples.
1 被処理液 2 No.1被処理液タンク 3 No.2被処理液タンク 4 ポンプ 5 1段目反応塔 6 pH計及び/又はフッ素濃度計 7 pH計及び/又はフッ素濃度計 8 2段目反応塔 9 処理液 10 pH計及び/又はフッ素濃度計 11 流量計 1 treated liquid 2 No. 1 treated liquid tank 3 No. 2 treated liquid tank 4 pump 5 1st stage reaction tower 6 pH meter and / or fluorine concentration meter 7 pH meter and / or fluorine concentration meter 8 2nd stage Reaction tower 9 Treatment liquid 10 pH meter and / or fluorine concentration meter 11 Flow meter
Claims (1)
向流で通水して、該フッ素含有水中のフッ素を除去する
とともにフッ化カルシウムを回収するに当たり、前記炭
酸カルシウム充填層の入口液と出口液のフッ素濃度又は
pHがほぼ同一になるまで通水処理することを特徴とする
フッ素含有水の処理方法。1. When the fluorine-containing water is passed through the calcium carbonate packed bed in an upward flow to remove fluorine in the fluorine-containing water and to recover calcium fluoride, an inlet liquid of the calcium carbonate packed layer is used. Fluorine concentration in outlet liquid or
A method for treating fluorine-containing water, characterized in that water treatment is carried out until the pH becomes almost the same.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP08761892A JP3466637B2 (en) | 1992-03-11 | 1992-03-11 | Method and apparatus for treating fluorine-containing water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP08761892A JP3466637B2 (en) | 1992-03-11 | 1992-03-11 | Method and apparatus for treating fluorine-containing water |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH05253578A true JPH05253578A (en) | 1993-10-05 |
JP3466637B2 JP3466637B2 (en) | 2003-11-17 |
Family
ID=13919964
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP08761892A Expired - Lifetime JP3466637B2 (en) | 1992-03-11 | 1992-03-11 | Method and apparatus for treating fluorine-containing water |
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Country | Link |
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JP (1) | JP3466637B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0698579A2 (en) | 1994-08-26 | 1996-02-28 | Sharp Kabushiki Kaisha | Apparatus and method for treatment of waste water and/or exhaust gases containing fluorine and surface active agents |
-
1992
- 1992-03-11 JP JP08761892A patent/JP3466637B2/en not_active Expired - Lifetime
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0698579A2 (en) | 1994-08-26 | 1996-02-28 | Sharp Kabushiki Kaisha | Apparatus and method for treatment of waste water and/or exhaust gases containing fluorine and surface active agents |
US5702594A (en) * | 1994-08-26 | 1997-12-30 | Sharp Kabushiki Kaisha | Apparatus for treatment of waste water and/or exhaust gases containing fluorine and surface active agents |
Also Published As
Publication number | Publication date |
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JP3466637B2 (en) | 2003-11-17 |
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