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JPH0783819B2 - Method and apparatus for treating wastewater containing fluoric and hydrogen peroxide and exhaust gas - Google Patents

Method and apparatus for treating wastewater containing fluoric and hydrogen peroxide and exhaust gas

Info

Publication number
JPH0783819B2
JPH0783819B2 JP61171027A JP17102786A JPH0783819B2 JP H0783819 B2 JPH0783819 B2 JP H0783819B2 JP 61171027 A JP61171027 A JP 61171027A JP 17102786 A JP17102786 A JP 17102786A JP H0783819 B2 JPH0783819 B2 JP H0783819B2
Authority
JP
Japan
Prior art keywords
exhaust gas
hydrogen peroxide
wastewater
fluorine
scrubber
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
JP61171027A
Other languages
Japanese (ja)
Other versions
JPS6328429A (en
Inventor
康修 森
弘治 三好
利道 三原
裕治 若林
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.)
Takenaka Corp
Original Assignee
Takenaka Corp
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 Takenaka Corp filed Critical Takenaka Corp
Priority to JP61171027A priority Critical patent/JPH0783819B2/en
Publication of JPS6328429A publication Critical patent/JPS6328429A/en
Publication of JPH0783819B2 publication Critical patent/JPH0783819B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Removal Of Specific Substances (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、電子部品や電気部品等の製造工場から排出さ
れる弗素,過酸化水素含有廃水及び排ガスの処理方法及
び装置に関するものである。
Description: TECHNICAL FIELD The present invention relates to a method and an apparatus for treating fluorine- and hydrogen peroxide-containing wastewater and exhaust gas discharged from a factory for manufacturing electronic parts, electric parts and the like.

〔従来の技術〕[Conventional technology]

電子部品や電気部品の製造に於て、弗素化合物はエッチ
ッグ等の表面処理工程では欠くことのできない物質であ
り、一般に広く使用されている。同時に、部品等の洗浄
等のために過酸化水素を使用することが多く、特に半導
体製造工場に於ては、弗素化合物の廃水に過酸化水素が
混入している場合が多い。
In the manufacture of electronic parts and electric parts, fluorine compounds are substances that are indispensable in the surface treatment process such as etching and are widely used. At the same time, hydrogen peroxide is often used for cleaning parts and the like, and particularly in semiconductor manufacturing plants, hydrogen peroxide is often mixed in waste water of fluorine compounds.

廃水中に含まれる弗素化合物は、多種多様のものがある
が、半導体製造工場では弗酸や弗化アンモニウム等が代
表例である。
There are various kinds of fluorine compounds contained in the wastewater, but in semiconductor manufacturing plants, typical examples are hydrofluoric acid and ammonium fluoride.

これらの弗素を廃水から除去する方法として、従来から
様々な方法が取られている。
Various methods have heretofore been used as methods for removing these fluorine from wastewater.

主な処理方法としては、 カルシュウム化合物添加+沈澱分離法 アルミニウム化合物添加+沈澱分離法 鉄塩添加 +沈澱分離法 上記,,の内2つ以上の組合せ カルシュウム塩+リン酸塩+沈澱法 活性アルミナによる吸着法 活性炭又は骨炭による吸着法 等がある。The main treatment methods are calcium compound addition + precipitation separation method Aluminum compound addition + precipitation separation method Iron salt addition + precipitation separation method Combination of two or more of the above, calcium salt + phosphate + precipitation method Activated alumina Adsorption method There is an adsorption method using activated carbon or bone charcoal.

この内、水質汚濁防止法に於ける排水基準である弗素化
合物15mg/を満足させる方法として、維持管理費が比
較的安価であることから、上記〜の凝集沈澱法が広
く採用されている。
Among these methods, the coagulation-precipitation method (1) to (4) above is widely adopted as a method for satisfying the fluorine compound content of 15 mg / which is the drainage standard in the Water Pollution Control Law because the maintenance cost is relatively low.

然し、前述したように、凝集沈澱法を行なう系統に過酸
化水素が数十〜数万mg/の割合で混入する場合が多
く、このままでは過酸化水素による微細気泡が、カルシ
ュウム塩等によって形成されたフロックに付着して一旦
沈澱槽に沈澱したスラッジから気泡が発生し、フロック
が再浮上して沈澱槽から溢流し、次工程に流出してしま
う。このフロックの流出によって、処理水中に高濃度の
弗化物やSSが検出されることもあった。
However, as described above, hydrogen peroxide is often mixed in the system for performing the coagulation-sedimentation method at a rate of several tens to several tens of thousands mg / min. Air bubbles are generated from the sludge that once adheres to the flocs and settles in the settling tank, and the flocs re-float and overflow from the settling tank to flow out to the next step. Due to the outflow of flocs, high concentrations of fluoride and SS were sometimes detected in the treated water.

そこで、過酸化水素除去のために、従来から活性炭によ
る吸着法や、重亜硫酸ナトリュウム等の還元剤注入によ
る化学反応法等が行なわれている。
Therefore, in order to remove hydrogen peroxide, an adsorption method using activated carbon and a chemical reaction method by injecting a reducing agent such as sodium bisulfite have been conventionally performed.

第4図は重亜硫酸ナトリュウム等の還元剤注入による化
学反応法を示す説明図で、弗素と過酸化水素を含む廃水
は、先ず、還元剤を添加する反応槽1に流入し、ここで
過酸化水素の分解を行なう。次に、過酸化カルシュウム
を添加する反応槽2に流入し、ここで弗化カルシュウム
を生成する。更に、この弗化カルシュウムを反応槽3に
於て、高分子凝集剤によって凝集させる。その後、沈澱
槽4に流入して、スラッジを底部から抜き取り、上部か
ら処理水を吐出する。尚、沈澱槽4での滞留時間は一般
に3〜5時間である。
FIG. 4 is an explanatory view showing a chemical reaction method by injecting a reducing agent such as sodium bisulfite. Waste water containing fluorine and hydrogen peroxide first flows into the reaction tank 1 to which the reducing agent is added, and the peroxidation is performed there. Decomposes hydrogen. Next, it flows into the reaction tank 2 to which calcium peroxide is added, where calcium fluoride is produced. Further, the calcium fluoride is coagulated in the reaction tank 3 by the polymer coagulant. Then, it flows into the settling tank 4, the sludge is extracted from the bottom, and the treated water is discharged from the upper part. The residence time in the settling tank 4 is generally 3 to 5 hours.

又、例えば半導体工場から排出される排ガスとしては、
弗酸,塩酸,硝酸,硫酸等のの酸系ガス、アンモニアガ
ス等のアルカリ系、アルコール,現像液等の有機系、シ
ラン,アルシン,ホスフィン等の毒系等があり、これら
はこれに応じたスクラバーによって処理されている。
Also, for example, as exhaust gas emitted from a semiconductor factory,
There are acid gases such as hydrofluoric acid, hydrochloric acid, nitric acid, and sulfuric acid, alkali gases such as ammonia gas, organic solvents such as alcohol and developer, poisonous gases such as silane, arsine, and phosphine. It is being processed by a scrubber.

〔発明が解決しようとする問題点〕[Problems to be solved by the invention]

然し、従来方法では廃水と排ガスとが各別に処理される
ため、設備が大掛かりとなりい望ましくなかった。
However, in the conventional method, the waste water and the exhaust gas are treated separately, which is not desirable because the equipment becomes large.

又、廃水の処理に於ても、活性炭吸着法はランニングコ
ストが高く、又、過酸化水素のみを選択的に吸着する訳
ではなく、有機物や金属等も多量に吸着してしまうの
で、効率が良くない。還元剤注入法も維持管理費が掛か
り、運転管理も繁雑となる外、処理水には微細なフロッ
クが混入し、良好な処理水を得ることが難しい、といっ
た問題がある。
Also, in the treatment of wastewater, the activated carbon adsorption method has a high running cost, and not only hydrogen peroxide is not selectively adsorbed but a large amount of organic substances, metals, etc. are also adsorbed, resulting in high efficiency. Not good. The reducing agent injection method has a problem that maintenance costs are high, operation management is complicated, and fine flocs are mixed in the treated water, making it difficult to obtain good treated water.

〔発明の目的〕[Object of the Invention]

本発明は斯る従来の問題点を解決するために為されたも
ので、その目的は、弗素,過酸化水素の除去と排ガス処
理とを簡便な手段によって行なうことにある。
The present invention has been made to solve the conventional problems, and an object thereof is to remove fluorine and hydrogen peroxide and to treat exhaust gas by a simple means.

〔問題点を解決するための手段〕[Means for solving problems]

本発明に係る弗素,過酸化水素含有廃水及び排ガスの処
理方法は、弗素,過酸化水素含有廃水と排ガスとを、上
部に排ガス処理用充填物を設け、下部に金属触媒を設け
たスクラバーに導入し、廃水を金属触媒に接触させて過
酸化水素を気泡化し、滴下する廃水に金属塩又は金属化
合物を添加して弗素化合物を生成した後、スクラバーか
ら排出して反応槽に於て高分子凝集剤を添加して弗素化
合物を凝集フロックとし、次いで加圧浮上槽の底部から
加圧水と共に流入させて固液を分離し、処理液の一部を
スクラバーの排ガス処理用充填物に散布しながら排ガス
を通過させるように構成したものである。
In the method for treating wastewater containing fluorine and hydrogen peroxide and exhaust gas according to the present invention, wastewater containing fluorine and hydrogen peroxide and exhaust gas are introduced into a scrubber provided with an exhaust gas treatment filler in the upper part and a metal catalyst in the lower part. Then, the wastewater is contacted with a metal catalyst to bubble hydrogen peroxide, and a metal salt or a metal compound is added to the dropped wastewater to generate a fluorine compound, which is then discharged from a scrubber and polymer aggregates in a reaction tank. A fluorine compound is added to make flocculant flocs, then it is made to flow with pressurized water from the bottom of the pressure flotation tank to separate the solid liquid, and a part of the treatment liquid is sprayed onto the scrubber exhaust gas treatment filler to generate the exhaust gas. It is configured to pass.

又、本発明に係る弗素,過酸化水素含有廃水及び排ガス
の処理装置は、上部に排ガス処理用充填物を設け、下部
に金属触媒を設け、排ガス処理用充填物と金属触媒との
間に弗素,過酸化水素含有廃水と排ガスとを各別に導入
する流入管を設け、排ガス処理用充填物の上部に吸収液
散布用管を設け、金属触媒の下部に滴下する廃水に金属
塩又は金属化合物と反応させる廃水貯溜槽を形成したス
クラバーと、このスクラバーと管路を介して連結し、高
分子凝集剤と廃水とを撹拌混合させる反応槽と、この反
応槽と管路を介して底部で連結し、上記管路に供給され
る加圧水と共に廃水を流入させ凝集フロックを分離する
加圧浮上槽と、この加圧浮上槽から導出された処理水を
貯溜する貯溜槽と、この貯溜槽と排ガス処理用充填物の
上部に設けた吸収液散布用管とを連結し、ポンプによっ
て貯溜槽中の処理水と所望の中和剤とを送水する吸収液
管路とから構成されるものである。
Further, the apparatus for treating wastewater containing fluorine and hydrogen peroxide and the exhaust gas according to the present invention is provided with an exhaust gas treatment filler in the upper portion and a metal catalyst in the lower portion, and fluorine is provided between the exhaust gas treatment filler and the metal catalyst. , Providing an inflow pipe for introducing hydrogen peroxide-containing wastewater and exhaust gas separately, an absorption liquid spraying pipe on the upper part of the exhaust gas treatment packing, and adding a metal salt or a metal compound to the wastewater dropped below the metal catalyst. A scrubber that forms a waste water storage tank to be reacted, a reaction tank that is connected to this scrubber through a pipe line, and that stirs and mixes a polymer flocculant and waste water, and a reaction tank that is connected at the bottom part through a pipe line. , A pressure flotation tank that separates coagulation flocs by inflowing wastewater together with the pressurized water supplied to the pipeline, a storage tank that stores the treated water derived from the pressure flotation tank, and this storage tank and exhaust gas treatment Absorption on top of packing A spray pipe connected and is formed from the absorption liquid pipe for water of the treated water in the reservoir and the desired neutralizing agent by a pump.

本発明に於て、金属塩としてはカルシュウム塩,鉄塩等
が好適である。又、金属化合物としてはカルシュウム化
合物,アルミニュウム化合物等が好適である。
In the present invention, as the metal salt, calcium salt, iron salt and the like are preferable. Further, as the metal compound, a calcium compound, an aluminum compound or the like is suitable.

〔発明の作用〕[Operation of the invention]

本発明に於ては、弗素と過酸化水素とを含む廃水が、金
属塩又は金属化合物及び高分子凝集剤の添加によって弗
素化合物の凝集フロックを生成した後、加圧浮上槽内に
加圧水と共に流入されるから、加圧水が大気開放される
ことによって生じる微細気泡により、それまで凝集フロ
ックに殆ど付着していた気泡は浮上し除去されると同時
に廃水中に溶解している過酸化水素の一部も気泡化して
上昇して除去される。又、排ガスは、廃水処理済の処理
液を散布する排ガス処理用充填物を通過するから、処理
液に有害物が吸収されたり、中和されたりして排気され
る。
In the present invention, wastewater containing fluorine and hydrogen peroxide flows into the pressurized flotation tank together with pressurized water after the aggregate flocs of the fluorine compound are generated by the addition of the metal salt or the metal compound and the polymer flocculant. Therefore, due to the fine bubbles generated by the pressurized water being released to the atmosphere, the bubbles that had mostly adhered to the flocs until then floated up and were removed, and at the same time, part of the hydrogen peroxide dissolved in the wastewater was also removed. Bubbles rise and are removed. Further, since the exhaust gas passes through the exhaust gas treatment filler that sprays the wastewater-treated treatment liquid, harmful substances are absorbed or neutralized by the treatment liquid and are exhausted.

〔発明の実施例〕Example of Invention

以下、本発明の実施例を図面に基づいて説明する。 Embodiments of the present invention will be described below with reference to the drawings.

第1図は本発明に於けるプロセスを説明するための図で
ある。
FIG. 1 is a diagram for explaining the process in the present invention.

図に於て、10はスクラバーで、上部に排ガス処理用充填
物11を設け、下部に金属触媒12を設け、排ガス処理用充
填物11と金属触媒12との間に、弗素,過酸化水素含有廃
水を導入する管路に連結する散布管13と、排ガスを導入
する管路14とが各別に設けてある。又、排ガス処理用充
填物11の上部には、吸収液散布用管15を設け、金属触媒
12の下部には滴下する廃水に金属塩又は金属化合物と反
応させる廃水貯溜槽16が形成してある。この廃水貯溜槽
16には、撹拌用空気を導入する管17が設けてある。そし
て、このスクラバー10には、上部に排ガスを排気する吐
出口18が設けてある。尚、金属触媒12の材質としては、
貴金属が最も良いが、銅,鉄でも可能である。形状とし
ては、円筒形状の充填物或いは網状にして容器内に設置
するようにしたものでも良い。
In the figure, 10 is a scrubber, which is provided with an exhaust gas treatment filler 11 in the upper portion and a metal catalyst 12 in the lower portion, and contains fluorine and hydrogen peroxide between the exhaust gas treatment filler 11 and the metal catalyst 12. A spray pipe 13 connected to a pipe for introducing waste water and a pipe 14 for introducing exhaust gas are separately provided. In addition, a pipe 15 for absorbing liquid is provided on the upper portion of the exhaust gas treatment filler 11, and a metal catalyst
A waste water storage tank 16 for reacting the dripping waste water with a metal salt or a metal compound is formed at the lower part of 12. This wastewater storage tank
The tube 16 is provided with a pipe 17 for introducing stirring air. The scrubber 10 is provided at its upper portion with a discharge port 18 for exhausting exhaust gas. Incidentally, as the material of the metal catalyst 12,
Precious metals are the best, but copper and iron are also possible. The shape may be a cylindrical packing or a net-like one that is installed in the container.

20はこのスクラバー10と管路10を介して連結し、高分子
凝集剤と廃水とを撹拌混合させる反応槽である。内部に
撹拌器21が設けてある。
Reference numeral 20 is a reaction tank which is connected to the scrubber 10 through the pipe line 10 to stir and mix the polymer coagulant and the waste water. An agitator 21 is provided inside.

23はこの反応槽20と管路22を介して底部24で連結し、上
記管路22に供給される加圧水と共に廃水を流入させ凝集
フロックを分離する加圧浮上槽である。この加圧浮上槽
23ではスラッジを排出する管路25と処理水を排出する管
路26とが上部に各別に設けてある。
Reference numeral 23 is a pressure flotation tank that is connected to the reaction tank 20 at a bottom portion 24 via a pipe line 22 and separates coagulated flocs by inflowing waste water together with the pressurized water supplied to the pipe line 22. This pressurized flotation tank
In 23, a pipeline 25 for discharging sludge and a pipeline 26 for discharging treated water are separately provided at the upper part.

27はこの加圧浮上槽23から排出された処理水を貯溜する
貯溜槽である。この貯溜槽27から処理水が排出される。
27 is a storage tank for storing the treated water discharged from the pressurized flotation tank 23. The treated water is discharged from this storage tank 27.

28はこの貯溜槽27と排ガス処理用充填物11の上部に設け
た吸収液散布用管15とを連結し、循環ポンプ29によって
貯溜槽27中の処理水と所望の中和剤とを送水する吸収液
管路である。
Reference numeral 28 connects this storage tank 27 with the absorption liquid spraying pipe 15 provided on the upper part of the exhaust gas treatment filler 11 and sends the treated water in the storage tank 27 and a desired neutralizing agent by a circulation pump 29. This is the absorption liquid line.

次に、このように構成された本実施例の作用を説明す
る。
Next, the operation of the present embodiment configured as described above will be described.

弗素と過酸化水素とを含む廃水と排ガスは、それぞれ散
布管13及び管路14を介してスクラバー10に導入される。
Waste water containing fluorine and hydrogen peroxide and exhaust gas are introduced into the scrubber 10 via the spray pipe 13 and the pipe 14, respectively.

そして、廃水は、金属触媒12に散布管13によって散布さ
れると、廃水中の過酸化水素が金属触媒12と接触するこ
とによって気泡化される。そのため、酸素はスクラバー
10内を上昇し、廃水は下方の廃水貯溜槽16に滴下してい
く。
Then, when the waste water is sprayed on the metal catalyst 12 by the spray tube 13, hydrogen peroxide in the waste water comes into contact with the metal catalyst 12 to be bubbled. Therefore, oxygen is a scrubber
Ascending within 10, the wastewater drops into the wastewater storage tank 16 below.

廃水貯溜槽16では、所望の水酸化カルシュウムが添加さ
れると共に撹拌用空気が管17を介して供給されており、
廃水中の弗素が水酸化カルシュウムと化学反応して弗化
カルシュウムを生成する。
In the waste water storage tank 16, desired calcium hydroxide is added and stirring air is supplied through a pipe 17,
Fluorine in the wastewater chemically reacts with calcium hydroxide to produce calcium fluoride.

次に、廃水貯溜槽16で処理された廃水は、管路19を介し
て反応槽20に送られる。反応槽20では、所望量添加され
る高分子凝集剤と撹拌器21によって撹拌されて、弗化カ
ルシュウムの凝集してフロックを大きくする。
Next, the wastewater treated in the wastewater storage tank 16 is sent to the reaction tank 20 via the conduit 19. In the reaction tank 20, the polymer flocculant added in a desired amount and the agitator 21 are agitated to agglomerate calcium fluoride to increase flocs.

その後、反応槽20で処理された廃水は、管路22を介して
加圧浮上槽23の底部24から加圧水と共に流入する。この
際、加圧水が大気解放された時に生じる微細気泡によっ
て、それまでに凝集フロックに殆ど付着していた気泡が
浮上し、除去される。同時に、加圧水による微細気泡に
よって原水中に溶解している過酸化水素の一部も気泡化
し、上昇して除去される。
After that, the wastewater treated in the reaction tank 20 flows in together with the pressurized water from the bottom portion 24 of the pressurized flotation tank 23 through the pipe line 22. At this time, fine bubbles generated when the pressurized water is released to the atmosphere raises and removes the bubbles that have mostly adhered to the flocs until then. At the same time, a part of the hydrogen peroxide dissolved in the raw water is also bubbled by the fine bubbles of the pressurized water, rising and removed.

この加圧浮上槽23に於ける『原水+加圧水』の滞留時間
は1〜3時間とする。これは、一般に使用されている加
圧浮上槽の滞留時間は30分前後であるが、加圧浮上槽14
内での過酸化水素の気泡発生を充分に行なわせるためで
ある。
The residence time of “raw water + pressurized water” in the pressure floating tank 23 is 1 to 3 hours. This is because the pressure levitation tank generally used has a residence time of around 30 minutes.
This is in order to sufficiently generate bubbles of hydrogen peroxide inside.

この気泡発生の効率を上げるためには、反応槽20に銅や
鉄等を注入するか、他の排水系統で有機物が含まれる水
を混入することが有効である。
In order to increase the efficiency of bubble generation, it is effective to inject copper, iron or the like into the reaction tank 20 or mix water containing organic matter in another drainage system.

ここで、銅としては、硫酸銅等があり、又、鉄として
は、硫酸第一鉄,硫酸第二鉄,塩化第一鉄,塩化第二鉄
等がある。又、有機系排水としては、し尿浄化槽処理
水,アルコール含有排水,脂肪酸含有排水等がある。
Here, the copper includes copper sulfate and the like, and the iron includes ferrous sulfate, ferric sulfate, ferrous chloride, ferric chloride and the like. The organic waste water includes human waste septic tank treated water, alcohol-containing waste water, fatty acid-containing waste water, and the like.

斯くして、加圧浮上槽23でスラッジを除去した処理水
は、管路26を介して貯溜槽27に送られる。そして、ここ
からポンプ29によって吸収液管路28を介してスクラバー
1内の吸収液散布管6に送られ、排ガス処理用充填物11
に散布される。
Thus, the treated water from which the sludge has been removed in the pressure flotation tank 23 is sent to the storage tank 27 via the pipe line 26. Then, from here, it is sent by the pump 29 to the absorbent dispersion pipe 6 in the scrubber 1 through the absorbent conduit 28, and the exhaust gas treating filler 11
Be sprinkled on.

この吸収液散布管15から散布される液は、排ガスの種類
に応じて所望の薬液が添加されるが、本実施例では排ガ
スが弗酸であるから、カセーソーダを添加してpHを9〜
10にしてある。
A desired chemical liquid is added to the liquid sprayed from the absorbent spray pipe 15 according to the type of the exhaust gas, but in the present embodiment, since the exhaust gas is hydrofluoric acid, caustic soda is added to adjust the pH to 9 to 9.
It's set to 10.

従って、管14を介してスクラバー10内に導入された排ガ
ス(弗酸)は、排ガス処理用充填物11を通過する時に液
で中和されて吐出口18から排気される。
Therefore, the exhaust gas (hydrofluoric acid) introduced into the scrubber 10 through the pipe 14 is neutralized by the liquid when passing through the exhaust gas treatment filler 11, and is exhausted from the discharge port 18.

尚、上記実施例では、排ガスとして弗酸について説明し
たが、その他の酸系、アルカリ系、有機系、毒系であっ
ても良い。その場合には、排ガスが酸系の場合にはカセ
ーゾーダを注入し、排ガスがアルカリ系の場合には塩酸
を注入する。又、有害物質が混入している場合には、そ
れらに応じた薬品を添加して除去するようにする。
Although hydrofluoric acid was used as the exhaust gas in the above embodiment, it may be other acid type, alkali type, organic type, or poison type. In that case, when the exhaust gas is an acid type, a caustic soda is injected, and when the exhaust gas is an alkaline type, hydrochloric acid is injected. If harmful substances are mixed, remove them by adding chemicals suitable for them.

又、吸収液散布管15を介して循環される吸収液の中に
は、SSは殆どないが、カルシュウムが溶解しているの
で、ポンプ29は連続運転して炭酸カルシュウム等の沈積
を防止する。更に、スクラバー10内の排ガス処理用充填
物11と金属触媒12にも、炭酸カルシュウム等が沈積する
ので、定期滴に塩酸を注入して、炭酸カルシュウムの固
形物を塩化カルシュウムの液に変えて目詰まりを防止す
る。
In addition, although SS is almost absent in the absorption liquid circulated through the absorption liquid spray pipe 15, since calcium is dissolved, the pump 29 is continuously operated to prevent deposition of calcium carbonate or the like. Further, since calcium carbonate and the like are deposited also on the exhaust gas treatment filler 11 and the metal catalyst 12 in the scrubber 10, hydrochloric acid is injected into the regular drops to change the calcium carbonate solid matter into calcium chloride liquid. Prevent clogging.

〔発明の効果〕 以上のように本発明によれば、還元剤による過酸化水素
の分解プロセスが不要となる。フロックの流出が極めて
少なくなるので、良好な処理水が得られる。排ガス用ス
クラバーと兼用しているので、設備費及びスペースの面
で有利である。排ガス処理に使うカセーソーダ溶液によ
って弗素含有廃水の中和を為され、添加すべき水酸化カ
ルシュウムの量を削減できるので、維持費が安くなる。
排ガス処理のための循環液は、通常その循環量の1/5〜1
/10はオーバフローさせて廃水処理装置まで移送する必
要がない等の利点がある、
[Effects of the Invention] As described above, according to the present invention, the decomposition process of hydrogen peroxide by a reducing agent is not necessary. Outflow of flocs is extremely small, and good treated water is obtained. Since it is also used as an exhaust gas scrubber, it is advantageous in terms of equipment cost and space. Maintenance cost is reduced because fluorine-containing wastewater is neutralized by the caustic soda solution used for exhaust gas treatment, and the amount of calcium hydroxide to be added can be reduced.
Circulating liquid for exhaust gas treatment is usually 1/5 to 1 of the circulating amount.
/ 10 has the advantage that there is no need to overflow and transfer to the wastewater treatment equipment,

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

第1図は本発明の実施例を示す説明図、第2図は従来例
を示す説明図である。 10……スクラバー、11……排ガス処理用充填物、12……
金属触媒、13,15……散布管、14……管、16……廃水貯
溜槽、20……反応槽、23……加圧浮上槽、27……貯溜
槽、28……吸収液管路、29……循環ポンプ。
FIG. 1 is an explanatory view showing an embodiment of the present invention, and FIG. 2 is an explanatory view showing a conventional example. 10 …… Scrubber, 11 …… Exhaust gas treatment filler, 12 ……
Metal catalyst, 13,15 ... Spraying pipe, 14 ... Tube, 16 ... Waste water storage tank, 20 ... Reaction tank, 23 ... Pressure flotation tank, 27 ... Storage tank, 28 ... Absorption liquid pipeline , 29 …… Circulation pump.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/46 53/72 53/77 C02F 1/58 CDG B01D 53/34 120 D 120 A ZAB (72)発明者 若林 裕治 東京都中央区銀座8丁目21番1号 株式会 社竹中工務店東京本店内 (56)参考文献 特開 昭63−20094(JP,A)─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location B01D 53/46 53/72 53/77 C02F 1/58 CDG B01D 53/34 120 D 120 A ZAB ( 72) Inventor Yuji Wakabayashi 8-21-1, Ginza, Chuo-ku, Tokyo Incorporated Takenaka Corporation Tokyo Head Office (56) References JP-A-63-20094 (JP, A)

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】弗素,過酸化水素含有廃水と排ガスとを、
上部に排ガス処理用充填物を設け、下部に金属触媒を設
けたスクラバーに導入し、廃水を金属触媒に接触させて
過酸化水素を気泡化し、滴下する廃水に金属塩又は金属
化合物を添加して弗素化合物を生成した後、スクラバー
から排出して反応槽に於て高分子凝集剤を添加して弗素
化合物を凝集フロックとし、次いで加圧浮上槽の底部か
ら加圧水と共に流入させて固液を分離し、処理液の一部
をスクラバーの排ガス処理用充填物に散布しながら排ガ
スを通過させることを特徴とする弗素,過酸化水素含有
廃水及び排ガスの処理方法。
1. A wastewater containing fluorine and hydrogen peroxide and an exhaust gas,
Introduced into a scrubber with an exhaust gas treatment filler on the top and a metal catalyst on the bottom, contacting the waste water with the metal catalyst to bubble hydrogen peroxide and adding a metal salt or metal compound to the dropping waste water. After the fluorine compound is generated, it is discharged from the scrubber and the polymer flocculant is added in the reaction tank to make the fluorine compound into floc. Then, it is introduced together with pressurized water from the bottom of the pressure flotation tank to separate the solid-liquid. A method for treating wastewater containing fluorine and hydrogen peroxide, and an exhaust gas, wherein the exhaust gas is passed while spraying a part of the treatment liquid on a scrubber filler for exhaust gas treatment.
【請求項2】金属塩が、カルシュウム塩,鉄塩等である
ことを特徴とする特許請求の範囲第1項記載の弗素,過
酸化水素含有廃水及び排ガスの処理方法。
2. The method for treating waste gas containing fluorine and hydrogen peroxide and exhaust gas according to claim 1, wherein the metal salt is calcium salt, iron salt or the like.
【請求項3】金属化合物が、カルシュウム化合物,アル
ミニュウム化合物等であることを特徴とする特許請求の
範囲第1項記載の弗素,過酸化水素含有廃水及び排ガス
の処理方法。
3. The method for treating wastewater containing fluorine and hydrogen peroxide and exhaust gas according to claim 1, wherein the metal compound is a calcium compound, an aluminum compound or the like.
【請求項4】排ガスが、弗酸,塩酸,硝酸,硫酸等の酸
系ガス、アンモニアガス等のアルカリ系、アルコール,
現像液等の有機系、シラン,アルシン,ホスフィン等の
毒系等であることを特徴とする特許請求の範囲第1項記
載の弗素,過酸化水素含有廃水及び排ガスの処理方法。
4. Exhaust gas is acid-based gas such as hydrofluoric acid, hydrochloric acid, nitric acid, sulfuric acid, alkali-based gas such as ammonia gas, alcohol,
The method for treating fluorine-containing and hydrogen peroxide-containing wastewater and exhaust gas according to claim 1, which is an organic type such as a developing solution and a toxic type such as silane, arsine and phosphine.
【請求項5】上部に排ガス処理用充填物を設け、下部に
金属触媒を設け、排ガス処理用充填物と金属触媒との間
に弗素,過酸化水素含有廃水と排ガスとを各別に導入す
る流入管を設け、排ガス処理用充填物の上部に吸収液散
布用管を設け、金属触媒の下部に滴下する廃水に金属塩
又は金属化合物と反応させる廃水貯溜槽を形成したスク
ラバーと、このスクラバーと管路を介して連結し、高分
子凝集剤と廃水とを撹拌混合させる反応槽と、この反応
槽と管路を介して底部で連結し、上記管路に供給される
加圧水と共に廃水を流入させ凝集フロックを分離する加
圧浮上槽と、この加圧浮上槽から導出された処理水を貯
溜する貯溜槽と、この貯溜槽と排ガス処理用充填物の上
部に設けた吸収液散布用管とを連結し、ポンプによって
貯溜槽中の処理水と所望の中和剤とを送水する吸収液管
路とから構成されたことを特徴とする弗素,過酸化水素
含有廃水及び排ガスの処理装置。
5. An inflow for providing an exhaust gas treatment filler on the upper portion and a metal catalyst on the lower portion, and separately introducing waste water containing fluorine and hydrogen peroxide and exhaust gas between the exhaust gas treatment filler and the metal catalyst. A scrubber provided with a pipe, a pipe for spraying the absorbing liquid on the upper part of the exhaust gas treatment filler, and a wastewater storage tank for reacting the metal salt or the metal compound with the wastewater added to the bottom of the metal catalyst, and the scrubber and the pipe. A reaction tank that is connected via a channel to stir and mix the polymer flocculant and the waste water, and this reaction tank is connected at the bottom via a pipeline, and the waste water is introduced together with the pressurized water supplied to the pipeline and aggregated. The pressure flotation tank that separates the flocs, the storage tank that stores the treated water derived from this pressure flotation tank, and this storage tank and the absorption liquid spray pipe provided above the exhaust gas treatment filler are connected. Then, the treated water in the storage tank is pumped. Fluorine, characterized in that it is composed of the absorption liquid pipe for water and the desired neutralizing agent, the hydrogen peroxide-containing wastewater and exhaust gas processing apparatus.
JP61171027A 1986-07-21 1986-07-21 Method and apparatus for treating wastewater containing fluoric and hydrogen peroxide and exhaust gas Expired - Fee Related JPH0783819B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61171027A JPH0783819B2 (en) 1986-07-21 1986-07-21 Method and apparatus for treating wastewater containing fluoric and hydrogen peroxide and exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61171027A JPH0783819B2 (en) 1986-07-21 1986-07-21 Method and apparatus for treating wastewater containing fluoric and hydrogen peroxide and exhaust gas

Publications (2)

Publication Number Publication Date
JPS6328429A JPS6328429A (en) 1988-02-06
JPH0783819B2 true JPH0783819B2 (en) 1995-09-13

Family

ID=15915726

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61171027A Expired - Fee Related JPH0783819B2 (en) 1986-07-21 1986-07-21 Method and apparatus for treating wastewater containing fluoric and hydrogen peroxide and exhaust gas

Country Status (1)

Country Link
JP (1) JPH0783819B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11267677A (en) * 1998-03-24 1999-10-05 Sharp Corp Wastewater treatment device and wastewater treatment method
KR20180099430A (en) * 2017-02-28 2018-09-05 (주)윈윈 System and method for treating water from scrubber using filters

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Publication number Priority date Publication date Assignee Title
JP3192557B2 (en) * 1994-08-26 2001-07-30 シャープ株式会社 Wastewater treatment device and wastewater treatment method
JP4314739B2 (en) * 2000-11-24 2009-08-19 富士電機システムズ株式会社 Exhaust gas detoxification method and apparatus for semiconductor thin film manufacturing apparatus
JP5148372B2 (en) * 2008-05-29 2013-02-20 パナソニック株式会社 Method of circulating and using fluorine-containing wastewater and wastewater treatment equipment used therefor
CN118255445B (en) * 2024-04-25 2025-11-21 上海韵申微电子技术有限公司 Hydrogen peroxide wastewater treatment safety device

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11267677A (en) * 1998-03-24 1999-10-05 Sharp Corp Wastewater treatment device and wastewater treatment method
KR20180099430A (en) * 2017-02-28 2018-09-05 (주)윈윈 System and method for treating water from scrubber using filters

Also Published As

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