JPS5898124A - Ozone treating apparatus - Google Patents

Ozone treating apparatus

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Publication number
JPS5898124A
JPS5898124A JP56195053A JP19505381A JPS5898124A JP S5898124 A JPS5898124 A JP S5898124A JP 56195053 A JP56195053 A JP 56195053A JP 19505381 A JP19505381 A JP 19505381A JP S5898124 A JPS5898124 A JP S5898124A
Authority
JP
Japan
Prior art keywords
ozone
gas
tank
generator
treated
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.)
Pending
Application number
JP56195053A
Other languages
Japanese (ja)
Inventor
Takekuni Azuma
吾妻 健国
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.)
Mitsubishi Electric Corp
Original Assignee
Mitsubishi Electric 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 Mitsubishi Electric Corp filed Critical Mitsubishi Electric Corp
Priority to JP56195053A priority Critical patent/JPS5898124A/en
Publication of JPS5898124A publication Critical patent/JPS5898124A/en
Pending legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PURPOSE:To provide the titled apparatus capable of purifying water or an exhaust gas containing a dirty component of which the concn. is variable by a small scale O3- generator, constituted so as to supply a necessary amount of an ozonized gas generated in the O3-generator and once stored therein to an ozone reaction system. CONSTITUTION:An ozonized gas generated in an O3-generator is pressurized by a compressor 11 and once stored in an O3-tank 9. The ozonized gas stored in the tank 9 is supplied to a duct 3 through a flow controller 13 and mixed with a gas to be treated supplied from a direction as shown by an arrow 13. In this case, the concn. of O3 in the gas to be treated, the concn. of a reducing component, for example NOx in a waste gas and the concn. of NH3 in a malodorous gas from sewage are measured by a densitometer 14 and the controller 13 is operated so as to mix a necessary amount of O3 corresponding to the concns. with the gas to be treated. In addition, when the pressure of the ozonized gas in the tank 9 is raised to a definite upper limit value, a pressure switch 10 is operated to stop the O3-generator 2 and a gas pump 11 as well as to close a solenoid valve 12. On the other hand, the pressure of the ozonized gas in the tank 19 is lowered to a definite lower limit value, the switch 10 is again operated to start the generator 2 and the pump 11 as well as to open the valve 12.

Description

【発明の詳細な説明】 この発明はオゾンによシ液体まだはガスの浄化を行うオ
ゾン処理装置に関し、さらに詳しくはオゾン発生器で発
生しオゾン化ガスを一旦オゾンタンクニ貯蔵し、このオ
ゾンタンクから必要量のオゾンをオゾン反応系へ供給す
るようにしたオゾン処理装置に関するものである。
[Detailed Description of the Invention] This invention relates to an ozone treatment device that purifies liquid or gas by using ozone, and more specifically, the ozonized gas generated in an ozone generator is temporarily stored in an ozone tank, and the ozone gas is removed from the ozone tank when necessary. The present invention relates to an ozone treatment device that supplies a large amount of ozone to an ozone reaction system.

従来のオゾン処理装置としては第1図および第2図に示
すものがあった。第1図は従来のオゾン脱臭装置の一例
を示すフロー図であり、図において、(1)は被処理ガ
スを送る送風機、(2)はオゾンをシン配管、(5)は
オゾン反応部としての脱臭塔、(6)はこの脱臭塔内に
充填された充填剤である。なお、矢印Aはオゾン化ガス
、矢印Bは被処理ガス、矢印Cは処理ガスの流れ方向を
示す。
Conventional ozone treatment apparatuses include those shown in FIGS. 1 and 2. Figure 1 is a flow diagram showing an example of a conventional ozone deodorizing device. In the diagram, (1) is a blower for sending the gas to be treated, (2) is a thin pipe for ozone, and (5) is for an ozone reaction section. The deodorizing tower (6) is a filler filled in this deodorizing tower. Note that arrow A indicates the flow direction of the ozonized gas, arrow B indicates the gas to be processed, and arrow C indicates the flow direction of the processing gas.

次に動作について説明する。送風機(1)によって捕集
された処理ガス(矢印B)はオゾン量a\ら所定量のオ
ゾン化ガス(矢印A)を混合された後、脱臭塔(5)に
送られる。脱臭塔(5)には活性炭または重金属酸化物
などの酸化還元反応を促進する充填剤(6)が充填され
ており、この充填剤(6)と混合ガスが接触する間にオ
ゾン酸化反応が進行し、被処理ガス中の有害な還元性ガ
スが酸化分解される。
Next, the operation will be explained. The processing gas (arrow B) collected by the blower (1) is mixed with an amount of ozone a\ and a predetermined amount of ozonized gas (arrow A), and then sent to the deodorizing tower (5). The deodorizing tower (5) is filled with a filler (6) that promotes redox reactions such as activated carbon or heavy metal oxides, and the ozone oxidation reaction progresses while the mixed gas comes into contact with the filler (6). However, harmful reducing gases in the gas to be treated are oxidized and decomposed.

上記のように構成された従来のオゾン脱臭装置では、被
処理ガス中の還元性ガスの濃度が季節および時間によっ
て変動するので、オゾン発生器は還元性ガスの量が最大
になったときの容量のものでなけれはならなかった。し
かし、現実には、還元性ガス濃度の最大値と最小値とで
は桁違いに相違し、下水処理場から発生する着具したガ
ス中の値化水素の濃度を例にとると、最大値は0.1チ
以上、最小値はlppm以下で、104:1以上の比と
なる。従って必要とされるオゾン発生器の容量が大きく
なるという欠点があった。
In the conventional ozone deodorizing equipment configured as described above, the concentration of reducing gas in the gas to be treated fluctuates depending on the season and time, so the ozone generator has a capacity at which the amount of reducing gas reaches its maximum. It had to belong to. However, in reality, the maximum and minimum values of the reducing gas concentration are different by an order of magnitude. Taking the concentration of valorized hydrogen in the gas emitted from a sewage treatment plant as an example, the maximum value is The ratio is 0.1 or more, the minimum value is 1ppm or less, and the ratio is 104:1 or more. Therefore, there is a drawback that the required capacity of the ozone generator becomes large.

第2図は従来のオゾンによる水処理装置の一例を示すフ
ロー図であり、図において、(7)はオゾン反応部とし
てのオゾン反応塔、(8)はこのオゾン反応塔内に設置
された散気管であり、オゾン配管(4)に接続している
。■)はオゾン反応塔(力から排出されるオゾン化ガス
、Eは被処理水、Fは処理水の流れ方向を示す矢印であ
る。
Figure 2 is a flow diagram showing an example of a conventional ozone-based water treatment system. It is the trachea and is connected to the ozone pipe (4). ①) is the ozonized gas discharged from the ozone reaction tower (power), E is the water to be treated, and F is the arrow indicating the flow direction of the treated water.

上記のように構成された水処理装置においては、オゾン
反応塔(力の上部から導入された被処理水(矢印E)を
、散気管(8)から気泡状となって供給されるオゾン化
ガス(矢印人)で曝気し、被処理水中の還元性物質をオ
ゾンで酸化する。その結果として、被処理水は脱色、化
学的酸素要求i (COD)の低減または脱臭等の浄化
作用を受け、矢印F方向へ排出される。この水処理装置
においても、被処理水の処理に要求される最大必要オゾ
ン量に見合った容量のオゾン発生器(2)を設置する必
要があった。
In the water treatment equipment configured as described above, the water to be treated (arrow E) introduced from the upper part of the ozone reaction tower (power) is treated with ozonized gas supplied in the form of bubbles from the aeration pipe (8). (arrow) to oxidize reducing substances in the water to be treated with ozone.As a result, the water to be treated undergoes purification effects such as decolorization, reduction of chemical oxygen demand (COD), and deodorization. The water is discharged in the direction of arrow F. In this water treatment device as well, it was necessary to install an ozone generator (2) with a capacity commensurate with the maximum amount of ozone required for treatment of the water to be treated.

上述のように、従来のオゾン処理装置aにおいては、オ
ゾン発生器の容量は必要とされる最大のオゾン量に合わ
せて決められていたので、容量が大きくなり、オゾン発
生器の建設費およびランニングコストが萬価になるとい
う欠点があった。
As mentioned above, in the conventional ozone treatment equipment a, the capacity of the ozone generator was determined according to the maximum amount of ozone required, so the capacity became large and the construction costs and running costs of the ozone generator were reduced. The drawback was that the cost was prohibitive.

この発明は上記のような従来のものの欠点を除去するた
めになされたもので、オゾン発生器で発生したオゾン化
ガスを一旦オシンタンクに貯蔵した後、オゾン反応部で
必要とされるオゾン量を自動的にオゾンタンクから供給
するようにすることによって、一時的に要求される過大
量のオゾンの供給を可能とするとともに、オゾン発生器
の容量が過大になるのを防ぐことができるオゾン処理装
置を提供することを目的としている。
This invention was made in order to eliminate the drawbacks of the conventional ones as described above. After the ozonized gas generated by the ozone generator is stored in the ozone tank, the amount of ozone required in the ozone reaction section is automatically adjusted. By supplying ozone from an ozone tank, it is possible to temporarily supply an excessive amount of ozone and prevent the capacity of the ozone generator from becoming excessive. is intended to provide.

以下、本発明の一実施例を図について説明する。An embodiment of the present invention will be described below with reference to the drawings.

第3図は悪臭ガスの脱臭や排煙脱硝等のガスのオゾン処
理に適用した本発明の一実施例によるオゾン処理装置の
オゾン供給部の構成例を示すフロー図であり、図におい
て、第1図または第2図と同一符号は同一または相当部
分を示す。(9)はオゾン配管(4)の途中に設けられ
たオゾンタンク、10)はこのオゾンタンクに設けられ
た圧力スイッチ、(Illはオゾン発生器(2)からオ
ゾンタンク(9)にオゾン化ガスを送る気体ポンプ、0
りはオゾン配管(4)の途中に設けられた電磁弁、αり
はオゾンタンク(9)とダクト(3)の間に設けられた
流量調整器、αaはダクト(3)中の被処理ガス中の還
元性成分の濃度を計測する濃度計、0つは電気配線であ
る。
FIG. 3 is a flow diagram showing an example of the configuration of an ozone supply section of an ozone treatment apparatus according to an embodiment of the present invention applied to ozone treatment of gas such as deodorization of malodorous gas and denitrification of exhaust gas. The same reference numerals as those in the figures or FIG. 2 indicate the same or corresponding parts. (9) is an ozone tank installed in the middle of the ozone pipe (4), 10) is a pressure switch installed in this ozone tank, (Ill is an ozone gas supplied from the ozone generator (2) to the ozone tank (9) gas pump to send, 0
αa is the solenoid valve installed in the middle of the ozone pipe (4), αa is the flow regulator installed between the ozone tank (9) and the duct (3), and αa is the gas to be treated in the duct (3). A densitometer that measures the concentration of reducing components inside, 0 is electrical wiring.

次に動作について説明する。オゾン発生器(2)で発生
したオゾン化ガス(矢印A)は気体ポンプαυによって
加圧されて、一旦オシンタンク(9)に貯蔵される。オ
ゾンタンク(9)中のオゾン化ガスの圧力が一定の上限
値に上昇すると、圧力スイッチ(io)が動作して、オ
ゾン発生器(2)および気体ポンプQl)を停止させ、
電磁弁(121を閉じる。しかしオゾンタンク(9)中
のオゾン化ガスの圧力が一定の下限値にまで低下すると
、再び圧力スイッチα0)が動作して、オゾン発生器(
2)および気体ポンプo1)を起動させ、1JL!弁(
1りを開く。オゾンタンク(9)に貯蔵されたオゾン化
ガスは流量調整器0国を通ってダクト(3)に導入され
、被処理ガス(矢印B)と混合される。被処理ガス中の
オゾンと反応する還元性成分、例えば排煙中の酸化窒素
、下水臭気中のアンモニア等の濃度は濃度計(14)で
計測され、その濃度に対応した必要オゾン量が、濃度計
圓の出力信号によって被処理ガスに混合されるように、
流量調整器031が動作する。
Next, the operation will be explained. The ozonized gas (arrow A) generated by the ozone generator (2) is pressurized by the gas pump αυ and temporarily stored in the ozone tank (9). When the pressure of the ozonized gas in the ozone tank (9) rises to a certain upper limit, the pressure switch (io) operates to stop the ozone generator (2) and the gas pump Ql),
The solenoid valve (121) is closed. However, when the pressure of the ozonized gas in the ozone tank (9) decreases to a certain lower limit value, the pressure switch α0) operates again and the ozone generator (
2) and gas pump o1) are started, and 1JL! valve(
Open 1. The ozonized gas stored in the ozone tank (9) is introduced into the duct (3) through the flow regulator 0 and mixed with the gas to be treated (arrow B). The concentration of reducing components that react with ozone in the gas to be treated, such as nitrogen oxide in flue gas and ammonia in sewage odor, is measured with a concentration meter (14), and the required amount of ozone corresponding to the concentration is determined by the concentration. so that it is mixed into the gas to be treated by the output signal of the meter,
The flow rate regulator 031 operates.

本実施例において、被処理ガスのオゾン必要量が最大1
5 ppm、最小0.2 ppm 、日間平均3.5 
ppm 、破堤ガス量10,000 Nm”/時のとき
、オゾン発生器(2)のオゾン発生容量は75g/時と
すればよい。寸だ、オゾン濃度を201 / Nm@、
オゾンタンク(9)内のガス圧力をゲージ圧で5に9/
i とすれば、日間平均オソ;゛ン必要量の1/3をオ
ゾンタンク(9)に貯蔵するとして、オゾンタンク(9
)の容積は5n1″となる。これに比べて第1図の従来
装置では、必要オゾン発生容量は321.9/時になる
。従って本発明による実施例では、従来装置よりもオゾ
ン発生器の規模を1/4以下に低減することが可能であ
る。
In this example, the required amount of ozone in the gas to be treated is at most 1
5 ppm, minimum 0.2 ppm, daily average 3.5
ppm, when the levee breach gas amount is 10,000 Nm"/hour, the ozone generation capacity of the ozone generator (2) should be 75 g/hour. In short, the ozone concentration is 201/Nm@,
Change the gas pressure in the ozone tank (9) to 5 by gauge pressure 9/
i, then assuming that 1/3 of the daily average ozone requirement is stored in the ozone tank (9), the ozone tank (9)
) is 5n1''.In comparison, in the conventional apparatus shown in FIG. can be reduced to 1/4 or less.

なおオゾンタンク(9)の材質としては耐オゾン性があ
り、オゾン分解を起さず、光を遮断する不透明のもので
あればよく、ステンレス鋼製タンク、またはガラスや塩
化ビニル樹脂、フッ素Ill 脂、エポキシ樹脂、ポリ
エチレン樹脂等のオゾンと反応しない樹脂でオゾンとの
接触部が被覆された金属製タンクを用いる。オゾン配管
(4)、気体ポンプ01)、電磁弁(121、流量調整
器0り等も、接ガス部は同様な材質とする。
The ozone tank (9) may be made of any material that is ozone resistant, does not cause ozone decomposition, and is opaque and blocks light, such as a stainless steel tank, glass, vinyl chloride resin, fluorine resin, etc. A metal tank is used whose parts that come into contact with ozone are coated with a resin that does not react with ozone, such as epoxy resin or polyethylene resin. The ozone piping (4), the gas pump 01), the solenoid valve (121, the flow rate regulator 0, etc.) are made of the same material for the parts that come into contact with the gas.

第4図は上水用原水またはし尿2次処理水や生活排水等
の汚濁物質を含んだ排水のオゾン処理に適用した本発明
の他の実施例によるオゾン処理装置を示すフロー図であ
り、図において、第1図ないし第3図と同一符号は同一
まだは相当部分を示すが、オゾンタンク(9)はプラス
チック袋部で伸縮自在に形成され、濃度計Iはオゾン反
応塔(力から排出されるオゾン化ガス(矢印D)中の残
存オゾン濃度を検出し、可変速モータ付気体ポンプαυ
を制御するようになっている。
FIG. 4 is a flow diagram showing an ozone treatment apparatus according to another embodiment of the present invention applied to ozone treatment of wastewater containing pollutants such as raw water for drinking water, secondary treated human waste water, and domestic wastewater. The same reference numerals as in Figs. 1 to 3 indicate corresponding parts, but the ozone tank (9) is made of a plastic bag and is expandable and retractable, and the densitometer I is connected to the ozone reaction tower (which is discharged from the force). The remaining ozone concentration in the ozonized gas (arrow D) is detected, and the gas pump αυ with variable speed motor
is designed to be controlled.

」二記のように構成されたオゾン処理装置において、オ
ゾン化ガス(矢印A)は、一旦、プラスチック袋部のオ
ゾンタンク(9)に貯蔵される。オゾンタンク(9)中
に貯蔵されるオゾン化ガスの量は第3図で示しだ実施例
と同様に、圧力スイッチ00)によって制御される。し
かし本実施例ではオゾンタンク(9)内のオゾン化ガス
の量はオゾンタンク(9)の伸縮によって調整され、ガ
ス圧は大気圧より01〜02気圧高いだけの圧力に保た
れるので、オゾンタンク(9)へのオゾン化ガスの輸送
はオゾン発生器(2)から排出されるオゾン化ガスの圧
力で行われる。
In the ozone treatment apparatus configured as shown in Section 2, the ozonized gas (arrow A) is temporarily stored in the ozone tank (9) in the plastic bag section. The amount of ozonated gas stored in the ozone tank (9) is controlled by a pressure switch 00), similar to the embodiment shown in FIG. However, in this embodiment, the amount of ozonized gas in the ozone tank (9) is adjusted by expanding and contracting the ozone tank (9), and the gas pressure is maintained at a pressure of 01 to 02 atm higher than atmospheric pressure. The ozonized gas is transported to the tank (9) using the pressure of the ozonized gas discharged from the ozone generator (2).

オゾンタンク(9)に一旦貯蔵されたオ1.シン化ガス
は気体ポンプα1)によってオゾン反応塔(力に導入さ
れる。一方、オゾン反応塔(力には塔上部から被処理水
(矢印E)が導入され、塔内でオゾン化ガス(矢印A)
と気液接触し、汚濁成分をオゾン酸化により除去した後
、矢印F方向へ排出される。濃度計Iはオゾン反応塔(
力から排出されるオゾン化ガス(矢印D)中の残存オゾ
ン濃度を検出し、その濃度が一定値、例えば導入される
オゾン化ガス(矢印A)中の1/10程度となるように
、気体ポンプ旧)の動作を制御する9 本実施例によって被処理水中のnj+、硝酸イオン(N
O2′)を硝酸イオン(N O’i)に酸化する場合、
被処理水量が24ゴ/日、NO; 濃度が最大で2.O
17m”、最小で0.1J/rr?、日間平均0.6,
9/n?であるとき、オゾン発生器(2)の必要オゾン
発生容量は15Kp/時とすればよい。またオゾン濃度
を209/Nm”、オゾンタンク(9)内の圧力をゲ゛
−ジ圧で0.2に内 とすれば、日間平均オゾン必’L
ftの1/3をオゾンタンク(9)に貯蔵するとして、
オゾンタンク(9)の最大容積を6−とすればよい、こ
れに比べて、第2図の従来装置では必要オゾン容量は5
0y/時となる。従って、本実施例の方がオゾン発生器
(2)の規模が約1、/3.3になり、著しく小形化さ
れる。
O1 once stored in the ozone tank (9). The sintered gas is introduced into the ozone reaction tower (arrow E) by the gas pump α1). On the other hand, the water to be treated (arrow E) is introduced into the ozone reaction tower (arrow E) from the top of the tower, and the ozonized gas (arrow A)
After coming into gas-liquid contact with and removing pollutant components by ozone oxidation, it is discharged in the direction of arrow F. Concentration meter I is an ozone reaction tower (
The residual ozone concentration in the ozonized gas (arrow D) discharged from the engine is detected, and the gas is In this example, nj+ and nitrate ions (N
When oxidizing O2') to nitrate ion (N O'i),
The amount of water to be treated is 24 g/day, NO; the concentration is 2. O
17m”, minimum 0.1J/rr?, daily average 0.6,
9/n? In this case, the required ozone generation capacity of the ozone generator (2) may be 15 Kp/hour. Also, if the ozone concentration is 209/Nm" and the pressure in the ozone tank (9) is within 0.2 in terms of gauge pressure, the daily average ozone must be
Assuming that 1/3 of ft is stored in the ozone tank (9),
The maximum capacity of the ozone tank (9) can be set to 6 -.Compared to this, in the conventional device shown in Fig. 2, the required ozone capacity is 5 -.
0y/hour. Therefore, in this embodiment, the scale of the ozone generator (2) is approximately 1./3.3, which is significantly smaller.

この実施例において、オゾンタンク(9)の材質として
は耐オゾン性があり、オゾン分解を起さず、光icS断
する不透明な硬質の布状のものであればよく、フッ素樹
脂、軟質塩化ビニル樹脂、ポリエチレン樹脂等の布製袋
であればよい。
In this embodiment, the material of the ozone tank (9) may be any opaque hard cloth-like material that is ozone resistant, does not cause ozone decomposition, and blocks light from the icS, such as fluororesin, soft vinyl chloride, etc. Any cloth bag made of resin, polyethylene resin, etc. may be used.

なおオゾンタンクの構造、材質、あるいはオゾンタンク
からのオゾン化ガスの供給装置は上記実施例のものに限
定されず、変更することが可能である。
Note that the structure and material of the ozone tank, or the supply device for ozonized gas from the ozone tank are not limited to those of the above embodiments, and can be changed.

また上記実施例では、脱臭装置および水処理装置に適用
した場合について述べたが、本発明は、他のオゾン処理
装置にも同様に適用可能である。
Further, in the above embodiments, the case where the present invention is applied to a deodorizing device and a water treatment device has been described, but the present invention is similarly applicable to other ozone treatment devices.

以上のように、この発明によれば、オゾン化ガスを一旦
オシンタンクに貯蔵した後、必要量を供給してオゾン処
理するようにしたので、濃度の変動する汚濁成分を含ん
だ水や排ガスを規模の小さいオゾン発生器で浄化するこ
とができ、実用上の価値が太きい。
As described above, according to the present invention, after the ozonized gas is stored in the ocin tank, the necessary amount is supplied for ozonation treatment. It can be purified with a small ozone generator and has great practical value.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は従来のオゾン脱臭装置の一例を示すフロー図、
第2図は従来のオゾン水処理装置の一例を示すフロー図
、第3図はこの発明の一実施例による排ガスのオゾン処
理装置のオゾン供給部の構成例を示すフロー図、第4図
はこの発明の他の実施例による水のオゾン処理装置を示
すフロー図である。 図中、同一符号は同一またはイ1」当部分を示すものと
し、(1)は送風機、(2)はオゾン発生器、(3)は
ダクト、(,5)は脱臭塔、(力はオゾン反応塔、(9
)はオゾンタンク、(lO)は圧力スイッチ、αaは濃
度計である。 代理人 葛 野 信 −(外1名)
Figure 1 is a flow diagram showing an example of a conventional ozone deodorizing device.
FIG. 2 is a flow diagram showing an example of a conventional ozone water treatment device, FIG. 3 is a flow diagram showing an example of the configuration of an ozone supply section of an exhaust gas ozone treatment device according to an embodiment of the present invention, and FIG. FIG. 3 is a flow diagram showing a water ozone treatment apparatus according to another embodiment of the invention. In the diagram, the same reference numerals indicate the same parts or parts, (1) is the blower, (2) is the ozone generator, (3) is the duct, (,5) is the deodorizing tower, (power is the ozone generator, Reaction tower, (9
) is an ozone tank, (lO) is a pressure switch, and αa is a concentration meter. Agent Shin Kuzuno - (1 other person)

Claims (4)

【特許請求の範囲】[Claims] (1)オゾン発生器、このオゾン発生器で発生したオゾ
ン化気体を貯蔵するオゾンタンク、オゾン反応部、およ
びこのオゾン反応部で必要とされるオゾンを上記オゾン
タンクから供給する装置を備えたことを特徴とするオゾ
ン処理装置。
(1) Equipped with an ozone generator, an ozone tank for storing the ozonized gas generated by the ozone generator, an ozone reaction section, and a device for supplying the ozone required by the ozone reaction section from the ozone tank. An ozone treatment device featuring:
(2)オゾン処理に供される被処理水オたは被処理ガス
のオゾン必要量を自動的に検出する検出装置、およびそ
の検出値によってオゾンタンクから供給されるオゾン首
を自動調節する調整装置を備えたことを特徴とする特許
請求の範囲第1項記載のオゾン処理装置。
(2) A detection device that automatically detects the required amount of ozone in the water or gas to be treated that is subjected to ozone treatment, and an adjustment device that automatically adjusts the ozone level supplied from the ozone tank based on the detected value. An ozone treatment apparatus according to claim 1, characterized by comprising:
(3)オゾンタンクはステンレス鋼製タンク、またはガ
ラス、塩化ビニル樹脂、フッ素樹脂、エポキシ柾脂もし
くはポリエチレン樹脂で被覆された金属製タンクである
ことを特徴とする特許請求の範囲第1項捷たけ第2項記
載のオゾン処理装fl。
(3) The ozone tank is a stainless steel tank, or a metal tank coated with glass, vinyl chloride resin, fluororesin, epoxy resin, or polyethylene resin. Ozone treatment apparatus fl according to item 2.
(4)オゾンタンクはフッ素樹脂、軟質塩化ビニル樹脂
、ポリエチレン樹脂からなる布状容器を用いることを特
徴とする特許請求の範囲第1項または第2項記載のオゾ
ン処理装置。
(4) The ozone treatment apparatus according to claim 1 or 2, wherein the ozone tank is a cloth-like container made of fluororesin, soft vinyl chloride resin, or polyethylene resin.
JP56195053A 1981-12-03 1981-12-03 Ozone treating apparatus Pending JPS5898124A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56195053A JPS5898124A (en) 1981-12-03 1981-12-03 Ozone treating apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56195053A JPS5898124A (en) 1981-12-03 1981-12-03 Ozone treating apparatus

Publications (1)

Publication Number Publication Date
JPS5898124A true JPS5898124A (en) 1983-06-10

Family

ID=16334762

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56195053A Pending JPS5898124A (en) 1981-12-03 1981-12-03 Ozone treating apparatus

Country Status (1)

Country Link
JP (1) JPS5898124A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008136278A1 (en) * 2007-04-27 2008-11-13 Toyota Jidosha Kabushiki Kaisha O3 producing device, and exhaust cleaning system for internal combustion engine
JP2017522186A (en) * 2014-07-21 2017-08-10 中国科学院過程工程研究所 Semi-dry simultaneous desulfurization and denitration apparatus and method for sintered flue gas by circulating fluidized bed

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008136278A1 (en) * 2007-04-27 2008-11-13 Toyota Jidosha Kabushiki Kaisha O3 producing device, and exhaust cleaning system for internal combustion engine
US8266895B2 (en) 2007-04-27 2012-09-18 Toyota Jidosha Kabushiki Kaisha O3 production apparatus and exhaust gas purification system for internal combustion engine
JP2017522186A (en) * 2014-07-21 2017-08-10 中国科学院過程工程研究所 Semi-dry simultaneous desulfurization and denitration apparatus and method for sintered flue gas by circulating fluidized bed
US10137408B2 (en) 2014-07-21 2018-11-27 Institute Of Process Engineering, Chinese Academy Of Sciences Equipment and method for circulating fluidized bed semidry simultaneous desulfurization and denitration of sintering flue gas

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