JPS58143821A - Method for deodorizing malodorous gas - Google Patents

Method for deodorizing malodorous gas

Info

Publication number
JPS58143821A
JPS58143821A JP57025156A JP2515682A JPS58143821A JP S58143821 A JPS58143821 A JP S58143821A JP 57025156 A JP57025156 A JP 57025156A JP 2515682 A JP2515682 A JP 2515682A JP S58143821 A JPS58143821 A JP S58143821A
Authority
JP
Japan
Prior art keywords
deodorizing
washing liquid
liquid
concn
amount
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
Application number
JP57025156A
Other languages
Japanese (ja)
Other versions
JPS625009B2 (en
Inventor
Tomiyoshi Iwasaki
岩崎 臣良
Kakio Matsumura
松村 桓生
Seiji Aoki
青木 精二
Hiroo Yamada
山田 啓夫
Masanori Kimura
正憲 木村
Junji Hagiwara
萩原 純二
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.)
Fuso KK
Original Assignee
Fuso KK
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 Fuso KK filed Critical Fuso KK
Priority to JP57025156A priority Critical patent/JPS58143821A/en
Publication of JPS58143821A publication Critical patent/JPS58143821A/en
Publication of JPS625009B2 publication Critical patent/JPS625009B2/ja
Granted legal-status Critical Current

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Abstract

PURPOSE:To operate an apparatus smoothly and develop stable deodorizing effect, by holding the concn. of NaHCO3 and/or Na2CO3 in a basic NaClO washing liquid in an absorptive oxidation method to a predetermined value or less to control the amount of replenishing water. CONSTITUTION:In supplying a basic NaClO washing liquid 6 to a washing liquid tank 5, the concn. of NaHCO3 and/or Na2CO3 in the washing liquid 6 is measured by a carbonate densitometer 16. By this measured value, an electromotive valve 17 is controlled to adjust the replenishing amount of fresh water 8 so as to hold the concn. of the washing liquid in the tank 5 to 4,000ppm or less, especially, 1,500-3,000ppm. Thus adjusted washing liquid is injected from the liquid distributor 3 of a washing tower 1 to be contacted with a malodorous gas 13 such as H2S contg. accompanied CO2. As the result, H2S is converted to S or Na2SO4 to carry out deodorizing while CO2 is converted to a proper amount of carbonates in the aforementioned concn. and the adhesion of carbonates to the liquid contact part of a deodorizing apparatus is prevented to smoothly operate the apparatus.

Description

【発明の詳細な説明】 この発明は悪臭ガスの脱臭方法、さらに詳しくいうと次
亜塩素酸ナトリウムをアルカリ性洗浄液として用いる吸
収酸化方式(以下吸収酸化法という)による二酸化炭素
を随伴含有する悪臭ガスの脱臭方法に関する。なお、こ
こでいう悪臭ガスとは悪臭防止法や地方公害防止条例に
よる規制の対象となる工場や事業場の排出ガスをはじめ
、悪臭苦情の原因となっているガスをさす。
DETAILED DESCRIPTION OF THE INVENTION This invention relates to a method for deodorizing malodorous gas, and more specifically, to deodorizing malodorous gas containing carbon dioxide by an absorption oxidation method (hereinafter referred to as absorption oxidation method) using sodium hypochlorite as an alkaline cleaning liquid. Regarding deodorizing methods. Note that the term "foul-smelling gas" here refers to gases that are the cause of malodor complaints, including exhaust gases from factories and business establishments that are subject to regulations under the Offensive Odor Prevention Act and local pollution control ordinances.

次面堵累酸ナトリウムをアルカリ洗浄液として用いる吸
収酸化法による脱臭は下水終末処理場、し尿処理場、ご
み処理場などの公共環境施設における大規模脱臭に特に
多く採用されており、その概要を最も一般的な装置M構
成について添付の図面により説明する。
Deodorization by the absorption oxidation method, which uses sodium chloride as an alkaline cleaning solution, is particularly often used for large-scale deodorization in public environmental facilities such as sewage treatment plants, human waste treatment plants, and garbage treatment plants. A general configuration of the device M will be explained with reference to the attached drawings.

図において、1は充填塔形式の洗浄塔であり。In the figure, 1 is a cleaning tower in the form of a packed column.

これはデミスタ−2、液分配器3および充填物層4を具
えている。5は洗浄液槽であり、図には洗浄塔1と分離
したものが示されているが、洗浄塔の底部に一体に形成
されたものもある。
It comprises a demister 2, a liquid distributor 3 and a packing layer 4. Reference numeral 5 denotes a cleaning liquid tank, and although the figure shows one separated from the cleaning tower 1, there is also a tank that is integrally formed at the bottom of the cleaning tower.

筐だ複数の洗浄塔を一体化して隔壁で機能を分けた形式
のものもある。図中6は次曲塩素酸ナトリウム液貯槽、
7は水酸化ナトリウム液貯槽、8は送水管、9はpH指
示調節計、10は次lIE地素酸ナトリウムの濃度調節
を指示するだめの濃度計である。I 1.12は薬液注
入ポンプであり、いずれもitI記の計器と連動して(
対応するポンプと計器の連係を点線で示す)薬液を各貯
槽から洗浄液中に制御注入し、洗浄液のpi(値および
次p+<塩素酸ナトリウムの濃度を所定値に保っている
。悪臭ガス(経路を太い実線で示す)は、入口13から
洗浄塔1を通過する間に、洗浄液循環ポンプ14によっ
て液槽から塔上部へ循環し散布される洗浄液と接触して
脱臭され出口15から大気中に放出される。16は本発
明に関与する炭酸塩類濃度計であり、アルカリ性吸収液
中の炭酸水素す) IJウムおよび/または炭酸ナトリ
ウムの濃度を検出し、電動弁17に信号を送って開閉に
より送水管8から洗浄液槽に補給する水量を調節する。
There is also a type that integrates multiple cleaning towers into one body and separates their functions with partition walls. 6 in the figure is the sodium chlorate liquid storage tank,
7 is a sodium hydroxide liquid storage tank, 8 is a water pipe, 9 is a pH indicating controller, and 10 is a concentration meter for instructing the next IIE sodium hydroxide concentration adjustment. I 1.12 is a drug infusion pump, and both are linked with the instrument described in it I (
The chemical solution (corresponding pump and meter connections are shown by dotted lines) is injected into the cleaning solution from each storage tank in a controlled manner to maintain the cleaning solution's pi value and the concentration of sodium chlorate at a predetermined value. (indicated by a thick solid line) passes through the cleaning tower 1 from the inlet 13, comes into contact with the cleaning fluid that is circulated from the liquid tank to the top of the tower by the cleaning fluid circulation pump 14, and is sprayed, and is deodorized and released into the atmosphere from the outlet 15. 16 is a carbonate concentration meter related to the present invention, which detects the concentration of hydrogen carbonate and/or sodium carbonate in the alkaline absorption liquid, and sends a signal to the electric valve 17 to transmit the signal by opening and closing. The amount of water supplied from the water pipe 8 to the cleaning liquid tank is adjusted.

18は排水管で洗浄液の一部を溢流排出する。なお、実
装置では、酸洗浄や活性炭吸着といった他の方式と組み
合わせて装置を構成することもよく行われている。
18 is a drain pipe for overflowing and discharging a part of the cleaning liquid. In addition, in actual devices, devices are often configured in combination with other methods such as acid cleaning and activated carbon adsorption.

吸収酸化法の基本原理は次亜塩素酸す) IJウムの酸
化作用により悪臭ガス中の臭気成分に変化を与えて無臭
安定化させることである。例えば主要対象成分である硫
化水輪をアルカリ性ではfil〜(3)式に示す様に化
学的に安定な硫黄または硫酸ソーダに変化させる。
The basic principle of the absorption oxidation method is to change the odor components in malodorous gas and make it odorless and stable through the oxidizing action of IJium (hypochlorous acid). For example, water sulfide, which is the main target component, is changed into chemically stable sulfur or sodium sulfate in alkaline conditions as shown in formula (3).

H2S + 2 NaOH= Na2S +2 H2O
−−”・叩−−(11Na2S +NaCl0+HtO
= S+Nacl+2NaOH−−f21Na2S+4
NaCIO= Na、So、+4NaC7−・−・旧・
・f3J(1+と(3)の反応は同時に起り液のpHに
よってどちらかが主反応となる。洗浄液に新水を補給し
て液の一部を溢流させる目的は、 1)反応生成物(例えばNaC1)の液中#度が高くな
って液のガス吸収速度が低下し脱臭効率が落ちるのを防
止する。
H2S + 2 NaOH= Na2S + 2 H2O
--"・beat--(11Na2S +NaCl0+HtO
= S+Nacl+2NaOH--f21Na2S+4
NaCIO= Na, So, +4NaC7-・-・old・
・The reactions of f3J(1+ and (3) occur simultaneously, and one of them becomes the main reaction depending on the pH of the solution.The purpose of replenishing fresh water to the cleaning solution and overflowing a part of the solution is to: 1) Reaction products ( For example, this prevents the deodorizing efficiency from decreasing due to the high concentration of NaC1) in the liquid, which reduces the gas absorption rate of the liquid.

2)浮遊性または沈降性生成*C例えばSや後述の炭酸
塩)を流出させて、その伺着による装置運転トの障害を
防II:、する。
2) Floatable or sedimentary products such as S and carbonates described below) are allowed to flow out to prevent trouble in the operation of the equipment due to their arrival.

の2点であって、これにより装置は脱臭能力を継続保持
している。しかし補給する新水の量を制御する方法は、
これまでのところ確立していない。例えば、PPM19
81年7月号1頁〜13頁「し尿処理場の標準的脱臭設
備」及び同誌1981年8月号32頁〜39頁「特殊充
填物を使用した下水処理場およびポンプ場の脱臭装置」
に、吸収酸化法について記述されているが、補給水量に
ついてはなんら示されていない。既設装置における新水
の補給は、設置者の経験に基いだ捷ち捷ちの肴ややり方
で行われているのが実状である。ところで、補給水量が
多いと溢流にともなって排出される薬品の曖が多くなっ
て障害が起こる。特に次亜塩素酸ナトリウムは0.3p
pm程度で殺菌力があり、脱臭では100〜2000p
pmの濃度範囲で使用するので、脱臭装置排水として多
量を放流することは水中生物に悪影響を及ぼす。また経
街性の点でも無視できる量ではなく、例えば、補給水量
を一定(i o t 7m1n)にして実施例の条件で
装置tを3ケ月間連続した場合における次亜塩素酸す)
 IJウムの溢流による排出量は全消費瑚:の23%に
達した。
These two points allow the device to maintain its deodorizing ability. However, the method of controlling the amount of fresh water to be replenished is
Not established so far. For example, PPM19
July 1981 issue, pages 1-13, "Standard deodorizing equipment for human waste treatment plants" and August 1981 issue, pages 32-39, "Deodorizing equipment for sewage treatment plants and pumping stations using special fillings"
describes the absorption oxidation method, but does not provide any information on the amount of make-up water. The reality is that the supply of fresh water to existing equipment is carried out in a way that is based on the experience of the installer. By the way, if the amount of make-up water is large, the amount of chemicals discharged due to overflow will increase, causing problems. Especially sodium hypochlorite is 0.3p
It has sterilizing power at about pm, and deodorizes at 100 to 2000 p.m.
Since it is used within the concentration range of pm, discharging a large amount as deodorizing equipment wastewater will have an adverse effect on aquatic life. In addition, the amount of hypochlorous acid is not negligible from the point of view of economic efficiency.
Emissions from IJum overflow reached 23% of total consumption.

一方補給水肘が少い状況で二酸化炭素を含む悪臭ガスを
処理すれば、炭酸塩を主体とする沈殿物が生成し付着し
て、吸収液の循環路を閉塞する上に計装のセンサ一部を
汚して検出値に誤差を生じ、脱臭装置の機能低下を来た
す。pH計はもちろん、特に最近普及してきた次亜塩素
酸 5− ナトリウム濃度計にあってはift極法によるものと光
電光度法によるものとを問わず、付着物による接液部の
汚染が使用上の大きな妨害要因となっている。
On the other hand, if foul-smelling gas containing carbon dioxide is processed in a situation where there is little make-up water, precipitates mainly composed of carbonates will form and adhere, blocking the absorption liquid circulation path and damaging the instrumentation sensors. The deodorizer becomes dirty, causing an error in the detected value and deteriorating the function of the deodorizing device. Not only pH meters, but especially 5-sodium hypochlorite concentration meters that have recently become popular, contamination of the wetted parts by deposits is a problem, regardless of whether they use the ift electrode method or the photoelectric photometry method. This is a major hindrance factor.

本発明者は、この付着物の発生が洗浄液中の炭酸塩類の
濃度と関係があり、炭酸塩類の濃度を補給水の注入制御
指標にとれば、装置の脱臭効果をそこなうことなく新水
補給量を調節できることを見出して本発明を完成した。
The present inventor believes that the occurrence of this deposit is related to the concentration of carbonates in the cleaning liquid, and that if the concentration of carbonates is taken as an index for controlling the injection of make-up water, the amount of fresh water to be refilled can be achieved without impairing the deodorizing effect of the device. The present invention was completed by discovering that it is possible to adjust the

すなわち、本発明は、吸収酸化法による脱臭方式にあっ
てアルカリ性次炬塩素酸す) IJウム洗浄液中の炭酸
水素ナトリウムおよび/まだは炭酸ナトリウムの*iを
4000 ppm以下好ましくrl:1500〜300
0ppmに保つように、液に補給するW「水の量を制御
することを特徴とする、悪臭ガスの脱臭方法である。
That is, the present invention is a deodorizing method using an absorption oxidation method, in which the *i of sodium bicarbonate and/or sodium carbonate in the IJium cleaning solution is preferably 4000 ppm or less, preferably rl: 1500 to 300.
This method of deodorizing foul-smelling gas is characterized by controlling the amount of water added to the liquid so as to maintain it at 0 ppm.

洗浄液に補給する水の肴を減らして炭酸塩類の濃度が4
000 ppmを超えると、短時間の中に沈殿が生じて
脱臭装置の接液部に付着する。
Reduce the amount of water supplied to the cleaning solution to reduce the carbonate concentration to 4.
If it exceeds 000 ppm, precipitation will occur within a short period of time and will adhere to the wetted parts of the deodorizing device.

また水量を増して?#度を1500 ppm以下にす 
6− れば、装置から排出される次亜塩素酸ナトリウムの針が
不必要に増大して前述の不都合を生ずる。本発明により
、吸収酸化法脱臭装置に常に適量の新水を補給できるの
で、前記の障害は防除されて、装置はその排水が環境に
及ぼす影響の少い円滑な運転が11能となり、安定した
脱臭効果を得ることができる。本発明を実施するに当っ
て、炭酸水素ナトリウムや炭酸ナトリウムの濃ノ5.を
検出制御する方法は、どのような方法でもよいが1例え
ば検出にはウィンクラ−法を用いることができる。また
自動的に濃JJiを検出し開側1信号を出せる装置とし
てはDlgi Chem3000(湯浅アイオニクス株
式会社製)等を利用でさる。
Can you increase the amount of water again? # Reduce the concentration to 1500 ppm or less
6- Otherwise, the number of sodium hypochlorite needles discharged from the device will be increased unnecessarily, resulting in the above-mentioned disadvantages. According to the present invention, an appropriate amount of fresh water can always be supplied to the absorption oxidation deodorizing equipment, so the above-mentioned problems are eliminated, and the equipment can operate smoothly with less impact on the environment due to its wastewater, resulting in stable operation. A deodorizing effect can be obtained. In carrying out the present invention, 5. Although any method may be used to detect and control the detection, for example, the Winkler method may be used for detection. Further, as a device that automatically detects the concentrated JJi and outputs the open side 1 signal, Dlgi Chem3000 (manufactured by Yuasa Ionics Co., Ltd.) or the like may be used.

炭酸水素ナトリウムと炭酸ナトリウムは装置の処理対象
である悪臭ガスに含まれている二酸化炭素が、洗浄液中
の水酸化す) IJウム(pH調整のため注入)と反応
して生じたものである。
Sodium hydrogen carbonate and sodium carbonate are produced when carbon dioxide contained in the malodorous gas that is treated by the device reacts with hydroxide (injected to adjust pH) in the cleaning solution.

一般に悪臭ガスは、発生にあたって嫌気性醗酵が関与し
ていることが多く、大抵は二酸化炭素を含みしかもその
濃度は常に変動して°いる。したがって、悪臭ガスの脱
臭に炭酸塩の影響は避けられず本願発明はこれに対応で
さる有用な方法である。
In general, anaerobic fermentation is often involved in the generation of malodorous gases, and most of them contain carbon dioxide, whose concentration is constantly changing. Therefore, the influence of carbonates on the deodorization of malodorous gases is unavoidable, and the present invention is a useful method for dealing with this.

実  施  例 下水処理場の汚泥濃縮洗浄槽から245Nm/minの
風歌で誘引した悪臭ガスを充填塔型式(2000φX5
200H,充填高さ1.9m、充填材トリカルノξツキ
ンP−164)の洗浄塔から成る脱臭装置により、洗浄
液の次亜塩素酸す) IJウムI#反100ppm 、
 pH10,液ガス比2kg/kgの条件で処理したと
ころ、洗浄液中の炭酸塩の![:(ウィンクラ−伝によ
るNa2CO3とNaHCO3の11k度)が3000
 ppmを超えると付着性の沈殿を生じ、4000 p
pmに達すると短時間の内に次能塩素計が使用不能とな
った。その時の補給水量は3〜5//minであった。
Example: A packed tower type (2000φX5
A deodorizing device consisting of a cleaning tower of 200H, filling height 1.9m, and packing material Tricarno ξtsukin P-164) removes 100 ppm of hypochlorous acid from the cleaning solution.
When treated under the conditions of pH 10 and liquid/gas ratio of 2 kg/kg, carbonate in the cleaning solution was... [: (11k degree of Na2CO3 and NaHCO3 according to Winkler biography) is 3000
Above 4000 ppm, a sticky precipitate will form.
Once it reached pm, the secondary chlorine meter became unusable within a short time. The amount of replenishing water at that time was 3 to 5 min.

また炭酸塩の濃j度を3000pprn以下に保つと付
着性の沈殿は起らなかった(補給水着7〜101/rn
ln)。なお、硫化水素の除去率(は悪臭ガス中のra
+z約1〜4ppmに対し装置通過による除去率は99
5%以上であった。
Furthermore, when the concentration of carbonate was kept below 3000 pprn, no adhesive precipitation occurred (replenishment swimwear 7-101/rn
ln). In addition, the removal rate of hydrogen sulfide (ra
The removal rate by passing through the device is 99 for +z approximately 1 to 4 ppm.
It was 5% or more.

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

図面は本発明実施装置の櫃略図である。 1・・・洗浄塔、2・・デミスタ−13・・液分配器、
4・・充填吻鳴、5・・・洗浄液槽、6・・次亜埴素酸
ナトリウム液貯槽、7・・水酸化ナトリウム液貯槽、8
・・送水管、9・・・pH指示調節計、10・・・次亜
塩素酸す) IJウム#度計、11.12・・・液薬注
入ポンプ、I3・・悪臭ガス入口、14・・洗浄液循環
Iンプ、15・・・脱臭ガス出口、16・・・炭酸塩類
濃度計、17・・電動弁18・・・排  水  管  9−
The drawing is a schematic diagram of an apparatus for implementing the present invention. 1... Washing tower, 2... Demister-13... Liquid distributor,
4. Filling snort, 5. Cleaning liquid tank, 6. Sodium hypovolite liquid storage tank, 7. Sodium hydroxide liquid storage tank, 8
... Water pipe, 9 ... pH indicator controller, 10 ... Hypochlorous acid (IJ) meter, 11.12 ... Liquid medicine injection pump, I3 ... Malodorous gas inlet, 14.・Cleaning liquid circulation I pump, 15...Deodorizing gas outlet, 16...Carbonate concentration meter, 17...Electric valve 18...Drain pipe 9-

Claims (1)

【特許請求の範囲】[Claims] 1、次亜塩素酸す) IJウムをアルカリ性洗浄液とし
て用いて吸収酸化方式により二酸化炭素を随伴含有する
悪臭ガスを脱臭する方法において、前記洗浄液中の炭酸
水素ナトリウムおよび/または炭酸ナトリウムの濃at
ヲ4000ppm具下に保つように洗浄液への新水の補
給水量を制御することを特徴とする脱臭方法。
1. Hypochlorous acid) In a method of deodorizing a malodorous gas containing accompanying carbon dioxide by an absorption oxidation method using IJium as an alkaline cleaning solution, the concentration of sodium bicarbonate and/or sodium carbonate in the cleaning solution is
A deodorizing method characterized by controlling the amount of fresh water added to the cleaning solution so as to keep the concentration below 4000 ppm.
JP57025156A 1982-02-18 1982-02-18 Method for deodorizing malodorous gas Granted JPS58143821A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57025156A JPS58143821A (en) 1982-02-18 1982-02-18 Method for deodorizing malodorous gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57025156A JPS58143821A (en) 1982-02-18 1982-02-18 Method for deodorizing malodorous gas

Publications (2)

Publication Number Publication Date
JPS58143821A true JPS58143821A (en) 1983-08-26
JPS625009B2 JPS625009B2 (en) 1987-02-03

Family

ID=12158152

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57025156A Granted JPS58143821A (en) 1982-02-18 1982-02-18 Method for deodorizing malodorous gas

Country Status (1)

Country Link
JP (1) JPS58143821A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020137986A1 (en) * 2018-12-26 2020-07-02 株式会社下瀬微生物研究所 Deodorization device in treatment apparatus for organic matter-containing substance to be treated, and deodorization method for deodorization device

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53144879A (en) * 1977-05-24 1978-12-16 Sanei Seisakusho Kk Exhaust gas treatment apparatus
JPS54125171A (en) * 1978-03-24 1979-09-28 Asahi Glass Co Ltd Deodorizing method for exhaust gas or drain liquid
JPS5586522A (en) * 1978-12-26 1980-06-30 Tokuyama Soda Co Ltd Desulfurization of exhaust gas

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53144879A (en) * 1977-05-24 1978-12-16 Sanei Seisakusho Kk Exhaust gas treatment apparatus
JPS54125171A (en) * 1978-03-24 1979-09-28 Asahi Glass Co Ltd Deodorizing method for exhaust gas or drain liquid
JPS5586522A (en) * 1978-12-26 1980-06-30 Tokuyama Soda Co Ltd Desulfurization of exhaust gas

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020137986A1 (en) * 2018-12-26 2020-07-02 株式会社下瀬微生物研究所 Deodorization device in treatment apparatus for organic matter-containing substance to be treated, and deodorization method for deodorization device

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JPS625009B2 (en) 1987-02-03

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