JPS6129613A - Method of burning and deodorizing waste gas - Google Patents

Method of burning and deodorizing waste gas

Info

Publication number
JPS6129613A
JPS6129613A JP59150101A JP15010184A JPS6129613A JP S6129613 A JPS6129613 A JP S6129613A JP 59150101 A JP59150101 A JP 59150101A JP 15010184 A JP15010184 A JP 15010184A JP S6129613 A JPS6129613 A JP S6129613A
Authority
JP
Japan
Prior art keywords
waste gas
tar
gas
water
combustion
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
JP59150101A
Other languages
Japanese (ja)
Inventor
Tatsuji Nomura
野村 達治
Toshimasa Umehara
梅原 敏正
Yoshihiro Takahashi
高橋 由宏
Makoto Yamamoto
真 山本
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.)
Hitachi Kasei Setsubi Kensetsu KK
Resonac Corp
Original Assignee
Hitachi Chemical Co Ltd
Hitachi Kasei Setsubi Kensetsu 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 Hitachi Chemical Co Ltd, Hitachi Kasei Setsubi Kensetsu KK filed Critical Hitachi Chemical Co Ltd
Priority to JP59150101A priority Critical patent/JPS6129613A/en
Publication of JPS6129613A publication Critical patent/JPS6129613A/en
Pending legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Treating Waste Gases (AREA)

Abstract

PURPOSE:To remove gas tar material and eliminate an explosion potential by a method wherein waste gas is injected onto the waste gas between the facility for generating waste gas and a combustion and deodorizing furnace. CONSTITUTION:Waste gas is guided into the lower part of a cylindrical water injection device 1 and in a direction of tangential line under an operation of a discharging fan 9, and discharged from the top end of the water injection device 1 while being lifted along the inner wall of the cylinder in a spiral form. The waste gas is contacted with water injected from the injection nozzle 2 arranged at the top end of the water injection device 1 while being guided in a spiral form, thereby gas-like tar contained in the waste gas becomes a liquid tar 3 and settled at the bottom part 4 of a circulating tank 4. With this arrangement, the gas-like tar in the waste gas is removed and thus it is possible to remove an explosive potential such as a source of ignition and film detonation.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 不発明は樹脂製造工程あるいに樹脂加工工程等から発生
′f6可燃性廃ガスの燃焼脱臭処理方法に関するもので
ある0 〔従来技術〕 可燃性別ガスの脱果処理とし1%最近に最も処理効率の
筒い燃焼力式がとられている。
[Detailed Description of the Invention] [Industrial Application Field] The invention relates to a method for combustion deodorization of `f6 combustible waste gas generated from resin manufacturing processes, resin processing processes, etc.0 [Prior Art] Combustible Recently, the cylinder combustion power method, which has the highest processing efficiency of 1%, has been adopted for the removal of sex gases.

この燃焼方式は、処理対象が可燃性ガスであることから
爆発の危険があるため種々の安全対策が施されている。
This combustion method involves the risk of explosion since the target to be treated is flammable gas, so various safety measures are taken.

この安全対策の1つとして、燃焼炉〃)ら火焔が逆火し
ダクト及び製造設備の曝発火災?防止するために燃焼炉
と製造設備と【連結するダクト内に逆火防止装置を設置
する方法がある。
One of the safety measures is to prevent flames from the combustion furnace from backfiring and causing fires in the ducts and manufacturing equipment. To prevent this, one method is to install a flashback prevention device in the duct that connects the combustion furnace and manufacturing equipment.

従来け、廃ガス盆発生する製造設備とこの廃ガスン処理
する燃焼炉と才連結するダクト内に消火剤(ハロン13
01等)が光横された消火装置7設け、火焔が逆火し火
焔が伝播した場会、このときの偏度あるいは圧力で検知
し、ある設定温度あるいけ設定圧力以上になると消火装
置が破裂し、消火剤が噴きされ、火焔伝播娑阻止する刀
弐〒採用していた。しかしながら、こうした方式だと爆
轟といった非常に速い火焔伝播(マツハ5〜6)に対し
ては、温度あるいに圧力を検知してから消火剤が噴きさ
れても火焔伝播を阻止できない可能性がある。
Conventionally, fire extinguishing agent (Halon 13
A fire extinguishing system 7 is equipped with a light source (such as 01) installed, and when the flame backfires and the flame propagates, it is detected by the deviation or pressure at this time, and if the temperature exceeds a certain set temperature or pressure, the fire extinguishing system will explode. Fire extinguishing agent was then sprayed, and a sword was used to prevent the spread of the flames. However, with this method, there is a possibility that the flame propagation cannot be stopped in the case of extremely fast flame propagation (Matsuha 5-6) such as detonation, even if the extinguishing agent is sprayed after detecting the temperature or pressure. be.

〔発明の目的〕[Purpose of the invention]

不発明にこうした従来の火焔伝播r阻止できない可能性
【な(すためのものである。
This is to avoid the possibility that conventional flame propagation cannot be prevented.

1友、廃ガス中にガス状の樹脂(通称タール以下タール
とする)が含1れている場合、このタールがタクト内に
付着し、冷却されると固化する1こめ、ダクトオ閉塞す
るだけでl(このタールは絶縁物であるため帯電し、着
火源(静電気による放電着火)となり、さらに燃焼源と
もなり爆発ポテンシャルとなる0この配管内にタールが
蓄積し、これが着火源と接することで燃焼、爆轟ン起す
、ンイルム・テトネーションという現象げ最近研究され
けじめ、実際にこうした可燃物(潤滑油)の蓄積による
爆発事故例がいくつか報告されている。不発明に、この
ようなタール娑除去するものでもある。
1) If the waste gas contains gaseous resin (commonly referred to as tar), this tar will adhere to the inside of the duct and solidify when cooled, causing the duct to become clogged. l (Since this tar is an insulator, it becomes electrically charged and becomes an ignition source (discharge ignition due to static electricity), which also becomes a combustion source and has explosive potential.0 Tar accumulates in this pipe and comes into contact with an ignition source. The phenomenon of tetonation, which causes combustion and detonation, has recently been studied, and several cases of explosion accidents caused by the accumulation of combustibles (lubricating oil) have been reported. It also removes tar.

〔発明の構成〕[Structure of the invention]

不発明に可燃性ガスで含む廃ガスを廃ガス発生設備〃)
ら燃焼脱臭炉へ供給して燃現脱臭する方法において、廃
ガス発生設備と燃焼脱臭炉の間で廃ガスに水葡噴射させ
るようにしたことτ特徴とするもので、以下′;$、発
明娑図■に従って説明する〇 第1図は水だけで循環、噴射し1で水噴射装置τ含む塗
工機廃ガス燃焼脱臭処理の20−シートτ示す〇 第2図U’[Iff環ポンプ配管中にアルキロ−ルアC
H2GHz OH1 ミド°型界面活性剤(R−CON〈。H2of(2oH
7オ注入し、水噴射したときり塗工機廃ガス燃焼脱臭処
理の20−シートで示す0第6図には水噴射装置の平面
図7示す0− ゞ −゛本発明では、“まずアイルム・
デトネーション及び着火源となりつる蒸気状のタール娑
除云するために、塗工機等から発生する可燃性ガス〒含
む廃ガスン水咳射装置1に導入し、廃ガスに噴射@2か
ら水ケ噴射させ、#、状のタール6として、循環槽4円
に沈降させ、キャーポンプ5等により、該沈降タールを
系外に排出する。水の噴射に循環ポンプ6により行われ
、水噴射装置1の出口ガスに水分が持ち去られるために
、水供給用のボールタップ装置7が取っ付けられている
。この水噴射装置の出口ガス中にげ、蒸気状のタールに
含まれない。また、rL秋タール3の取り出しン容易に
する1ζめ(タールのV5度τ下ける)に、循環ポンプ
5と唄射器2の間の配管内にアルキロールアミド型界面
活性剤′f注入すると効果的である。また該水噴射装置
は塗工機の溌ガス出口及び脱臭炉別ガス入口の2ケ酒に
塩9付けることが好ましい。
Waste gas generation equipment that uninventively generates waste gas containing flammable gas
In a method for deodorizing combustion gas by supplying it to a combustion deodorizing furnace, the waste gas is injected with water grapes between the waste gas generation equipment and the combustion deodorizing furnace. 〇 Figure 1 shows the 20-sheet τ of the coating machine waste gas combustion deodorization treatment that uses only water for circulation and injection, and includes the water injection device τ 〇 Figure 2 U' [If Alkilolua C inside
H2GHz OH1 Mid° type surfactant (R-CON〈H2of(2oH
7. When the water is injected and water is injected, the coating machine waste gas combustion deodorizing treatment is shown in 20 sheets.・
In order to remove vine vapor-like tar that becomes a source of detonation and ignition, combustible gas generated from coating machines etc. The tar is injected and settled in a circulation tank 4 as #-shaped tar 6, and the settled tar is discharged out of the system by a car pump 5 or the like. Water injection is carried out by a circulation pump 6, and a ball tap device 7 for water supply is installed so that the water is carried away by the outlet gas of the water injection device 1. It is released into the outlet gas of this water injection device and is not included in the vaporized tar. In addition, injecting an alkylolamide type surfactant 'f into the piping between the circulation pump 5 and the syringe 2 at the 1ζ stage (lowering the V5 degree τ of the tar) to make it easier to take out the rL autumn tar 3. Effective. Further, it is preferable that the water injection device applies salt 9 to two locations, one at the spray gas outlet of the coating machine and the other gas inlet of the deodorizing furnace.

火炎伝播阻止という目的からは、噴射される循環水量と
廃ガスの液/ガス比(モル比)に7以上が好1しく噴射
方法も第6図に見られるように噴射ノズルを数列、数行
取V付け、噴射域〒重ね合わせることが好寸しい。
For the purpose of preventing flame propagation, it is preferable that the amount of circulating water to be injected and the liquid/gas ratio (mole ratio) of waste gas be 7 or more, and the injection method is to arrange the injection nozzles in several rows or rows as shown in Figure 6. It is best to overlap the V mounting and injection areas.

逆火し、燃焼、爆轟に移ると火炎と同時に急激な圧力が
発生する。このため単なる噴霧ではこの圧力によジ吹き
飛ばされる可能性がアさい。
When it backfires, burns, and detonates, a sudden burst of pressure is generated along with the flame. For this reason, there is a high possibility that simple spraying will be blown away by this pressure.

従って、噴鋪γ行うときには、上記圧力の放散口で設は
圧力を放散させなければならない。
Therefore, when spraying, the pressure must be dissipated through the pressure dissipation port.

四側δの序言・(内容に変更なし) 高圧噴射にすれば上記圧力でも吹き飛ばされず、火炎は
阻止できる。ただし、噴射帯の間隙をなくす必要がある
。この間隙をなくせば、火炎は不連続になるため確実に
火炎の伝播はなくなる。
Preface to the fourth side δ (No changes to the content) If high-pressure injection is used, it will not be blown away even at the above pressure, and flames can be prevented. However, it is necessary to eliminate gaps in the injection zone. If this gap is eliminated, the flame will become discontinuous, and flame propagation will definitely be eliminated.

水だけで噴射、循環させる水噴射装置及び循環槽を含む
屏ガス燃焼脱臭処理フローシート第1図の実施例につい
て説明する。
An embodiment of the folding gas combustion deodorizing process flow sheet shown in FIG. 1, which includes a water injection device that injects and circulates only water and a circulation tank, will be described.

〔実施例1〕 表1 廃ガスの成分と濃度 *:ガス状タール濃度単位 はrrIg/kgである。[Example 1] Table 1 Components and concentration of waste gas *: Gaseous tar concentration unit is rrIg/kg.

表1に示す成分と濃度を有する廃ガスが塗工機からガス
風量300 Nrn’/1nin、温度120℃で排出
される。該廃ガスは排気ンアン9により円筒状の水嘱射
装置1の下部及び円筒の接吻カ向に導入され、円筒の内
壁tらせん状に上昇しながら、水噴射装置1の頂部力)
ら接線力向に排出される。該廃ガスけらせん状で上昇す
る過程で、7に噴射装置1の頂部に設けられた吹射ノズ
ル271’ら噴射された水と接触することにより、廃ガ
ス中に含まれるガス状のタールが液状タール6と’z!
ll循環偕4の底部に沈降する。噴射ノズル2刀1ら噴
射される水に循環槽4でa秋タール6と分離された上澄
ケ漱7澹環ポンプ6で供給したものである。
Waste gas having the components and concentrations shown in Table 1 is discharged from the coating machine at a gas flow rate of 300 Nrn'/1 nin and a temperature of 120°C. The waste gas is introduced into the lower part of the cylindrical water injection device 1 and the kissing direction of the cylinder by the exhaust hole 9, and as it rises spirally on the inner wall of the cylinder, the top force of the water injection device 1 is increased.
It is discharged in the direction of tangential force. During the spiral upward movement of the waste gas, the gaseous tar contained in the waste gas comes into contact with water injected from the spray nozzle 271' provided at the top of the injection device 1 at 7. Liquid tar 6 and 'z!
It settles to the bottom of the 11 circulation. The water injected from the two injection nozzles 1 is separated from the tar 6 in a circulation tank 4, and is supplied by a pump 6.

ガス風量300 Nm7m1nのとさ、循環水量t1、
2 m’/min (循環水量1.2 m”/ min
 = 67 kg−mol/minガスに量300 N
m7m1n= 13.4kg mo I/minから液
/ガス比5表2参照)とすると、出口タール濃度σs、
 (S mg/kgとlクタ〜ル除去率は、280−5
.6/2.80X100二98%となる。噴射圧力は5
kg/an’である。
Gas air volume 300 Nm7m1n, circulating water volume t1,
2 m'/min (Circulating water amount 1.2 m'/min
= 67 kg-mol/min gas with a quantity of 300 N
If m7m1n = 13.4kg mo I/min, liquid/gas ratio 5 (see Table 2), the outlet tar concentration σs,
(S mg/kg and l-lactal removal rate are 280-5
.. 6/2.80X100298%. Injection pressure is 5
kg/an'.

循環水量才笈化させπと@(欧/ガス比を笈明細し′■
t’fI仕〜(内容に変更なし)化させたとき)のター
ル除去率と出口タール濃度を表2に示す。
The amount of circulating water is calculated and π and @ (Europe/Gas ratio is specified)
Table 2 shows the tar removal rate and outlet tar concentration of t'fI (no change in content).

表2 液/ガス比(モル比)とタール除去率、出口ター
ル濃度 循環水温度は64℃、水噴射装置1の頂部から排出され
るガス温度は37℃となった。塗工機8と水噴射装置1
とをつなぐダクトは、熱風により加熱16されている。
Table 2 Liquid/Gas Ratio (Molar Ratio), Tar Removal Rate, and Outlet Tar Concentration The temperature of the circulating water was 64°C, and the temperature of the gas discharged from the top of the water injection device 1 was 37°C. Coating machine 8 and water injection device 1
The duct connecting the two is heated 16 with hot air.

噴射ノズル2から噴射さitた水と接触した廃ガスは水
を同伴するため、循環槽4内の水量が減少する。
The waste gas that comes into contact with the water injected from the injection nozzle 2 carries water with it, so that the amount of water in the circulation tank 4 decreases.

このため、循環槽4には、水自動供給用のぎ−ルターグ
装置7が取っ付けられている。
For this reason, the circulation tank 4 is equipped with a water tag device 7 for automatic water supply.

廃ガス量600 Nm7m1nのとさ、循環槽内4の酸
受水量に23m’/日であった。
The amount of waste gas was 600 Nm7mln, and the amount of acid water received in the circulation tank 4 was 23m'/day.

また、循環槽4は、液状タール6盆分離するために2僧
に仕切られ、−力の槽に沈降した液状タール6けギヤー
ポンプ5により糸外に排出さn、上澄液に他力の槽へ溢
流し循環ポンプ6によジ馳射ノズル2に送られゐ。
In addition, the circulation tank 4 is divided into 2 parts to separate 6 basins of liquid tar, and the liquid tar settled in the tank is discharged to the outside by a gear pump 5 with 6 tanks, and the supernatant liquid is transferred to the tank of other power. It overflows into the air and is sent to the spray nozzle 2 by the circulation pump 6.

液状タール3に、水温37℃で4.QQQ〜5゜000
CPL/)粘度であるため非常に排出しにぐい。
Add liquid tar 3 to 4 at a water temperature of 37°C. QQQ~5゜000
CPL/) Because of its viscosity, it is very difficult to discharge.

このため、循環水配管内にアルキロールアミド型界面活
性剤(RCON < CHzCHzOH) 、注入CH
2CH20H すると、敵性タールが軟化し、排出しやすぐなる(鵠2
図)。
For this reason, an alkylolamide type surfactant (RCON < CHzCHzOH), injection CH
2CH20H Then, the enemy tar will soften and be discharged easily (Mouse 2
figure).

廃ガス中のタール除去率280111g/kgK対シテ
循環水中の界面活性剤濃度が約60 [11g/kg(
#)になるように界面活性剤r証刀I]すると(界面活
性剤濃度/クヘル濃度−02)タール粘度は、2゜5 
Q OCPに低下する。
The tar removal rate in the waste gas is 280111g/kgK vs. the surfactant concentration in the shite circulating water is approximately 60 [11g/kg (
#) Then, the tar viscosity is 2゜5.
Q Decrease in OCP.

さらに界面活性剤濃度を増加させてい(と、タール粘度
に1,0OOCP以下に低下した。
Furthermore, when the surfactant concentration was increased, the tar viscosity decreased to below 1.0 OOCP.

噴射装置ケ通過した出口ガス中には水滴が同伴されるた
めエリミネータ−18で除去され。
Since water droplets are entrained in the outlet gas that has passed through the injector, they are removed by the eliminator 18.

水滴は循環槽4へ戻される。エリミネータ−18才通過
した湿式廃ガスげ送気ンアン19により燃焼炉1Qの出
口にある熱又換器へ送らnゐこの湿式廃ガスに熱又換器
により400℃に温度上昇してから、燃焼炉へ送ら扛、
火焔と接触し燃籏脱果される。こりときの、燃焼温度け
800°Cである。この筒淵燃焼ガスは前述の熱父?A
器11廃熱回収装置12、さらに煙突へと導かれる。廃
P回収装置12における蒸気回収量は1.7t/Hr煙
突へ排気されるガス温度は200°Cであった。
The water droplets are returned to the circulation tank 4. The wet waste gas that has passed through the eliminator is sent to the heat exchanger at the outlet of the combustion furnace 1Q by the air supply unit 19.The temperature of this wet waste gas is raised to 400°C by the heat exchanger, and then it is combusted. sent to the furnace,
When it comes into contact with the flames, it is decomposed. At the time of burning, the combustion temperature was 800°C. Is this Tsutsubuchi combustion gas the aforementioned heat source? A
The waste heat is guided to the vessel 11, the waste heat recovery device 12, and then to the chimney. The amount of steam recovered in the waste P recovery device 12 was 1.7 t/hr, and the temperature of the gas exhausted to the chimney was 200°C.

〔発明の効果〕〔Effect of the invention〕

不発明によれば、 1、廃ガス発生設備あるいに廃ガス燃焼炉から逆火によ
る燃焼あるいに爆鞠があっても、水噴射ノズルからの水
噴射膜により、燃焼及び2、廃ガス娑水噴射ノズルから
の噴射水と接触させることにより、廃ガス中のガス状タ
ールが98%以上除去され、着火源及びフィルム・テト
ネーションといった爆発ポテンシャルを除(ことができ
る。
According to the invention, 1. Even if there is combustion or explosion due to backfire from the waste gas generation equipment or waste gas combustion furnace, the water jet film from the water jet nozzle will cause the combustion and 2. By contacting with water jetted from the water injection nozzle, more than 98% of the gaseous tar in the waste gas is removed, and explosive potential such as ignition sources and film tetonation can be eliminated.

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

第1図、第2図は不発明の燃焼脱臭処理の20−シート
で示す。第6図に水噴射装置の平面図である。 符号の説明 1 水噴射装置    2 噴射ノズル6 液状タール
    4 循環槽 5 ギヤーポンプ   6 循環ポンプ7  ボールタ
ップ装置   8 塗工機9 排気ファン    10
  燃焼炉11  熱交換器     12  別事回
収装置15  界面活性剤タンク  16 P風加熱部
21  廃ガス排出口 手続補正書(方式)
1 and 2 are 20-sheet illustrations of the inventive combustion deodorizing process. FIG. 6 is a plan view of the water injection device. Explanation of symbols 1 Water injection device 2 Injection nozzle 6 Liquid tar 4 Circulation tank 5 Gear pump 6 Circulation pump 7 Ball tap device 8 Coating machine 9 Exhaust fan 10
Combustion furnace 11 Heat exchanger 12 Separate recovery device 15 Surfactant tank 16 P-air heating section 21 Waste gas outlet procedure amendment (method)

Claims (1)

【特許請求の範囲】 1、可燃性ガスを含む廃ガスを廃ガス発生設備から燃焼
脱臭炉へ供給して燃焼脱臭する方法において、廃ガス発
生設備と燃焼脱臭炉の間で廃ガスに水を噴射させるよう
にしたことを特徴とする廃ガスの燃焼脱臭方法。 2、アルキロールアミド型界面活性剤を含有した水を噴
射させる特許請求の範囲第1項記載の廃ガスの燃焼脱臭
方法。
[Scope of Claims] 1. In a method of supplying waste gas containing flammable gas from waste gas generation equipment to a combustion deodorizing furnace to perform combustion deodorization, water is added to the waste gas between the waste gas generation equipment and the combustion deodorization furnace. A method for combustion deodorization of waste gas, characterized in that it is injected. 2. A combustion deodorizing method for waste gas according to claim 1, which comprises injecting water containing an alkylolamide type surfactant.
JP59150101A 1984-07-19 1984-07-19 Method of burning and deodorizing waste gas Pending JPS6129613A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59150101A JPS6129613A (en) 1984-07-19 1984-07-19 Method of burning and deodorizing waste gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59150101A JPS6129613A (en) 1984-07-19 1984-07-19 Method of burning and deodorizing waste gas

Publications (1)

Publication Number Publication Date
JPS6129613A true JPS6129613A (en) 1986-02-10

Family

ID=15489525

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59150101A Pending JPS6129613A (en) 1984-07-19 1984-07-19 Method of burning and deodorizing waste gas

Country Status (1)

Country Link
JP (1) JPS6129613A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010042342A (en) * 2008-08-12 2010-02-25 Kubota Kankyo Service Kk Device and method for treating evacuated vapor containing exhaust gas and organic waste treatment system

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5121570A (en) * 1974-08-16 1976-02-20 Sharp Kk Haigasuno shorisochi
JPS5248941A (en) * 1975-10-16 1977-04-19 Matsushita Electric Ind Co Ltd Subtraction circuit
JPS5624022A (en) * 1979-08-03 1981-03-07 Mitsubishi Rayon Co Ltd Treatment of tar containing exhaust gas

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5121570A (en) * 1974-08-16 1976-02-20 Sharp Kk Haigasuno shorisochi
JPS5248941A (en) * 1975-10-16 1977-04-19 Matsushita Electric Ind Co Ltd Subtraction circuit
JPS5624022A (en) * 1979-08-03 1981-03-07 Mitsubishi Rayon Co Ltd Treatment of tar containing exhaust gas

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010042342A (en) * 2008-08-12 2010-02-25 Kubota Kankyo Service Kk Device and method for treating evacuated vapor containing exhaust gas and organic waste treatment system

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