JPS6022967B2 - Deodorization treatment method for odor gas - Google Patents
Deodorization treatment method for odor gasInfo
- Publication number
- JPS6022967B2 JPS6022967B2 JP54129433A JP12943379A JPS6022967B2 JP S6022967 B2 JPS6022967 B2 JP S6022967B2 JP 54129433 A JP54129433 A JP 54129433A JP 12943379 A JP12943379 A JP 12943379A JP S6022967 B2 JPS6022967 B2 JP S6022967B2
- Authority
- JP
- Japan
- Prior art keywords
- gas
- temperature
- heat exchanger
- low
- odor
- 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
Links
- 238000000034 method Methods 0.000 title claims description 28
- 238000004332 deodorization Methods 0.000 title claims description 8
- 239000007789 gas Substances 0.000 claims description 106
- 230000001877 deodorizing effect Effects 0.000 claims description 24
- 239000003595 mist Substances 0.000 claims description 16
- 230000003197 catalytic effect Effects 0.000 claims description 9
- 238000010438 heat treatment Methods 0.000 claims description 8
- 230000003647 oxidation Effects 0.000 claims description 7
- 238000007254 oxidation reaction Methods 0.000 claims description 7
- 239000002912 waste gas Substances 0.000 claims description 6
- 238000009841 combustion method Methods 0.000 claims description 5
- 230000015572 biosynthetic process Effects 0.000 claims description 3
- 238000006555 catalytic reaction Methods 0.000 claims description 3
- WKBOTKDWSSQWDR-UHFFFAOYSA-N Bromine atom Chemical compound [Br] WKBOTKDWSSQWDR-UHFFFAOYSA-N 0.000 claims 1
- GDTBXPJZTBHREO-UHFFFAOYSA-N bromine Substances BrBr GDTBXPJZTBHREO-UHFFFAOYSA-N 0.000 claims 1
- 229910052794 bromium Inorganic materials 0.000 claims 1
- 235000019645 odor Nutrition 0.000 description 34
- 239000003054 catalyst Substances 0.000 description 9
- 238000002485 combustion reaction Methods 0.000 description 9
- 239000003517 fume Substances 0.000 description 6
- 238000010422 painting Methods 0.000 description 6
- 238000007639 printing Methods 0.000 description 6
- 238000012546 transfer Methods 0.000 description 6
- 239000002918 waste heat Substances 0.000 description 6
- 230000000694 effects Effects 0.000 description 5
- 239000003960 organic solvent Substances 0.000 description 5
- 238000011084 recovery Methods 0.000 description 5
- 239000000446 fuel Substances 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- 238000007796 conventional method Methods 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 239000002537 cosmetic Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 206010037660 Pyrexia Diseases 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- -1 canned goods Substances 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 238000007791 dehumidification Methods 0.000 description 1
- 238000007865 diluting Methods 0.000 description 1
- 238000005485 electric heating Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 125000002485 formyl group Chemical class [H]C(*)=O 0.000 description 1
- 235000011389 fruit/vegetable juice Nutrition 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 239000000383 hazardous chemical Substances 0.000 description 1
- 239000000543 intermediate Substances 0.000 description 1
- 239000013067 intermediate product Substances 0.000 description 1
- 239000003350 kerosene Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000007257 malfunction Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 235000014593 oils and fats Nutrition 0.000 description 1
- 238000006864 oxidative decomposition reaction Methods 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 239000011269 tar Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
Landscapes
- Incineration Of Waste (AREA)
- Treating Waste Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Description
【発明の詳細な説明】
この発明は、複数の臭気ガス発生源または排出口をもつ
系における凝縮・粘着性臭気ガスおよび低温度、鍵凝縮
・粘着性臭気ガスを、その臭気ガスの特性と高温側熱交
換器および低温側熱交換器の機能特性とを合理的に粗合
せて、有効に廃熱回収しながら脱臭処理する方法に関す
るものである。DETAILED DESCRIPTION OF THE INVENTION The present invention provides a method for controlling condensed and sticky odorous gases and low-temperature, key condensed and sticky odorous gases in a system with multiple odorous gas generation sources or outlets. The present invention relates to a method for deodorizing while effectively recovering waste heat by rationally and roughly matching the functional characteristics of a side heat exchanger and a low-temperature side heat exchanger.
有機溶剤を多用する自動車の車体、弱電気製品の容器な
らびに缶詰、化粧缶等の塗装、焼付工程あるいは印刷工
程において排出されるガスは、各種炭火水素、アルデヒ
ド系中間生成物、タール状ヒューム等のガス成分を多く
含み、そのガスは複数個所の発生源または排出口から排
出される。The gases emitted during the painting, baking, or printing processes for automobile bodies, containers for weak electrical products, canned goods, cosmetic cans, etc., which use a large amount of organic solvents, contain various hydrocarbons, aldehyde intermediates, tar-like fumes, etc. It contains a large amount of gas components, and the gas is discharged from multiple sources or outlets.
前記ガス成分は、有害物質規制の対象となるものや光化
学スモッグの原因となる、ものもあり、かつ悪臭を伴な
うものである。また前記ガスは、その物理的性状からみ
て、凝縮・粘着性の、タールヒューム等を含むガス系か
ら比較的湿度の低いタールあるいは油脂系を含まないガ
ス系までの種々な系に分類されている。Some of the gas components are subject to hazardous substance regulations, some cause photochemical smog, and some are accompanied by bad odors. In addition, the above gases are classified into various types based on their physical properties, from gases that are condensed and sticky and include tar fume, etc. to gases that have relatively low humidity and do not contain tar or oils and fats. .
従来、これらのガスを処理するに際し、大風量、低温、
低湿度の、ガスは、、フィルター等により前処理された
のち、活性炭による吸着装置で処理されているが、それ
以外の既述した各系からの排ガスは集合ダクトで一括し
て臭気ガスフアンを経て臭気ガス予熱熱交換器を経て直
接燃焼装置あるいは触媒脱臭装置で処理されるのが一般
的である。最近、省エネルギ対策として、フィルター等
でミスト、粉塵を緒集したのち、触媒脱臭装置で処理す
る傾向になっている。Traditionally, when processing these gases, large air volumes, low temperatures,
Low-humidity gas is pretreated with a filter, etc., and then treated with an adsorption device using activated carbon, but the exhaust gases from the other systems mentioned above are collected in a collective duct and passed through an odor gas fan. Generally, the odor gas is treated with a direct combustion device or a catalytic deodorization device via a preheating heat exchanger. Recently, as an energy-saving measure, there has been a trend to collect mist and dust using filters, etc., and then dispose of the mist and dust using catalyst deodorizing equipment.
しかしこれ等何れの方式を用いても、各系の臭気ガスを
合流させることにより、温度低下に伴うミスト化、ある
いは単独処理のタール状ヒュームを含む系のガスは、脱
臭処理する以前に、前処理フィルターを汚損して圧力損
失を高め、臭気ファンの駆動部分に付着して、回転のア
ンバランスを生じ、さらに臭気ガス子熱熱交換器に付着
物を形成して、伝熱面の機能を低下させると共に、ガス
通過抵抗を増大させ、プラントの運転および停止の繰返
し1こより、前記付着物が酸化または劣化して雰囲気温
度160〜190℃付近で発火しやすい危険物質を生成
させる要因をつくることが多く、過去に熱交換器の焼損
、ダクト系からプロセス源への類焼事故等をひき起した
事例があり、このため前処理の重要性が強調されている
。これらの対策について、本発明者は、複数の臭気ガス
発生源をもつ系における臭気ガスを、接触酸化法まなた
は直接燃焼法により脱臭処理するに際し「凝縮・粘着性
臭気ガスをミスト補集後に接触酸化法または直接燃焼法
により脱臭処理し、この脱臭処理のとき発生する高温廃
ガスの熱を生産系が必要とする熱媒体に転換させ、さら
にその廃ガスの熱により低温・低温度臭気ガスを子熱し
、その予熱された臭気ガスを、バーナーの燃焼用空気と
して使用すると共に、前記凝縮・粘着性臭気ガスに合流
させて、温ならびに相対湿度を低下させることによりミ
ストを抑制することを特徴とする臭気ガスの脱臭処理方
法を提案したく特磯昭54−115756号(特関昭5
6−40021号公報)参照)。However, no matter which method is used, by merging the odor gases of each system, the gases of the system that turn into mist as the temperature decreases or that contain tar-like fumes that are treated alone can be removed before being deodorized. It fouls the treatment filter and increases pressure loss, it adheres to the drive part of the odor fan, causing unbalanced rotation, and it also forms deposits on the odor gas heat exchanger, impairing the function of the heat transfer surface. At the same time, the gas passing resistance is increased, and due to repeated operation and shutdown of the plant, the deposits are oxidized or deteriorated, creating a factor that generates dangerous substances that are likely to ignite at ambient temperatures of around 160 to 190 degrees Celsius. There have been many cases in the past where heat exchangers were burnt out and fires were caused from duct systems to process sources, etc. Therefore, the importance of pretreatment is emphasized. Regarding these countermeasures, the present inventor proposed that when deodorizing odor gas in a system with multiple odor gas generation sources by catalytic oxidation or direct combustion, Deodorizing treatment is carried out by catalytic oxidation method or direct combustion method, and the heat of high temperature waste gas generated during this deodorization treatment is converted into a heat medium required by the production system, and the heat of the waste gas is used to generate low temperature and low temperature odor gas. The preheated odorous gas is used as combustion air for the burner, and is combined with the condensed and sticky odorous gas to reduce the temperature and relative humidity, thereby suppressing mist. We would like to propose a deodorizing treatment method for odorous gases.
6-40021)).
しかるに、この臭気ガスの脱臭処理方法は、プラント全
体から、みて廃熱利用上、臭気発生源のプロセスへ回収
熱量の大半を返還する場合において有効な手段であるが
、プラントの形態によっては、廃熱回収の利用手段をそ
の発生源のプロセスが殆んど必要としない場合もある。
特に有機溶剤系の臭気ガス発生源では、、プラントの特
性、設備改善費等から廃熱熱利用手段は少なく、したが
って臭気予熟々交換器によって、廃熱回収を計かり燃料
の節減を行わざるを得ない。However, this method of deodorizing odorous gas is an effective means for returning most of the recovered heat from the plant as a whole to the process that generates the odor in terms of waste heat utilization. In some cases, the source process requires little use of heat recovery.
Particularly for organic solvent-based sources of odor gas, there are few methods of utilizing waste heat due to plant characteristics, equipment improvement costs, etc. Therefore, it is necessary to recover waste heat and save fuel using an odor pre-determined exchanger. I don't get it.
かかる場合、凝縮・粘着性ガスを含むミスト化しやすい
ガスは、その熱交換器の低温入口側の伝熱面にミストを
付着させ、酸化または劣化した低級カーボンを形成する
。In such a case, gases that easily form into mist, including condensed and sticky gases, adhere to the heat transfer surface on the low-temperature inlet side of the heat exchanger, forming oxidized or degraded lower carbon.
特に臭気ガス量の負荷低下あるいは冬期屋外ダクトの壁
面温度低下時に顕著となる。This is particularly noticeable when the load on the amount of odor gas decreases or when the wall temperature of the outdoor duct decreases in winter.
このようなトラブルを回避するため、熱交換器の熱回収
効率を決めるとき、最も重要なことは、臭気ガスを導入
する低温側熱交換器の伝熱面におけるメタル温度を常時
そのガスの霧点温度以上に保持することが必要である。To avoid such troubles, when determining the heat recovery efficiency of a heat exchanger, the most important thing is to always adjust the metal temperature on the heat transfer surface of the low-temperature side heat exchanger into which the odor gas is introduced to the fog point of the gas. It is necessary to maintain the temperature above that temperature.
したがって、前記入口臭気ガス温度と前記熱交換器の出
口廃ガス温度は密接な関係をもつため、熱交換器の温度
効率はみずから制約をうけることとなる。一般に、前記
のような凝縮・粘着性ガスの場合、低温伝熱温度は15
000以上が望ましく、そのために熱交換器出口廃ガス
温度は通常200〜250qo以上が必要である。Therefore, since the inlet odor gas temperature and the outlet waste gas temperature of the heat exchanger have a close relationship, the temperature efficiency of the heat exchanger is itself subject to restrictions. Generally, in the case of condensed and sticky gases as mentioned above, the low temperature heat transfer temperature is 15
000 or more is desirable, and therefore the heat exchanger outlet waste gas temperature usually needs to be 200 to 250 qo or more.
この発明は、前述の問題を有利に解決した臭気ガスの脱
臭処理方法を提供することを目的とするものである。An object of the present invention is to provide a method for deodorizing odor gas that advantageously solves the above-mentioned problems.
次にこの発明を図によって詳細に説明する。Next, this invention will be explained in detail with reference to the drawings.
第1図は、缶詰、ジュース等の化粧缶を製造する塗装あ
るいはプリント印刷および凝付工程から発生する有機溶
剤系ヒュームの有害悪臭ガスを触媒脱臭装置で処理する
に際し、臭気の性状に応じて、高・低温二系列の臭気ガ
ス予熱々交換器に導入し、同時に脱臭処理するプロセス
系統を示すものである。前記設備において発生する臭気
ガスの特性を大別すると、塗装あるいはプリント印刷用
焼付オーブン3で発生するガスは、その系にバーナ加熱
装置4、ガス循環ファンF4をもつために、有機溶剤系
ヒューム以外に炭化水素系中間生成物、タール系ヒュー
ムを多量に含有し、通常約100〜150℃の範囲に霧
点をもつ凝縮・粘着性臭気ガスであり、循環ファンF4
の出口側からその一部がダクト5に排出される。Figure 1 shows that when using a catalytic deodorizing device to treat harmful foul-smelling gases from organic solvent-based fumes generated from the painting, printing, and condensation processes used to manufacture cosmetic cans for cans, juice, etc., This shows a process system in which odor gas is introduced into two high- and low-temperature preheating exchangers and deodorized at the same time. Roughly classifying the characteristics of the odor gases generated in the above equipment, the gases generated in the baking oven 3 for painting or printing are other than organic solvent fumes because the system includes a burner heating device 4 and a gas circulation fan F4. It is a condensed and sticky odor gas that contains large amounts of hydrocarbon intermediate products and tar-based fumes, and has a fog point usually in the range of about 100 to 150°C.
A part of it is discharged into the duct 5 from the outlet side.
また塗装あるいは印刷装置6と晩付オーブン3の入口と
の間のガスは、有機溶剤の自然蒸発工程と前記焼付オー
ブンをェアカーテン等でシールすることにより発生する
臭気ガスであるため、フ−ド7から排出されるガスは、
低温・低湿度・低濃度ガスめである。Furthermore, the gas between the painting or printing device 6 and the inlet of the late baking oven 3 is an odor gas generated by the natural evaporation process of the organic solvent and the sealing of the baking oven with an air curtain or the like. The gas emitted from
Low temperature, low humidity, and low concentration gas.
また製品の冷却工程8は暁付オープン出口側のェアシー
ルを兼ねるため、低温度・低濃度の乾燥性ガスであり、
フード9から排出されて前記フード7からのガスと共に
ダクト101こ集合される。In addition, the cooling process 8 of the product also serves as an air seal on the Akatsuki open exit side, so the drying gas is low temperature and low concentration.
The gas is discharged from the hood 9 and collected together with the gas from the hood 7 in the duct 101.
ダクト10内の約20qoの低温・低温度ガスは、臭気
ガスファンF2を経由して低温側熱交換器2で予熱され
、約19800の過熱乾燥性ガスとなってダクト1 1
を経て前記ダクト5内の約13000の凝縮・粘着性ガ
スと合流し、約155qoでかつ結霧性ガスを稀釈する
ために、そのガスのミスト化を防止し、比較的低い相対
湿度となってダクト12を経て前処理フィルター13に
導入される。この手段により、従来結霧性ガスに対して
、昇温あるいはミスト除去することにより、効果を得よ
うとした方法とは異なり、従来の温度上昇効果のみによ
る結霧防止ではなく、乾燥過熱臭気ガスの混合により凝
縮・粘着性ガスを希釈しながら昇温する相乗効果によっ
て、結霧防止に顕著な効果がある。The low temperature gas of about 20 qo in the duct 10 is preheated by the low temperature side heat exchanger 2 via the odor gas fan F2, and becomes superheated dry gas of about 19,800 qo and is sent to the duct 1 1
It merges with the condensed and sticky gas of about 13,000 in the duct 5, and in order to dilute the atomizing gas and prevent the gas from becoming a mist, it becomes a relatively low relative humidity. It is introduced into a pretreatment filter 13 via a duct 12. Unlike conventional methods that attempted to achieve the effect of fogging gas by increasing the temperature or removing mist, this method does not prevent fogging only by the conventional temperature raising effect, but rather prevents fogging by drying superheated odor gas. The synergistic effect of increasing the temperature while diluting the condensed and sticky gas by mixing them has a remarkable effect on preventing fogging.
前記のような性状のガスが前処理フィルター13に導入
されるため、ミスト付着は著しくあ減少され、したがっ
てそのフィルターの機構を単純化し圧損の低減を計るそ
とができる。Since the gas having the above-mentioned properties is introduced into the pretreatment filter 13, mist adhesion is significantly reduced, and the filter mechanism can therefore be simplified to reduce pressure loss.
まなた前処理フィルター13から高温側熱交換器1にガ
スを送る脱臭ファンF,の回転部分にミストが付着する
のを防止するので、アンバランス運転も防止される。さ
らに高温側熱交換器1に導入されたガスは、その低温側
伝熱面のメタル平均温度または対数平均温度を最低約1
5000以上になるよう計画しているため、タールミス
トによる付着物の形成は生じない。Moreover, since mist is prevented from adhering to the rotating part of the deodorizing fan F, which sends gas from the pretreatment filter 13 to the high temperature side heat exchanger 1, unbalanced operation is also prevented. Furthermore, the gas introduced into the high-temperature side heat exchanger 1 has a metal average temperature or a logarithmic average temperature of the low-temperature side heat transfer surface at least about 1
Since it is planned to be 5,000 or more, no deposits will be formed due to tar mist.
高温側熱交換器1により予熱された臭気ガスは約31が
0となって触媒脱臭装置1 4に導入され、その触媒脱
臭装置14における子熱室15内でバーナ16により約
400q0に加熱されて活性化される。The odor gas preheated by the high-temperature side heat exchanger 1 is introduced into the catalyst deodorizing device 14 at a temperature of about 31 to 0, and is heated to about 400q0 by the burner 16 in the subheating chamber 15 of the catalyst deodorizing device 14. activated.
従来、バーナの燃焼用空気としては、導入ガスの性状の
問題がある関係で、大気を吸引していたが、この発明の
システムにおいては、低温側熱交換器2から出る約1班
℃の臭気ガスをダクト17およびファンF3によりバー
ナ16に送って燃焼用空気として利用するので、燃料の
低減に寄与する。Conventionally, atmospheric air was sucked in as the combustion air for the burner due to problems with the properties of the introduced gas, but in the system of the present invention, the odor of approximately 1 ℃ temperature emitted from the low-temperature side heat exchanger 2 is removed. Since the gas is sent to the burner 16 through the duct 17 and the fan F3 and used as combustion air, it contributes to a reduction in fuel consumption.
前記子熱室16内で約40000に子熱されたガスはし
触媒層18内で触媒反応により接触酸化し脱臭されて、
約40000(臭気ガスの酸化分解による反応熱で若干
の昇温がある)のクリーンガスとなり、このガスは高温
側熱交換器1に入り、ここでそのガスの熱が臭気ガスに
熱吸収されて約25000になったのち、低温側熱交換
器2に入り、ここで低温度系ガスに熱吸収されて約18
0℃に下がり、次いで排気筒19を経て大気に放出され
る。The gas heated to about 40,000 ℃ in the heating chamber 16 is catalytically oxidized and deodorized by a catalytic reaction in the catalyst layer 18,
The gas becomes a clean gas with a temperature of about 40,000 g (slight temperature rise due to reaction heat due to oxidative decomposition of the odorous gas), and this gas enters the high temperature side heat exchanger 1, where the heat of the gas is absorbed by the odorous gas. After the temperature reaches about 25,000, it enters the low-temperature side heat exchanger 2, where the heat is absorbed by the low-temperature gas and the temperature reaches about 18
The temperature drops to 0° C., and then it is released into the atmosphere through the exhaust stack 19.
低温側熱交換器2は臭気ガス特性とその温度から最も低
価格の敏鋼材製でよく、機構的にも加熱側と被加熱側の
通過ガス量の重量比はほぼ100対40であるので、被
加熱側の昇温率が高く、他方のガスとの減湿効果を高め
る。また低温度で低温側熱交換器2に導入できるため、
その器内の最高と最低の温度中を大きくとることができ
、そのため廃熱回収効率を高くすることが極めて容易に
なる。したがって、従来は前記のような混合ガスを脱臭
処理する場合の排気筒19内の排ガス温度を約200〜
250qo以内にすることは危険であったが、この発明
では経済的な熱交換器の伝熱面積が安全かつ容易に得ら
れ、さらに低温側熱交換器内の圧力損失を低くすること
ができるためにシステム圧力損失は、熱回収効率のわり
に低くすることができ、たとえ排気筒19内の温度が約
150℃になっても、保守、管理上の煩雑あるいは危険
性は生じなくなる。The low-temperature side heat exchanger 2 may be made of the lowest-priced steel material due to its odor gas characteristics and its temperature, and mechanically, the weight ratio of the amount of passing gas on the heating side and the heated side is approximately 100:40. The temperature increase rate on the heated side is high, increasing the dehumidification effect with the other gas. In addition, since it can be introduced into the low temperature side heat exchanger 2 at a low temperature,
The difference between the highest and lowest temperatures inside the vessel can be increased, making it extremely easy to increase waste heat recovery efficiency. Therefore, conventionally, when deodorizing the mixed gas as described above, the temperature of the exhaust gas in the exhaust stack 19 has been set at about 200-200°C.
It was dangerous to set it within 250 qo, but with this invention, an economical heat transfer area of the heat exchanger can be obtained safely and easily, and the pressure loss in the low temperature side heat exchanger can be lowered. In addition, the system pressure drop can be kept low relative to the heat recovery efficiency, and even if the temperature inside the exhaust stack 19 reaches about 150° C., no trouble or danger arises in terms of maintenance and management.
第2図は従来の脱臭装置の一例を示すものであって、ダ
クト5の約13000の凝縮・粘着性ガス系とダクト1
0の約20q○の低温・低温度性ガス系とがダクト12
で合流して約8600になり、次いでミスト補集フィル
ター13、臭気ガスフアンF・を経て熱交換器1で予熱
され約240q0となって触媒脱臭装置14に導入され
、ここでバーナ16により約400qoに予熱され、触
媒反応により接触酸化して熱交換器1を経て排気筒19
から約2500Cで排出される。Figure 2 shows an example of a conventional deodorizing device, showing approximately 13,000 condensed and sticky gas systems in duct 5 and duct 1.
About 20q○ of low-temperature/low-temperature gas system is connected to duct 12.
Then, it passes through the mist collection filter 13 and the odor gas fan F, and is preheated in the heat exchanger 1 to become about 240q0 and introduced into the catalyst deodorizing device 14, where it is reduced to about 400qo by the burner 16. It is preheated, catalytically oxidized by a catalytic reaction, and then passed through a heat exchanger 1 to an exhaust pipe 19.
It is discharged at about 2500C.
なおミスト化防止のため、銀線で示すダクト20を設け
る場合もある。またバーナ16の燃焼用空気としてダク
ト10の約20ooのガスを用いる。なお第2図におい
て、21は燃焼用空気の温度を上昇させるために熱交換
器1と燃焼空気用ダクト17とを接続する昇温用ダクト
である。Note that in order to prevent mist formation, a duct 20 indicated by a silver wire may be provided. Also, about 20 oo of gas from the duct 10 is used as combustion air for the burner 16. In FIG. 2, reference numeral 21 denotes a temperature increasing duct that connects the heat exchanger 1 and the combustion air duct 17 in order to increase the temperature of the combustion air.
第1図および第2図に示、す脱臭装置の条件を第1表の
通り設定して比較試験を行ったところ、第2表に示す結
果が得られた。A comparative test was conducted with the conditions of the deodorizing apparatus shown in FIGS. 1 and 2 set as shown in Table 1, and the results shown in Table 2 were obtained.
第1表
第2表
注)使用燃料 :白灯油
低位発熱量 :10,400Kca必/紘比 重
:0.8
硫黄分 :0.015拷以下
この発明を実施する場合、ミスト除去装置としては、前
処理フィルター13に代えて他の装置を使用してもよく
、また触媒脱臭装置14の加熱方法としてバーナ16の
代りに電気加熱方法を用いてもよく、また触媒脱臭に必
要な加熱温度は、臭気ガスの成分ならびに触媒の種類に
応じて脱臭性能を維持できる範囲で種々変更することが
できる。Table 1 Table 2 Note) Fuel used: White kerosene Lower calorific value: 10,400Kca/Hiro specific gravity
: 0.8 Sulfur content: 0.015 or less When carrying out this invention, other devices may be used as the mist removal device in place of the pretreatment filter 13, and the heating method of the catalyst deodorization device 14 An electric heating method may be used instead of the burner 16, and the heating temperature required for catalyst deodorization can be varied depending on the components of the odor gas and the type of catalyst within a range that can maintain the deodorization performance.
さらにまた、直接燃焼式脱臭装置を使用してもよい。こ
の発明によれば、複数の臭気ガス発生源まなたは排出口
をもつ系における臭気ガスを、触媒反応による接触酸化
法まなたは直接燃焼法により脱臭処理するに際し、凝縮
・粘着性ガス系統と低湿度、難凝縮・粘着性ガス系統に
区別し、前記接触酸化法または直接燃焼法により脱臭処
理したのちの高温廃ガスを直列に接続した高温側熱交換
器1および低温側熱交換器2に予熱用ガスとして順次導
入し、前記低湿度、難凝縮・粘着性ガスを前記低温側熱
交換器2により加熱乾燥してなる臭気ガスを、前記凝縮
・粘着性ガスと合流混合させることにより、昇温させる
と共に相対湿度を下げてミスト化を抑制し、次いでその
合流混合された臭気ガスを、前記高温側熱交換器1によ
り加熱したのち、脱臭装置に導入するので、臭気ガスの
特性と高温側熱交換器1および低温側熱交換器2の特性
とを合理的に組合せて、高い脱臭効率を維持すると共に
、廃熱回収効率を高くして、燃料消費量を大中に減少さ
せることができ、かつ脱臭装置へ導入されるガス系にミ
スト付着による機能障害が生じるのを防止できる等の効
果が得られる。Furthermore, a direct combustion type deodorization device may be used. According to this invention, when deodorizing odor gas in a system with multiple odor gas generation sources or exhaust ports by catalytic oxidation method or direct combustion method, it is possible to use a condensed and sticky gas system. The high-temperature waste gas is separated into low-humidity, difficult-to-condensate, and sticky gas systems, and deodorized by the catalytic oxidation method or direct combustion method, and then sent to the high-temperature side heat exchanger 1 and the low-temperature side heat exchanger 2, which are connected in series. The low-humidity, difficult-to-condensate, sticky gas is heated and dried by the low-temperature side heat exchanger 2, and the odor gas is mixed with the condensable, sticky gas. The odor gas is heated and the relative humidity is lowered to suppress mist formation, and then the combined and mixed odor gas is heated by the high temperature side heat exchanger 1 and then introduced into the deodorizing device, so that the characteristics of the odor gas and the high temperature side are By rationally combining the characteristics of the heat exchanger 1 and the low-temperature side heat exchanger 2, high deodorizing efficiency can be maintained, waste heat recovery efficiency can be increased, and fuel consumption can be significantly reduced. Moreover, effects such as being able to prevent malfunctions due to mist adhesion in the gas system introduced into the deodorizing device can be obtained.
【図面の簡単な説明】
第1図はこの発明の臭気ガスの脱臭処理方法のプロセス
を示す図、第2図は従来の臭気ガスの脱臭処理方法のプ
ロセスを示す図である。
図において、1は高温側熱交換器、2は低温側熱交換器
、3は塗装あるいはプリント印刷用焼付オーブン、4は
バーナ加熱装置、、6は塗装あるいは印刷装置、7はフ
ード、8は冷却工程、9はフード、13は前処理フィル
ター、14は触媒脱臭装置、15は臭気ガス子熱室、1
6はバーナ、18は触媒酸化層、F,〜F5はファンで
ある。
第2図第1図BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a diagram showing the process of a method for deodorizing a malodorous gas according to the present invention, and FIG. 2 is a diagram showing a process of a conventional method for deodorizing a malodorous gas. In the figure, 1 is a high temperature side heat exchanger, 2 is a low temperature side heat exchanger, 3 is a baking oven for painting or printing, 4 is a burner heating device, 6 is a painting or printing device, 7 is a hood, and 8 is a cooling device. 9 is a hood, 13 is a pretreatment filter, 14 is a catalyst deodorizing device, 15 is an odor gas heating chamber, 1
6 is a burner, 18 is a catalytic oxidation layer, and F, to F5 are fans. Figure 2 Figure 1
Claims (1)
る臭気ガスを、触媒反応による接触酸化法または直接燃
焼法により脱臭処理するのに際し、凝縮・粘着性ガス系
統と低温度、難凝縮・粘着性ガス系統に区別し、前記接
触酸化法または直接燃焼法により脱臭処理したのちの高
温廃ガスを直列に接続した高温側熱交換器1および低温
側熱交換器2に予熱用ガスとして順次導入し、前記低温
度、難凝縮・粘着性ガスを前記低温側熱交換器2により
加熱乾燥してなる臭気ガスを、前記凝縮・粘着性ガスと
合流混合させることにより、昇温させると共に相対湿度
を下げてミスト化を抑制し、次いでその合流混合された
臭気ガスを、前記高温側熱交換器1により加熱したのち
、脱臭装置に導入することを特徴とする臭気ガスの脱臭
処理方法。1. When deodorizing odor gas in a system with multiple bromine gas generation sources or exhaust ports using a catalytic oxidation method using a catalytic reaction or a direct combustion method, it is necessary to use a condensable/sticky gas system and low temperature, difficult to condense/sticky gas system. The high-temperature waste gas, which has been deodorized by the catalytic oxidation method or the direct combustion method, is sequentially introduced into the series-connected high-temperature side heat exchanger 1 and low-temperature side heat exchanger 2 as a preheating gas, The low-temperature, difficult-to-condensate, sticky gas is heated and dried by the low-temperature side heat exchanger 2, and the odor gas is mixed with the condensable, sticky gas to raise the temperature and lower the relative humidity. A method for deodorizing odor gas, which comprises suppressing the formation of mist, and then heating the combined and mixed odor gas by the high-temperature side heat exchanger 1, and then introducing the odor gas into a deodorization device.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP54129433A JPS6022967B2 (en) | 1979-10-09 | 1979-10-09 | Deodorization treatment method for odor gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP54129433A JPS6022967B2 (en) | 1979-10-09 | 1979-10-09 | Deodorization treatment method for odor gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5653727A JPS5653727A (en) | 1981-05-13 |
| JPS6022967B2 true JPS6022967B2 (en) | 1985-06-05 |
Family
ID=15009358
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP54129433A Expired JPS6022967B2 (en) | 1979-10-09 | 1979-10-09 | Deodorization treatment method for odor gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6022967B2 (en) |
-
1979
- 1979-10-09 JP JP54129433A patent/JPS6022967B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5653727A (en) | 1981-05-13 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN107398260A (en) | A kind of regenerating unit and its method for being used to adsorb the activated carbon of organic exhaust gas | |
| US4242084A (en) | Air pollution control and heat recovery system for industrial ovens | |
| JP4642814B2 (en) | Exhaust gas deodorization treatment system for paint drying furnace | |
| CA1292391C (en) | Deodorization and cleaning of medium temperature wet off-gases derived from burning of wet waste sludge | |
| US4261268A (en) | Method and apparatus for treating waste material | |
| US6974494B1 (en) | Apparatus and method using an electrified filter bed for removal of pollutants from a flue gas stream | |
| US5444029A (en) | Process for destroying suspended particles | |
| US4118220A (en) | Method for treating waste material | |
| US6183707B1 (en) | Incineration of waste gases containing contaminant aerosols | |
| JPS63256200A (en) | Method and device for treating organic and inorganic mixed waste | |
| CN109899851B (en) | Fume purifying integrated machine | |
| JPS6022967B2 (en) | Deodorization treatment method for odor gas | |
| CN213840986U (en) | Organic waste gas treatment equipment | |
| CN104056530A (en) | Contaminated soil thermal decomposition tail gas treatment method | |
| CN113772915A (en) | Equipment and process technology for integrally treating oily sludge through high-temperature oxidation pyrolysis thermal desorption | |
| CN114100312A (en) | Waste gas collecting and treating system and method for semi-coke production device | |
| CN222788477U (en) | Waste oil regeneration rectifying device | |
| CN112460621A (en) | Organic waste gas treatment equipment and treatment method thereof | |
| CN106753474A (en) | A kind of domestic garbage pyrolysis processing system and low temperature, high temperature pyrolysis processing method | |
| CN206553459U (en) | A kind of domestic garbage pyrolysis processing system | |
| JPS6039415B2 (en) | Deodorization treatment method for odor gas | |
| CN114877362A (en) | Organic hazardous waste pyrolysis non-condensing incineration flue gas purification system and purification method | |
| US3258846A (en) | Drying of web materials | |
| US4176611A (en) | Method and apparatus for treating waste material | |
| CN216191844U (en) | Ageing fatlute equipment is handled in integration of high temperature oxidation pyrolysis thermal desorption |