JPS6071079A - Treatment of washing waste water - Google Patents

Treatment of washing waste water

Info

Publication number
JPS6071079A
JPS6071079A JP58181475A JP18147583A JPS6071079A JP S6071079 A JPS6071079 A JP S6071079A JP 58181475 A JP58181475 A JP 58181475A JP 18147583 A JP18147583 A JP 18147583A JP S6071079 A JPS6071079 A JP S6071079A
Authority
JP
Japan
Prior art keywords
exhaust gas
waste water
washing waste
catalyst
treatment
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
JP58181475A
Other languages
Japanese (ja)
Inventor
Shigeaki Mitsuoka
光岡 薫明
Hiroshi Ogawa
弘 小川
Toru Seto
徹 瀬戸
Korehiko Nishimoto
西本 是彦
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 Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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 Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP58181475A priority Critical patent/JPS6071079A/en
Publication of JPS6071079A publication Critical patent/JPS6071079A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To easily treat washing waste water in a system without discharging the same, by charging washing waste water, generated when an exhaust gas treating packing material is washed with water and regenerated, into the gas treating apparatus of a furnace. CONSTITUTION:When an exhaust gas treating packing material such as a catalyst is washed with water and regenerated while a reactor 12 is packed therewith, washing waste water is generated. When this washing waste water is introduced into a gas treating apparatus such as a boiler, an incinerator 2 or a flue 3, it is directly evaporated without discharging same. As mentioned above, washing waste water can be treated in the system easily without discharging the same out of the system for the purpose of treatment and post-treatment is facilitated.

Description

【発明の詳細な説明】 本発明は性能の低下した排ガス処理用の充填物でおる各
種触媒を水洗再生することによって。
DETAILED DESCRIPTION OF THE INVENTION The present invention regenerates various catalysts that are packed for exhaust gas treatment and whose performance has deteriorated by washing with water.

生じた洗浄排水を系内で処理する廃水処理方法に関する
The present invention relates to a wastewater treatment method in which generated cleaning wastewater is treated within the system.

都市とみ、産業廃棄物1石炭や石油などを燃焼させた排
ガスを触媒に通過させて排ガス中の窒素酸化物を還元し
て無害化除去する脱硝反応。
Urban and industrial waste 1 A denitrification reaction in which exhaust gas from burning coal, oil, etc. is passed through a catalyst to reduce and detoxify nitrogen oxides in the exhaust gas.

−酸化炭素あるいは炭化水素などを酸化燃焼させる反応
等に適用される各種触媒に燃焼排ガス中のダストに含ま
れるアルカリ又はアルカリ土類金属が蓄積して性能が低
下する。カリウム(Ka )、ナトリウム(Na)、マ
グネ7ウム(Mg)などのアルカリ金属は、脱硝触媒、
燃焼触媒など燃焼排ガスを対象にした触媒反応において
- Alkali or alkaline earth metals contained in dust in combustion exhaust gas accumulate in various catalysts applied to reactions that oxidize and burn carbon oxides or hydrocarbons, and their performance deteriorates. Alkali metals such as potassium (Ka), sodium (Na), and magnesium (Mg) can be used as denitrification catalysts,
In catalytic reactions targeting combustion exhaust gas such as combustion catalysts.

触媒活性を阻害する被毒物質であり、できるだけその含
有量を低減させることが望ましいが。
It is a poisonous substance that inhibits catalyst activity, and it is desirable to reduce its content as much as possible.

合成反応に使用される触媒と異なり、排ガス処理用の触
媒は環境改善が主目的であり、触媒活性、寿命を保護す
るように該排ガスを前処理するような配慮は皆無である
。最近では燃料事情の悪化からますますダスト量、ダス
ト組成の点で触媒に悪影響を与えるような排ガス源にな
ってきてかり、そこで使用される触媒に耐ダスト被毒性
を要求される状況にある。
Unlike catalysts used in synthesis reactions, the main purpose of catalysts for exhaust gas treatment is environmental improvement, and no consideration is given to pre-treating the exhaust gas to protect catalyst activity and life. Recently, due to worsening fuel conditions, dust has increasingly become a source of exhaust gas that has an adverse effect on catalysts in terms of dust amount and dust composition, and the catalysts used there are required to be resistant to dust poisoning.

そして上記の排ガス中に含有される窒素酸化物をアンモ
ニアで還元除去するに最適な脱硝触媒が開発され、各排
ガス源に対応して触媒組成。
The most suitable denitrification catalyst was developed to reduce and remove the nitrogen oxides contained in the above exhaust gas using ammonia, and the catalyst composition was developed to correspond to each exhaust gas source.

形状、製法を変えて高活−性、長期耐久性のある脱硝装
置を提供し、火力発電所、各種化学工場のボイラで数多
くの実用機が既に数多く順調に゛稼動している現状にあ
る。
We provide highly active and long-lasting denitrification equipment with different shapes and manufacturing methods, and many practical equipment are already in smooth operation in boilers at thermal power plants and various chemical factories.

この場合、ごみ焼却炉や1重油焚き及び石炭焚きボイラ
のようにダストやSOxを含有するダーティ−ガスでは
耐SOx性、耐ダスト閉塞性。
In this case, it has SOx resistance and dust blockage resistance for dirty gas containing dust and SOx, such as garbage incinerators, single fuel oil-fired boilers, and coal-fired boilers.

耐ダスト摩耗性などを考慮して最適な触媒仕様を選定す
る必要があり、 TiO2を担体にすることで耐SOx
性が十分であることから、TiO2にV2O5゜WO3
1Fe 2031 Mo03などの活性成分を担持させ
た触媒等が使用されている。又、ダスト閉塞しない触媒
形状としては前述の粒状9円柱状、だ円棒状などに成形
された触媒を移動床で使用する方法、板状、パイプ状、
ノ・ニカム状、格子状などの触媒構造体を固定床にして
排ガスを並行流で通過させる方法が比較検討され、現在
では経済性があり、保守の簡単なノーニカム触媒や格子
状触媒が主流となっている。
It is necessary to select the optimal catalyst specifications taking into account dust abrasion resistance, etc., and by using TiO2 as a carrier, SOx resistance
Since the properties are sufficient, V2O5°WO3 is added to TiO2.
A catalyst supporting an active component such as 1Fe 2031 Mo03 is used. In addition, as catalyst shapes that do not become clogged with dust, the above-mentioned catalysts shaped into granules, cylinders, elliptical rods, etc. are used in a moving bed, plate shapes, pipe shapes, etc.
Methods of using a fixed bed of catalyst structures such as non-nicum or lattice structures to allow exhaust gas to pass through in parallel have been compared, and now non-nicum catalysts and lattice-shaped catalysts are mainstream because they are economical and easy to maintain. It has become.

一万、ダスト成分が触媒内部に入りこみ触媒性能を低下
させるのを防ぐ方法としては、ダストが触媒内部に入り
にくぐするような触媒組成にしてできるだけその影響を
やわらげる以外に方法はなく、ダスト成分でも性能医下
に特に悪影響を及ぼすに、Na、Mgなどのアルカリ又
はアルカリ土類金属に耐える活性成分の選択が重要であ
り1本発明者らも種々のガス源に対応した最適の触媒組
成を提供してきた。しかしながら重油1石炭は採取され
る場所によってに、Na。
The only way to prevent dust components from entering the catalyst and reducing catalyst performance is to soften the effect as much as possible by creating a catalyst composition that allows dust to pass through the catalyst. However, it is important to select active ingredients that can withstand alkali or alkaline earth metals such as Na and Mg, which have a particularly negative effect on performance. have provided. However, the Na content of heavy oil 1 coal depends on where it is extracted.

Mg含有量が犬きく、また、ごみ焼却炉排ガス中のダス
トにはこれらアルカリ成分がかなり含有されており、こ
のような、アルカリダスト濃度の高い排ガスを処理する
場合には、運転を通じて触媒の性能が経時的に低下する
ことも考えられ、このようにして脱硝装置が所期の性能
を発揮しなくなった時は、触媒性能を回復させる必要が
あるが、に、Na、Mgなどのアルカリ又はアルカリ土
類金属を主体としたダストが触媒内部に蓄積した場合に
ぼ、その水溶性を利用して十分に水洗することが行われ
ており、触媒を反応器に充填したま\で効果的に水洗す
る方法が提供されている。
The Mg content is very high, and the dust in the exhaust gas from waste incinerators contains a considerable amount of these alkaline components. When the denitration equipment no longer exhibits the expected performance, it is necessary to restore the catalyst performance. When dust mainly composed of earth metals accumulates inside the catalyst, its water solubility is used to thoroughly wash it with water. A method is provided.

水洗は被毒物の蓄積による劣化触媒の再生に対してはも
っとも効果的な方法ではあるが、ダスト成分や溶出した
触媒成分を含み、しかも触媒量に対して、数倍の洗浄廃
水がでるために。
Washing with water is the most effective method for regenerating a deteriorated catalyst due to the accumulation of poisonous substances, but it contains dust components and eluted catalyst components, and the amount of washing wastewater is several times the amount of catalyst. .

その処理が問題とたる。The problem is how to handle it.

本発明は上記の問題点を解消する廃水処理に関するもの
で、排ガス処理充填物を反応器に充填したままの状態で
水洗再生した場合に発生する洗浄廃水をボイラ、焼却炉
な・と炉その後流の煙道内又は上記炉に付属するガス処
理装置の少なくとも1つに投入し、系内で無排水化する
洗浄廃水の処理方法を特徴とし、その目的とするところ
は洗浄廃液を系外に排出することなくプラント系内で無
排水化処理する点にある。
The present invention relates to wastewater treatment that solves the above-mentioned problems.The present invention relates to wastewater treatment that solves the above-mentioned problems. It is characterized by a method for treating cleaning wastewater that is introduced into the flue of the furnace or into at least one of the gas treatment devices attached to the above-mentioned furnace, and is made non-drainage within the system, and its purpose is to discharge the cleaning waste liquid to the outside of the system. The point is that wastewater treatment is carried out within the plant system without any waste.

次に添付図面にもとすいて本発明の詳細な説明する。第
1図はごみ焼迦炉の排ガス脱硝装置に適用した場合の1
例である。
The present invention will now be described in detail with reference to the accompanying drawings. Figure 1 shows the case when applied to the exhaust gas denitrification equipment of a garbage incinerator.
This is an example.

通常の運転時においてはホッパー1から投入されたごみ
は焼却炉2で燃焼され、その排ガスは煙道3を通りガス
冷却装置4で冷却されて。
During normal operation, garbage introduced from a hopper 1 is burned in an incinerator 2, and its exhaust gas passes through a flue 3 and is cooled by a gas cooling device 4.

集塵器6で除塵後排ガス中のNOxと還元剤として供給
されたアンモニアガス11とを脱硝触媒層内の反応ゾー
ン7vcて反応せしめて、無害な窒素と水とに分解させ
るものであり、脱硝後の排ガス8は更に後流に通される
。ごみ焼却炉の排ガスの場合塵芥中の塩化ビニールの燃
焼によって生じfcHctの濃度が高いために消石灰な
どの吹き込み方法を採用した脱塩酸処理塔の如きガス処
理装置5を集塵器の上流側あるいは脱硝装置の下流側に
設ける(第1図は上流側に設けた場合を示す)のが一般
的である。
After dust removal in the dust collector 6, the NOx in the exhaust gas and the ammonia gas 11 supplied as a reducing agent are reacted in the reaction zone 7vc in the denitrification catalyst layer, decomposing them into harmless nitrogen and water. The subsequent exhaust gas 8 is further passed into the wake. In the case of exhaust gas from a garbage incinerator, the concentration of fcHct produced by the combustion of vinyl chloride in the garbage is high. It is generally provided on the downstream side of the device (Figure 1 shows the case where it is provided on the upstream side).

プラントの運転を通じ何らかの原因例えば排ガスダスト
中のアルカリ成分などによる蓄積によって、触媒の性能
が低下してきた場合にはス−ツブロー装置13に洗浄水
を外部から導入し。
If the performance of the catalyst deteriorates due to some reason during plant operation, such as accumulation of alkaline components in exhaust gas dust, cleaning water is introduced into the soot blowing device 13 from the outside.

洗浄ノズル12全通して触媒を水洗し再生する。The catalyst is washed with water through the entire cleaning nozzle 12 and regenerated.

触媒の被毒成分や溶出した活性成分を含んだ洗浄廃水9
は洗浄廃水出口ホッパ−10を通して。
Washing wastewater containing catalyst poisoning components and eluted active components 9
through the washing waste water outlet hopper 10.

供給ポンプ14によってプラント系内の各場所に導入さ
れる。この場所としては焼却炉、ガス処理装置を構成す
るガス冷却装置、脱塩酸処理塔などであり、この導入方
法は3ケ所同時又は単独に行ってもよい。焼却炉に導入
された廃水は直ちに蒸発し、ガス冷却装置では通常水を
噴霧する冷却方法が採用されており、廃水をこの冷却水
の一部として使用し、しかもこの冷却水は循環使用され
るため、系外に排出されることはなく、無排水化処理が
可能となる。一方脱塩酸処理塔では消石灰や炭酸カルシ
ウムのスラリー溶液を噴霧し、排ガス中のHClを塩化
物に置換して、除去する方法がとられているが、洗浄廃
水をこのスラリー溶液に混入させて、処理することがで
きる。洗浄廃水を利用しても脱HC1そのものの機能は
何んら低下することは&(。
It is introduced to each location within the plant system by a feed pump 14. These locations include an incinerator, a gas cooling device constituting a gas treatment device, a dehydrochlorination treatment tower, etc., and this introduction method may be carried out at three locations simultaneously or individually. The wastewater introduced into the incinerator evaporates immediately, and gas cooling equipment usually uses a cooling method that sprays water, and the wastewater is used as part of this cooling water, and this cooling water is recycled. Therefore, it is not discharged outside the system, making it possible to perform wastewater-free treatment. On the other hand, in dehydrochlorination treatment towers, a slurry solution of slaked lime or calcium carbonate is sprayed to replace HCl in the exhaust gas with chloride and remove it. can be processed. Even if washing wastewater is used, the function of deHC1 itself will not deteriorate in any way.

効果的に処理できる。Can be processed effectively.

第2図はボイラ排ガス脱硝装置に適用した場合の1例を
示し、第1図を簡略して図示したものである。この場合
も水洗再生によって生じた洗浄廃水はボイラ15および
又は煙道3内に投入散布され、処理される。その他につ
いては第1図と同様であるので説明を省略する。
FIG. 2 shows an example of application to a boiler exhaust gas denitrification device, and is a simplified illustration of FIG. 1. In this case as well, the washing wastewater generated by the water washing regeneration is thrown into the boiler 15 and/or the flue 3, and is then disposed of therein. The other details are the same as those in FIG. 1, so the explanation will be omitted.

捷た1本実施例における洗浄水は添加薬品を含む水溶液
なども該当し、水のみに限定するものではない。
The washing water in this embodiment may also be an aqueous solution containing additive chemicals, and is not limited to water alone.

以上説明したように本発明は排ガス中のアルカリダスト
などによって触媒が被毒して、脱硝装置が初期の性能を
発揮できなくなり、水洗再生する場合において、洗浄廃
液を系外で処理することなく、系内で容易に無排水化で
きるものであり、実用上多いに有用である。
As explained above, the present invention enables the catalyst to be poisoned by alkaline dust in the exhaust gas, making it impossible for the denitrification equipment to perform at its initial level, and when the denitrification equipment is regenerated by water washing, without treating the washing waste liquid outside the system. It can easily be made waste-free within the system, and is very useful in practice.

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

第1図はごみ焼却炉の排ガス用脱硝装置に適用した実施
例を示すフロー チャト、第2図はボイラ排ガス用脱硝
装置に適用した場合の実施例を示すフローチャートであ
る。 2・・・焼却炉、3・・・煙道、4・・・ガス冷却装置
。 5・・・脱塩酸処理塔。 (9)
FIG. 1 is a flowchart showing an embodiment applied to a denitration device for exhaust gas of a garbage incinerator, and FIG. 2 is a flowchart showing an embodiment applied to a denitrification device for boiler exhaust gas. 2... Incinerator, 3... Flue, 4... Gas cooling device. 5...Dehydrochlorination treatment tower. (9)

Claims (1)

【特許請求の範囲】[Claims] 排ガス処理充填物を反応器に充填した1まの状態で水洗
再生した場合に発生する洗浄廃水をボイラ、焼却炉など
の炉、その後流の煙道内又は上記炉に付属するガス処理
装置の少なくとも1つに投入し系内で無排水化すること
を特徴とする洗浄廃水の処理方法。
The cleaning waste water generated when the exhaust gas treatment filler is washed and regenerated in the state of filling the reactor with water is collected in a boiler, a furnace such as an incinerator, the flue downstream of it, or at least one of the gas treatment equipment attached to the above-mentioned furnace. A method for treating cleaning wastewater, which is characterized by inputting it into a system and making it non-drainage within the system.
JP58181475A 1983-09-29 1983-09-29 Treatment of washing waste water Pending JPS6071079A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58181475A JPS6071079A (en) 1983-09-29 1983-09-29 Treatment of washing waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58181475A JPS6071079A (en) 1983-09-29 1983-09-29 Treatment of washing waste water

Publications (1)

Publication Number Publication Date
JPS6071079A true JPS6071079A (en) 1985-04-22

Family

ID=16101401

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58181475A Pending JPS6071079A (en) 1983-09-29 1983-09-29 Treatment of washing waste water

Country Status (1)

Country Link
JP (1) JPS6071079A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6631727B2 (en) * 1996-07-12 2003-10-14 Energie-Versorgung Schwaben Ag Method of cleaning and/or regenerating wholly or partially de-activated catalysts of stack-gas nitrogen scrubbing

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6631727B2 (en) * 1996-07-12 2003-10-14 Energie-Versorgung Schwaben Ag Method of cleaning and/or regenerating wholly or partially de-activated catalysts of stack-gas nitrogen scrubbing

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