JPS5817843A - Activating method for catalyst - Google Patents
Activating method for catalystInfo
- Publication number
- JPS5817843A JPS5817843A JP56114419A JP11441981A JPS5817843A JP S5817843 A JPS5817843 A JP S5817843A JP 56114419 A JP56114419 A JP 56114419A JP 11441981 A JP11441981 A JP 11441981A JP S5817843 A JPS5817843 A JP S5817843A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- catalysts
- water
- performance
- washing
- 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
Links
- 239000003054 catalyst Substances 0.000 title claims abstract description 104
- 238000000034 method Methods 0.000 title claims abstract description 28
- 230000003213 activating effect Effects 0.000 title abstract description 6
- 238000005406 washing Methods 0.000 claims abstract description 34
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 50
- 230000004913 activation Effects 0.000 claims description 3
- 239000007864 aqueous solution Substances 0.000 claims description 3
- 238000002485 combustion reaction Methods 0.000 abstract description 8
- 230000000694 effects Effects 0.000 abstract description 8
- 230000003197 catalytic effect Effects 0.000 abstract description 2
- 239000008237 rinsing water Substances 0.000 abstract 1
- 239000002912 waste gas Substances 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 29
- 239000000428 dust Substances 0.000 description 18
- 239000000243 solution Substances 0.000 description 16
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 14
- 239000004480 active ingredient Substances 0.000 description 11
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 9
- 239000003513 alkali Substances 0.000 description 8
- 150000001342 alkaline earth metals Chemical class 0.000 description 8
- 238000006243 chemical reaction Methods 0.000 description 6
- 239000011777 magnesium Substances 0.000 description 6
- 231100000614 poison Toxicity 0.000 description 6
- 230000007096 poisonous effect Effects 0.000 description 6
- 238000011084 recovery Methods 0.000 description 6
- 229910052783 alkali metal Inorganic materials 0.000 description 5
- 150000001340 alkali metals Chemical class 0.000 description 5
- 229910052708 sodium Inorganic materials 0.000 description 5
- 239000011734 sodium Substances 0.000 description 5
- 239000013543 active substance Substances 0.000 description 4
- 229910052749 magnesium Inorganic materials 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 239000002994 raw material Substances 0.000 description 4
- 239000007921 spray Substances 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 3
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 3
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 3
- 238000001035 drying Methods 0.000 description 3
- 229910052700 potassium Inorganic materials 0.000 description 3
- 239000011591 potassium Substances 0.000 description 3
- 238000005507 spraying Methods 0.000 description 3
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- -1 cylinders Substances 0.000 description 2
- 230000003247 decreasing effect Effects 0.000 description 2
- 230000006866 deterioration Effects 0.000 description 2
- 238000010828 elution Methods 0.000 description 2
- 239000008187 granular material Substances 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 231100000572 poisoning Toxicity 0.000 description 2
- 230000000607 poisoning effect Effects 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 238000005299 abrasion Methods 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000012190 activator Substances 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 239000012298 atmosphere Substances 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 230000005923 long-lasting effect Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 230000008685 targeting Effects 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 238000009736 wetting Methods 0.000 description 1
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
Description
【発明の詳細な説明】
中に被毒物の蓄積により性能が低下した時、水洗で性能
を回復させる場合に実装置に触媒を充填した使用できる
状態のままで水洗して賦活させる方法の改良法に関し、
石炭や石油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、
一酸化炭素あるいは炭化水素などを酸化燃焼させる反応
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(カリウム、ナトリ
ウム、マグネシウムなど)が蓄積して性能が低下した場
合に特に有効な手段である。[Detailed Description of the Invention] An improved method of activating a catalyst by washing it with water while the catalyst is still in a ready-to-use state when the performance is degraded due to the accumulation of poisonous substances in the device and the performance is restored by washing with water. Regarding
A denitrification reaction that passes exhaust gas from burning coal or oil through a catalyst to reduce and detoxify nitrogen oxides in the exhaust gas.
Alkali or alkaline earth metals (potassium, sodium, magnesium, etc.) contained in dust in combustion exhaust gas accumulate in various catalysts used in reactions that oxidize and burn carbon monoxide or hydrocarbons, resulting in decreased performance. This is a particularly effective method in cases where
カリウム、ナトリウムなどのアルカリ金属&ま、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
いて触媒活性点を阻害する被毒物質であるので、できる
だけその含有量を低減させることが望ましいが、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Gマ皆無で“あり、
最近では燃料事情の悪化からますますダスト量、ダスト
組成で触媒に悪影響を与えるような排ガス源になってき
ており、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。Alkali metals such as potassium and sodium are poisonous substances that inhibit catalytic active sites in catalytic reactions targeting combustion exhaust gas, such as denitrification catalysts and combustion catalysts, so it is desirable to reduce their content as much as possible. Unlike catalysts used in synthesis reactions, the main purpose of catalysts for exhaust gas treatment is to improve the environment, and there is no consideration given to pre-treating the exhaust gas to protect catalyst activity and lifespan.
In recent years, due to worsening fuel conditions, dust has increasingly become a source of exhaust gas that has an adverse effect on catalysts due to its amount and composition, and the catalysts used there are required to be resistant to dust poisoning.
本発明者らも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を開発し、
各排ガス源に対エムして触媒組成、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。The present inventors have also developed a denitrification catalyst that is optimal for reducing and removing nitrogen oxides contained in the above exhaust gas with ammonia,
By changing the catalyst composition, shape, and manufacturing method to suit each exhaust gas source, we provide highly active and long-lasting denitrification equipment, which is already successfully used in many practical applications in boilers of thermal power plants and various chemical plants. It is in operation.
部ち、LNG焚きボイラの如くダス)、SOxを含まな
いクリーンガスでは耐SOx性、耐ダスト閉塞性の心配
がないため、AI!20.のような耐SOX性の不十分
な担体でも実用上は何ら問題なく安価なことから、A/
203にv2o5. WO5* ii’e203゜M
o Os などの活性成分を組合せた触媒が使用され
、ダスト閉塞性の心配もないことがら粒状、円柱状、だ
固体状などに成形された触媒を固定床で使用している。However, with clean gas that does not contain SOx, there is no need to worry about SOx resistance or dust blockage resistance, so AI! 20. Even carriers with insufficient SOX resistance such as A/
203 v2o5. WO5* ii'e203゜M
A catalyst containing active ingredients such as o Os is used, and since there is no concern about dust clogging, catalysts shaped into granules, cylinders, solids, etc. are used in a fixed bed.
そして排ガス中のダストも皆無に近く、ダストによる性
能低下は全くないといっても過言ではない。There is also almost no dust in the exhaust gas, and it is no exaggeration to say that there is no deterioration in performance due to dust.
一方、重油焚きボイラや石炭焚きボイラのようにダスト
とSOxを含有するダーティガスでは耐SOx性、耐ダ
スト被毒性、耐ダスト閉塞性、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、TlO
2を担体にすることで耐SOx性が十分あることがら、
T z O2にv2o5゜WO3,Fe2O2,MoO
3などの活性成分を組合せた触媒が使用されている。又
ダスト閉塞しない触媒形状としては、前述の粒状、円柱
状、だ固体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、ハニカム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、保守の簡単なハニカム
触媒が主流となっている。On the other hand, in the case of dirty gas containing dust and SOx, such as heavy oil-fired boilers and coal-fired boilers, the SOx resistance, dust toxicity resistance, dust clogging resistance, dust abrasion resistance, etc.
It is necessary to select the optimal catalyst specifications in consideration of TlO
2 as a carrier has sufficient SOx resistance,
T z O2 v2o5゜WO3, Fe2O2, MoO
Catalysts with combinations of active ingredients such as 3 have been used. In addition, as catalyst shapes that do not become clogged with dust, the above-mentioned method of using catalysts shaped like granules, cylinders, solids, etc. in a moving bed, and using catalyst structures such as plates, pipes, honeycomb shapes, etc. as fixed beds. Methods of passing exhaust gas in parallel flow have been compared and studied, and honeycomb catalysts are now mainstream because they are economical and easy to maintain.
そして石炭焚きボイラの高ダスト側での脱硝反応にも硬
度の高いハニカム触媒が開発され実用上はとんど問題の
ない状態である。A highly hard honeycomb catalyst has also been developed for denitrification reactions on the high-dust side of coal-fired boilers, and there are virtually no problems in practical use.
しかしダスト成分が触媒内部に入りこる触媒性能を低下
させるのを防ぐ方法としては、ダストが触媒内部に入り
にくく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低
下に特に悪影響を及ぼすカリウム(Kへナトリウム(N
a)、マグネシウム(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、
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
見出してきた。重油、石炭は採取される場所によってに
、 Na、 Mg含有量が大きく異なり、これらの金属
含有量が多い程、耐アルカリダクト性が触媒に要求され
る。しかしながら、これらの金属は排ガス中では大部分
硫酸塩として存在しているので、水に可溶であり、触媒
表面にダストが付着した状態で水で濡れたり、ボイラ蒸
発管やエコノマイザ−給水管の破損事故で火炉中のダス
トを含んだ蒸気又は水が触媒を濡らす場合には触媒内部
に急激にに、 Na、 Mgなとの被毒物が増加して、
予期していない性能低下をきたし、ボイラ運用できない
場合が考えられる。However, 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 makes it difficult for dust to enter the catalyst. Potassium (K) and sodium (N
a) It is important to select active ingredients that are resistant to alkali or alkaline earth metals such as magnesium (Mg);
The present inventors have also discovered optimal catalyst compositions compatible with various gas sources. The Na and Mg contents of heavy oil and coal vary greatly depending on where they are extracted, and the higher the metal content, the more alkali duct resistance is required of the catalyst. However, since most of these metals exist in the form of sulfates in exhaust gas, they are soluble in water, and they may become wet with water with dust attached to the catalyst surface, or they may be exposed to boiler evaporator pipes or economizer water supply pipes. If the catalyst is wetted by dust-laden steam or water in the furnace due to a breakage accident, poisonous substances such as Na and Mg will rapidly increase inside the catalyst.
There is a possibility that the boiler cannot be operated due to unexpected performance deterioration.
このような緊急事故により脱硝装置が所期の性能を発揮
しなくなった時は最悪の場合ボイラを停止せざるを得な
い状況になることも想定されるので短期間で性能回復さ
せる方法を提供する必要がある。If the denitrification equipment no longer performs as expected due to such an emergency accident, in the worst case scenario, the boiler may have to be shut down, so we provide a method to restore performance in a short period of time. There is a need.
前述のようにに、 Ka、 Mgなとのアルカリ又はア
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
た場合は、水溶性を利用して十分に水洗すれば良いこと
は知られている。しかしこれは触媒を脱硝装置から取り
出して、さらに触媒を複数にまとめているパックからは
ずした後の処理法であり、事業用ボイラのように触媒が
大量に使用されており、それらを短期間に水洗賦活させ
る方法としては全く実用性はないといえる。即ち緊急時
に触媒性能を回復させるためにだけボイラを長期間停止
することは、前述のように排ガス処理用触媒としての使
命から許されないことであり、できるだけ短期間に安価
に活性を賦活させなければならない。As mentioned above, it is known that if dust mainly composed of alkali or alkaline earth metals such as Ka and Mg accumulates inside the catalyst, it is sufficient to take advantage of its water solubility and wash it thoroughly with water. . However, this is a treatment method that takes the catalyst out of the denitrification equipment and then removes it from the pack that holds multiple catalysts together.In commercial boilers where large quantities of catalysts are used, they can be processed in a short period of time. It can be said that the method of activating by washing with water is completely impractical. In other words, stopping the boiler for a long period of time only to restore catalyst performance in an emergency is not allowed due to its mission as an exhaust gas treatment catalyst, as mentioned above. No.
本発明者らはこのような考えに基づいて大量の触媒を実
装置内に充填した状態でできるだけ短時間に水洗処理で
触媒性能を回復させる方法として、水洗ノズルを使−用
して整置反応層においてはガス入口部、横置反応層にお
いてはガス入口部又は出口部に前記の水洗ノズルを設け
て触媒を洗浄することで被毒成分を溶出させ、触媒性能
を回復させる方法を先に帰寮したが、本発明はこの方法
の改良法に関するものである。Based on this idea, the present inventors conducted a stationary reaction using a water washing nozzle as a method to recover the catalyst performance by water washing treatment in the shortest possible time with a large amount of catalyst packed in an actual device. We have previously proposed a method in which poisoning components are eluted and the catalyst performance is restored by installing the water washing nozzle at the gas inlet in the bed and at the gas inlet or outlet in the horizontal reaction bed to wash the catalyst. However, the present invention relates to an improved method of this method.
前述のように排ガスダスト中のアルカリ又はアルカリ土
類金属成分によって被毒した触媒は水洗によって性能の
回復が計られるが、本発明者等の試験ではアルカリ又は
アルカリ土類金属成分を触媒中から完全に溶出したにも
がかわらず、フレッシュ時の性能まで戻らない現象が度
々みられた。本発明者らはこの現象を解明するべく、比
表面積、細孔容積をはじめとして、触媒成分の変化など
性能に影響を与えるあらゆる物性の水洗による回復度合
を調べた結果、水洗によって触媒成分が一部溶出して、
濃度低下をきたしたことがその主原因であるとの結論に
達した。ての溶出量は水洗量が増せば多くなるのでアル
カリ又はアルカリ土類金属による触媒被毒が大きい場合
など、水洗回数を多くすれば、それだけ性能の回復が悪
くなるが、ただ、酸化物の形態をとる触媒成分の方がア
ルカリ又はアルカリ土類金属よりも溶解度ははるかに小
さいため被毒成分除去による性能回復効果に比べて、溶
出によるマイナス効果は小さくすることば可本発明者ら
は大量の触媒を装置内に充填したままの状態で、水洗後
、フレッシュ触媒の性能まで回復させる方法として、水
洗時の活性成分溶出分を水洗の最後に補充し、活性賦活
する方法を見い出し、ここに提案するものである。As mentioned above, the performance of catalysts poisoned by alkali or alkaline earth metal components in exhaust gas dust can be restored by washing with water, but in our tests, the alkali or alkaline earth metal components were completely removed from the catalyst. Despite being eluted, the performance often did not return to its fresh state. In order to elucidate this phenomenon, the present inventors investigated the degree of recovery by water washing of all physical properties that affect performance, including specific surface area, pore volume, and changes in catalyst components. Partly eluted,
It was concluded that the main cause was a decrease in the concentration. The amount of eluted water increases as the amount of water washing increases, so if the catalyst is heavily poisoned by alkali or alkaline earth metals, increasing the number of water washings will worsen the performance recovery. Since the solubility of the catalyst component is much lower than that of alkali or alkaline earth metals, the negative effect of leaching is smaller than the performance recovery effect of removing the poisonous component. As a method to restore the performance of a fresh catalyst after washing with water still filled in the equipment, we have discovered and proposed here a method of replenishing the active ingredient eluted during washing at the end of washing and activating the catalyst. It is something.
すなわち、本発明は触媒の性能低下時に、触媒を装置内
に充填したままの状態で水洗により性能を回復させる方
法において、水洗時に溶出する触媒活性成分を含有する
水溶液を水洗工程の最後に使用することを特徴とする触
媒の賦活方法に関するものである。That is, the present invention is a method for restoring the performance of a catalyst by washing it with water while the catalyst is still packed in an apparatus when its performance deteriorates, in which an aqueous solution containing a catalytically active component that is eluted during washing is used at the end of the washing step. The present invention relates to a method for activating a catalyst characterized by the following.
本発明はアルカリ又はアルカリ土類金属による触媒への
被毒作用で触媒性能が低下した場合には、脱硝触媒だけ
に限定されることはなく、燃焼触媒のような酸化触媒、
吸着剤を使用する脱硫法にも適用可能であることはいう
までもな()。The present invention is not limited only to denitrification catalysts, but also applies to oxidation catalysts such as combustion catalysts,
It goes without saying that it is also applicable to desulfurization methods that use adsorbents ().
以下具体的に本発明を詳述する。The present invention will be specifically described below.
第1図はボイラ燃焼排ガス用脱硝装置に適用する場合の
1例を示す。通常の運転時においてはボイラ7の燃焼排
ガス8は脱硝装置6に導入され、排ガス中の窒素酸化物
と、還元剤として供給されたアンモニアガス14を脱硝
触媒層1内疋て反応せしめて、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9は後流のエアヒー
タ10を通して燃交換した後に更に後流に通される。触
媒層の水洗は反応層1のガス通過面に対面して洗浄用ノ
ズル2を設置し、洗浄水3を外部から導入して行い、触
媒中に含まねている被毒成分を溶出せしめ、洗浄排出水
4として排気処理槽5に集合させる。水洗が完了したな
らば、次に、活性成分溶出分の補充操作ii二移る。そ
の方法は単に水洗水が活性成分溶液(・コとりかJつっ
ただけであって、何んら水洗要領と変わりない。FIG. 1 shows an example of application to a denitrification device for boiler combustion exhaust gas. During normal operation, the combustion exhaust gas 8 of the boiler 7 is introduced into the denitrification device 6, and nitrogen oxides in the exhaust gas and ammonia gas 14 supplied as a reducing agent react within the denitrification catalyst layer 1 and are harmless. The denitrified exhaust gas 9 is passed through the downstream air heater 10 for refueling, and then passed further downstream. The catalyst layer is washed with water by installing a cleaning nozzle 2 facing the gas passage surface of the reaction layer 1 and introducing cleaning water 3 from the outside to elute poisonous components contained in the catalyst and clean it. The waste water is collected in an exhaust treatment tank 5 as waste water 4. Once the water washing is completed, the next step is to replenish the eluted active ingredient (ii). This method is no different from the washing procedure, as the washing water is simply an active ingredient solution.
即ち、活性溶液3をノズル2を通して触媒全体に散布し
、過剰溶液4は回収槽5に集合させろ。回収槽5の活性
溶液は水洗が完全であったならば、アルカリ金属成分の
混入はないため、循環使用も可能である。That is, the active solution 3 is sprayed over the entire catalyst through the nozzle 2, and the excess solution 4 is collected in the recovery tank 5. If the active solution in the recovery tank 5 has been thoroughly washed with water, there will be no alkali metal components mixed in, so it can be recycled.
ただし、この活性成分を触媒に散布する時期が水洗直後
であれば触媒の吸水量はかなり低下しているので、でき
れば触媒に残っている水分の水切りはもとより、触媒の
乾燥を行い、吸水量を高めた上で、活性成分の散布操作
に移るのが望ましい。散布する溶液濃度は活性成分の溶
出量及び触媒の吸水量によって決定されなければならな
いが、溶出量はその溶解度から使用水購と液温さえわか
れば容易に推定し得るし、又吸水量は残水量から求め得
るので、溶液の濃度を水洗の条件に応じて変化させるの
は容易である。活性体の原料としては通常の触媒調製時
と同様、硝酸塩、硫酸塩など溶解度の大きい化合物を用
い、その水溶液として触媒に散布すれば脱硝雰囲気のガ
ス温度によって容縞に酸化物の形に変換し得る。However, if this active ingredient is sprayed on the catalyst immediately after washing, the amount of water absorbed by the catalyst will have decreased considerably, so if possible, drain the remaining water from the catalyst and dry the catalyst to reduce the amount of water absorbed. After increasing the concentration, it is desirable to proceed to the spraying operation of the active ingredient. The concentration of the solution to be sprayed must be determined by the amount of elution of the active ingredient and the amount of water absorbed by the catalyst, but the amount of elution can be easily estimated from its solubility as long as the amount of water used and the liquid temperature are known, and the amount of water absorbed can be determined by determining the amount of water absorbed by the remaining water. Since it can be determined from the amount of water, it is easy to change the concentration of the solution depending on the washing conditions. As in the case of normal catalyst preparation, compounds with high solubility such as nitrates and sulfates are used as raw materials for the active substance, and if they are sprayed on the catalyst as an aqueous solution, they will be rapidly converted into oxides depending on the gas temperature of the denitrification atmosphere. obtain.
触媒の乾燥方法としては例えば通気ブロワ13を駆動し
、空気11.12をボイラを紅由して、触媒層1に供給
することなどが挙げ1)れる。As a method for drying the catalyst, for example, 1) the ventilation blower 13 is driven, air 11, 12 is passed through a boiler, and the air is supplied to the catalyst layer 1.
以上の如く、本発明は触媒の性能低下時に装置内に触媒
を充填したままの状態で、水洗後、活性成分溶出分を再
担持することにより、短期間に性能を初期性能まで回復
させるものであり、従来のように脱硝装置から触媒を系
外に取り出して再生を行い、再生後の触媒を再充填する
といった方法は必要とせず、本発明の採用により、簡易
な方法で短期間に経済的に初期性能までの触媒の再生が
可能となり、実用上大きく貢献するものである。As described above, the present invention recovers the performance to the initial performance in a short period of time by re-supporting the active ingredient eluted after washing with water while the catalyst is still packed in the device when the performance of the catalyst deteriorates. There is no need for the conventional method of taking the catalyst out of the denitrification equipment, regenerating it, and refilling the regenerated catalyst, and by adopting the present invention, it can be done in a simple and economical manner in a short period of time. This makes it possible to regenerate the catalyst to its initial performance, making a major contribution to practical use.
次に本発明方法を実施例によって説明する。Next, the method of the present invention will be explained with reference to examples.
〔実施例1〕 重油焚ボイラ排ガス用脱硝装置内で約−年間。[Example 1] Approximately 1 year in a denitrification equipment for heavy oil-fired boiler exhaust gas.
の運転実績を持つTlO2−V205触媒に水を噴霧し
て湿潤させ、その後乾燥し、その前後の脱硝性能を比較
した結果、湿潤、乾燥後のものは性能に劣化がみられた
。これは触媒表面の付着ダスト中のアルカリ金属成分(
K、 Naなと)が溶解し、触媒内部に浸入したもので
あることが、第1表に示す触媒の組成分析の結果、判明
した。。A TlO2-V205 catalyst with a track record of operation was wetted by spraying water, then dried, and the denitrification performance before and after was compared. As a result, the denitrification performance of the catalyst after wetting and drying was found to be degraded. This is due to the alkali metal component (
As a result of the compositional analysis of the catalyst shown in Table 1, it was found that the catalyst was dissolved and infiltrated into the catalyst. .
第 1 表
この湿潤・乾燥した触媒1a〜1dを第2図に示す如く
4段積み重ねて、その上部にフルコーン型スプレーノズ
ル2を設置し、水洗水5を触媒上に55 l / mi
nで噴霧し続け、触媒内部に含まれているアルカリ金属
成分など被毒成分を水洗溶出させた。水洗時間を区切り
、乾燥させて脱硝性能を計測し、引続いて水洗を行う操
作を繰返した。水洗は計100分間実施したが、60分
間以とでは性能かや匁低下する傾向は見えても、これ以
上の上昇は期待できず、初期から4%低い脱硝率であっ
た。Table 1 The wet and dry catalysts 1a to 1d were stacked in four stages as shown in Fig. 2, a full cone spray nozzle 2 was installed on top of the stack, and washing water 5 was poured onto the catalyst at a rate of 55 l/mi.
The catalyst was continuously sprayed with water to wash and elute poisonous components such as alkali metal components contained inside the catalyst. The operation of washing with water was divided into intervals, drying was performed, the denitrification performance was measured, and the subsequent washing with water was repeated. Water washing was carried out for a total of 100 minutes, and although there was a tendency for the performance to decrease slightly after 60 minutes, no further increase could be expected, and the denitrification rate was 4% lower than from the initial stage.
活性成分v205 の水に対する溶解度と使用水量な
どからv205 の単位触媒量当りの溶出量を求め、
これに見合う量を補充するものとして、吸水量とがら■
2o5の原料である■os04 溶液の濃度を割り出
し、調製した。この溶液を水洗の場合と同じ要領で、4
段積み重ねた触媒上に設置したフルコーン型スプレーノ
ズル2を通して、活性溶液を触媒層全体に噴霧し、回収
液は一部循環使用した。賦活条件は第2表に示す通りで
ある。また、第6表に示す脱硝率測定条件下での脱硝性
能測定結果を第4表に示すが、活性溶液塗布後脱硝性能
は完全に初期性能まで賦活した。From the solubility of the active ingredient v205 in water and the amount of water used, calculate the amount of v205 eluted per unit amount of catalyst.
To replenish the amount commensurate with this, the water absorption capacity and ■
■The concentration of the os04 solution, which is the raw material for 2o5, was determined and prepared. Add this solution in the same way as for washing with water,
The active solution was sprayed over the entire catalyst layer through a full-cone spray nozzle 2 installed on the stacked catalysts, and a portion of the recovered liquid was recycled and used. Activation conditions are as shown in Table 2. Further, Table 4 shows the results of measuring the denitrification performance under the conditions for measuring the denitrification rate shown in Table 6, and the denitrification performance was completely activated to the initial performance after application of the active solution.
第2表 賦活条件
第3表 脱硝率測定条件
〔実施例2〕
実施例1における方法をFe2O,を活性体とするT1
02−Fe2o3 触媒に適用した結果を第5表に示
すが、アルカリ金属成分によって被毒したFe2O3を
活性体とする触媒においても本発明方法は適用可能であ
った。Table 2 Activation conditions Table 3 Denitrification rate measurement conditions [Example 2] T1 using the method in Example 1 with Fe2O as the activator
Table 5 shows the results when applied to the 02-Fe2o3 catalyst, but the method of the present invention was also applicable to a catalyst whose active substance is Fe2O3 poisoned by an alkali metal component.
第 5 表
〔実施例3〕
第5図に示すように、停止中の重油焚ボイラ排ガス用脱
硝装置6の上部に設置したスプレーノズル2で触媒層全
体1を60分間水洗後、触媒層を仕切り、触媒層1−a
〜1dの上部からスプレーノズルで濃度調製したvO8
04溶液を触媒層全体に噴霧した。排水又は過剰溶液4
は排水処理槽又は活性溶液回収槽5に投入し、活性、溶
液は一部循環使用した。触媒は洗浄後、乾燥させ、ボイ
ラの再スタート後に水洗浄のみの触媒層部と水洗後活性
溶液の散布を受けた触媒層部との脱硝性能を比較したそ
の結果を第6表に示す。Table 5 [Example 3] As shown in Fig. 5, the entire catalyst layer 1 was washed with water for 60 minutes using the spray nozzle 2 installed at the top of the denitrification device 6 for the exhaust gas of a stopped heavy oil-fired boiler, and then the catalyst layer was partitioned. , catalyst layer 1-a
vO8 concentration was adjusted with a spray nozzle from the top of ~1d.
04 solution was sprayed over the entire catalyst layer. Drainage or excess solution 4
was put into a wastewater treatment tank or active solution recovery tank 5, and part of the active solution was recycled and used. The catalyst was washed and dried, and after restarting the boiler, the denitrification performance of the catalyst layer section that was only washed with water and the catalyst layer section that was sprayed with an active solution after water washing were compared. Table 6 shows the results.
第 6 表
排ガス温度380℃
上記実施例においては活性体としてU2O5゜Fe2O
3,その原料としてV OSO4+ F e S O4
の場合についてのみ記したが、活性体及びその原料とも
これらに限定されるものではない。Table 6 Exhaust gas temperature: 380°C In the above example, the active substance was U2O5°Fe2O.
3.V OSO4+ Fe SO4 as its raw material
Although only the cases described above are described, the active substance and its raw materials are not limited thereto.
第1図はボイラ燃焼排ガス脱硝装置に本発明方法を適用
した場合のフローシートであり、第2図は触媒の水洗ま
たは活性溶液散布試験の態様を示す図であり、第3図は
実用脱硝装置内で本発明方法と、比較例としての水洗の
みを適用してその効果を比較した際の実施態様を示す側
面図Aおよび平面図Bである。
復代理人 内 1) 明
復代理人 萩 原 亮 −
第3図
(A) (B)
J−5Figure 1 is a flow sheet when the method of the present invention is applied to a boiler combustion exhaust gas denitrification system, Figure 2 is a diagram showing the mode of catalyst washing with water or active solution spraying test, and Figure 3 is a practical denitrification equipment. FIG. 2 is a side view A and a plan view B showing an embodiment in which the effects of the method of the present invention and only water washing as a comparative example are compared. Sub-agents 1) Meiji agent Ryo Hagiwara - Figure 3 (A) (B) J-5
Claims (1)
態で水洗により性能を回復させる方法において、水洗時
に溶出する触媒成分を含有する水溶液を水洗工程の最後
に使用することを特徴とする触媒の賦活方法。A method for restoring the performance of a catalyst by washing it with water while the catalyst is still packed in an apparatus when its performance deteriorates, characterized in that an aqueous solution containing a catalyst component that is eluted during washing is used at the end of the washing step. Activation method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56114419A JPS5817843A (en) | 1981-07-23 | 1981-07-23 | Activating method for catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56114419A JPS5817843A (en) | 1981-07-23 | 1981-07-23 | Activating method for catalyst |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5817843A true JPS5817843A (en) | 1983-02-02 |
| JPS6313734B2 JPS6313734B2 (en) | 1988-03-28 |
Family
ID=14637230
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP56114419A Granted JPS5817843A (en) | 1981-07-23 | 1981-07-23 | Activating method for catalyst |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5817843A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61102232U (en) * | 1984-12-11 | 1986-06-30 | ||
| CN105126568A (en) * | 2015-09-10 | 2015-12-09 | 杭州正清环保科技有限公司 | Multiphase strong oxygen catalytic reaction complete equipment for treating plastics and rubber waste gas |
| JP2023116431A (en) * | 2022-02-09 | 2023-08-22 | ソン・ホ・ホン | Filter regeneration device and method for denitrification equipment |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0371856A (en) * | 1989-08-11 | 1991-03-27 | Brother Ind Ltd | Piezoelectric element driven print head |
-
1981
- 1981-07-23 JP JP56114419A patent/JPS5817843A/en active Granted
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61102232U (en) * | 1984-12-11 | 1986-06-30 | ||
| CN105126568A (en) * | 2015-09-10 | 2015-12-09 | 杭州正清环保科技有限公司 | Multiphase strong oxygen catalytic reaction complete equipment for treating plastics and rubber waste gas |
| JP2023116431A (en) * | 2022-02-09 | 2023-08-22 | ソン・ホ・ホン | Filter regeneration device and method for denitrification equipment |
| JP2025036656A (en) * | 2022-02-09 | 2025-03-14 | ソン・ホ・ホン | Filter regeneration device and method for denitrification equipment |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6313734B2 (en) | 1988-03-28 |
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