JPS6049012B2 - How to regenerate denitrification catalyst - Google Patents
How to regenerate denitrification catalystInfo
- Publication number
- JPS6049012B2 JPS6049012B2 JP51118510A JP11851076A JPS6049012B2 JP S6049012 B2 JPS6049012 B2 JP S6049012B2 JP 51118510 A JP51118510 A JP 51118510A JP 11851076 A JP11851076 A JP 11851076A JP S6049012 B2 JPS6049012 B2 JP S6049012B2
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- exhaust gas
- denitrification
- reactor
- gas
- 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
- 239000003054 catalyst Substances 0.000 title claims description 63
- 239000007789 gas Substances 0.000 claims description 64
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims description 32
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 18
- 238000010438 heat treatment Methods 0.000 claims description 16
- 238000000034 method Methods 0.000 claims description 9
- 238000002485 combustion reaction Methods 0.000 claims description 8
- 230000008929 regeneration Effects 0.000 claims description 8
- 238000011069 regeneration method Methods 0.000 claims description 8
- 229910052815 sulfur oxide Inorganic materials 0.000 claims description 8
- 238000006243 chemical reaction Methods 0.000 claims description 6
- 230000001172 regenerating effect Effects 0.000 claims description 4
- 229910021529 ammonia Inorganic materials 0.000 claims description 3
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 claims description 3
- 238000011144 upstream manufacturing Methods 0.000 claims description 2
- 239000000203 mixture Substances 0.000 claims 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 9
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 9
- 235000011130 ammonium sulphate Nutrition 0.000 description 9
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 6
- 230000002378 acidificating effect Effects 0.000 description 5
- 230000000694 effects Effects 0.000 description 4
- 239000000446 fuel Substances 0.000 description 4
- 238000000605 extraction Methods 0.000 description 3
- 238000000354 decomposition reaction Methods 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000011049 filling Methods 0.000 description 2
- 239000002912 waste gas Substances 0.000 description 2
- 239000000571 coke Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J8/00—Chemical or physical processes in general, conducted in the presence of fluids and solid particles; Apparatus for such processes
- B01J8/08—Chemical or physical processes in general, conducted in the presence of fluids and solid particles; Apparatus for such processes with moving particles
- B01J8/12—Chemical or physical processes in general, conducted in the presence of fluids and solid particles; Apparatus for such processes with moving particles moved by gravity in a downward flow
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Devices And Processes Conducted In The Presence Of Fluids And Solid Particles (AREA)
Description
【発明の詳細な説明】
この発明は硫黄酸化物(SOx)と窒素酸化物(N0x
)を共に含有する排ガスの処理と触媒の再生をする方法
に関する。DETAILED DESCRIPTION OF THE INVENTION This invention is a method for treating sulfur oxides (SOx) and nitrogen oxides (NOx).
) and a method for treating exhaust gas and regenerating a catalyst.
S0xを含有する排ガスの脱硝処理に対してアンモニア
還元法を使用する場合には335〜320℃以下の排ガ
スに適用すること、 ・ 1止゛9← / KTUU
Cハ 、セ ZF、、斗μH力〔(Ni(、)。SO、
〕の生成があるため、触媒の活性の低下触媒の圧損上昇
等の悪影響を惹き起し長期安定運転ができないので採用
されていないのが現状である。この発明は低温脱硝によ
り生成した酸性硫安あるいは硫安が付着して脱硝機能が
低下した脱硝反応器の触媒の一部を350〜450℃、
好ましくは350〜400℃に昇温させ、付着物を分解
ガス化して除去し、脱硝機能を回復した触媒を脱硝用と
して再使用することを目的とする。When using the ammonia reduction method for denitrification treatment of exhaust gas containing SOx, it must be applied to exhaust gas of 335 to 320°C or lower. ・ 1 stop゛9← / KTUU
C Ha, Se ZF,, 斗μH force [(Ni(,).SO,
), which causes negative effects such as a decrease in catalyst activity and an increase in catalyst pressure loss, making long-term stable operation impossible, so it is currently not used. In this invention, a part of the catalyst of a denitrification reactor whose denitrification function has deteriorated due to the adhesion of acidic ammonium sulfate or ammonium sulfate produced by low-temperature denitrification is heated at 350 to 450°C.
Preferably, the temperature is raised to 350 to 400°C, the deposits are decomposed and gasified and removed, and the catalyst which has recovered its denitration function is intended to be reused for denitration.
第2図に250℃の低温度域における脱硝性能効率の時
間に対する変化状態の例を示す。FIG. 2 shows an example of how the denitrification performance efficiency changes over time in a low temperature range of 250°C.
即ち時間経過と共に脱硝率は徐々に低下しそのまま使用
する場合には比較的短時間て所期性能を維持てきなくな
ることを示す。これを脱硝効率の許容限度の点イで酸性
硫安等の分解温度以上(例えば400℃)に加熱保持す
るときは、初期の脱硝率値の口の点迄回復することを示
すものである。That is, the denitrification rate gradually decreases with the passage of time, and when used as is, it becomes impossible to maintain the desired performance in a relatively short period of time. This indicates that when this is heated and maintained at a temperature above the decomposition temperature of acidic ammonium sulfate (for example, 400° C.) at point A, which is the allowable limit of the denitrification efficiency, the denitrification rate is recovered to the initial point.
即ち(ハーイ)(ローニ)区J間は低温脱硝、(イーロ
)区間は加熱分解の処理期間であることを示すものであ
る。このような特性に基き、触媒を収容する反応器を用
いて一定時間使用後は性能劣化した触媒を加熱昇温処理
し触媒性能を回復させて繰返し使用すれは脱硝反応器口
こついて常時安定した脱硝性能を維持させることを可能
とするものてある。この発明の他の利点は、従来の触媒
加熱設備を小型化したものにできることである。In other words, the (hi) and (roni) sections J are for low-temperature denitrification, and the (euro) sections are for thermal decomposition. Based on these characteristics, after using a reactor containing a catalyst for a certain period of time, the catalyst whose performance has deteriorated is heated and heated to restore the catalyst performance and used repeatedly. There are things that make it possible to maintain denitrification performance. Another advantage of the invention is that it allows for miniaturization of conventional catalyst heating equipment.
脱硝触媒反応器の触媒の全量を同時に間欠的に速かに処
理しようとする場合にはその収容する触媒の全量を同時
に加熱する要があり、熱源としての資材設備を多く要す
ることと、反応器設備全体を高温時の条件に耐える設計
とせねばならぬこと等により経済的な手段でない。この
発明にかかる方法を実施するときは、加熱再生する触媒
の量は脱硝触媒反応器に収容する触媒の一部でよく従つ
て排ガス発生源からの要処理排ガスの4〜5%以下のガ
スをバイパスし加熱昇温すれば良く、設備並びに運転費
をいちぢるしく節減することを可能とするものてある。In order to treat the entire amount of catalyst in the denitrification catalyst reactor simultaneously and intermittently, it is necessary to heat the entire amount of catalyst contained therein at the same time, which requires a large amount of material and equipment as a heat source, and This is not an economical method because the entire equipment must be designed to withstand high temperature conditions. When carrying out the method according to the present invention, the amount of catalyst to be heated and regenerated may be a part of the catalyst contained in the denitrification catalyst reactor, so that less than 4 to 5% of the exhaust gas to be treated from the exhaust gas generation source is recovered. It is sufficient to bypass the heating and raise the temperature, making it possible to significantly reduce equipment and operating costs.
更にバイパスガスと触媒加熱処理後の排ガスとを熱交換
し熱回収をはかることによる省エネルギー化も可能て触
媒再生の熱源のための燃料費を低減することがてきる。Furthermore, it is possible to save energy by recovering heat by exchanging heat between the bypass gas and the exhaust gas after the catalyst heat treatment, and it is possible to reduce fuel costs for the heat source for catalyst regeneration.
なお好適なことには、触媒の加熱再生に際し触媒に付着
している硫安、酸性硫安を分解気化させてNH3ガスを
発生させ、前記バイパスした排ガス中に含まれるNOx
と反応させてH2O(5N2とし、触媒の加熱再生に際
して生する排ガス中のNOx,NH3を脱硝触媒の存在
下で同時に除去できるという一石二鳥の効果を挙げるこ
とができる。Preferably, during heating regeneration of the catalyst, ammonium sulfate and acidic ammonium sulfate adhering to the catalyst are decomposed and vaporized to generate NH3 gas, and the NOx contained in the bypassed exhaust gas is decomposed and vaporized.
By reacting with H2O (5N2), it is possible to simultaneously remove NOx and NH3 in the exhaust gas produced during heating regeneration of the catalyst in the presence of a denitrification catalyst, which can kill two birds with one stone.
以下図面によりこの発明につき説明する。第1図はこの
発明の実施にかかる装置及ひ配管を示すものである。The present invention will be explained below with reference to the drawings. FIG. 1 shows an apparatus and piping according to the present invention.
プラントのコークス炉、焼結機、ボイラ等のSOx及び
NOx含有ガス発生源を符.号1で示す。またこのガス
発生源にはこれらのガス発生源からの排ガスを低温脱硝
反応温度なる200〜300′C迄に昇温加熱する設備
を含むものとする。これらのガス発生源からの要処理排
ガスは、要処理排ガス管路2を通り、反応器3へと導か
れ;るが、この間で必要なNH3ガスを管路2aから注
入する。反応器3内には触媒層4があり排ガスを通過さ
せることにより脱硝を行なうものである。脱硝後排ガス
は排ガス出口ダクト5を通り、ファン6により吸引され
煙突7より大気放出される。上流側のガス圧力が触媒層
を通過するには充分なプラス圧力を有するものである場
合にはファン6は不要となる。第1図の実施例において
は、触媒層4の下部には触媒抜き出し装置9を設けられ
ており、これに接続して脱硝反応器の触媒の他の部分で
ある。Specify sources of gas containing SOx and NOx such as coke ovens, sintering machines, and boilers in plants. Indicated by No. 1. Further, this gas generation source shall include equipment for heating the exhaust gas from these gas generation sources to a temperature of 200 to 300'C, which is the low temperature denitrification reaction temperature. The waste gas to be treated from these gas generation sources passes through the waste gas to be treated pipe 2 and is led to the reactor 3; during this time, necessary NH3 gas is injected from the pipe 2a. There is a catalyst layer 4 in the reactor 3, which denitrates the exhaust gas by passing it therethrough. After denitration, the exhaust gas passes through an exhaust gas outlet duct 5, is sucked in by a fan 6, and is discharged into the atmosphere from a chimney 7. If the gas pressure on the upstream side is positive enough to pass through the catalyst layer, the fan 6 is not necessary. In the embodiment shown in FIG. 1, a catalyst extraction device 9 is provided at the bottom of the catalyst layer 4, and connected to this is another part of the catalyst of the denitrification reactor.
要再生触媒容器たる触媒加熱装置10を設けている。触
媒加熱装置10内の触媒には、付着した硫安、酸性硫安
ガス化除去するに必要な温度に昇温したガスが供給され
、性能の回復した触媒は触媒輸送装置11により反応器
上部に戻し触媒充填装置8により触媒層内へ戻される。A catalyst heating device 10 is provided as a catalyst container requiring regeneration. The catalyst in the catalyst heating device 10 is supplied with gas heated to a temperature necessary to gasify and remove the attached ammonium sulfate and acidic ammonium sulfate, and the catalyst whose performance has been recovered is returned to the upper part of the reactor by the catalyst transport device 11. It is returned into the catalyst bed by the filling device 8.
加熱用ガスは排フガス管路2より分岐するバイパスガス
ダクト12を通りガスブースターファン13で吸引され
バーナ19を有する燃焼炉14に送られる。なおバイパ
スガスの取り出し点はプラントのガス発生源1の高温ゾ
ーンからでもよく、その楊合燃焼炉19牡空気ファン1
7及び燃料系統は不用となる。燃焼炉14に於ては、前
記バイパスした排ガスを所要温度350〜450′Cま
で昇温させるため燃料(燃料の種類は規制しない)を燃
焼させて生じた排ガスと前記バイパスした排ガスと混合
し触媒加ノ熱装置10へ導き、その排ガスは更に排ガス
ダクト16を通し反応器出口排ガス5へ送りファン6経
由煙突7より排出する。なお排ガスタクト16に熱交換
器18を設けバイパスガスダクト12の排ガスと熱交換
を行えば更に運転コストの低減をはかることが可能であ
る。The heating gas passes through a bypass gas duct 12 branching from the exhaust gas pipe 2, is sucked in by a gas booster fan 13, and is sent to a combustion furnace 14 having a burner 19. Note that the bypass gas extraction point may be from the high-temperature zone of the gas generation source 1 of the plant;
7 and the fuel system will be unnecessary. In the combustion furnace 14, in order to raise the temperature of the bypassed exhaust gas to a required temperature of 350 to 450'C, the exhaust gas produced by burning fuel (the type of fuel is not regulated) is mixed with the bypassed exhaust gas and a catalyst is heated. The exhaust gas is further passed through an exhaust gas duct 16 to the reactor outlet exhaust gas 5 and discharged from a chimney 7 via a fan 6. Note that if a heat exchanger 18 is provided in the exhaust gas duct 16 to exchange heat with the exhaust gas of the bypass gas duct 12, it is possible to further reduce operating costs.
この発明は以下の特徴を有する。This invention has the following features.
即ち、硫黄酸化物と窒素酸化物を含有する燃焼排ガスを
触媒を有する脱硝触媒反応器てNOxを除去する方法に
おいて、この脱硝触媒反応器へ前記燃焼排ガスを供給す
る管路から、燃焼排ガスの一部を取り出し、触媒の再生
に好適な温度の排ガスとして脱硝触媒反応器内の触媒の
一部を収容することになる触媒加熱装置で加熱し、付着
している硫安、酸性硫安をガス化させ触媒を再生すると
ともに、分解により発生したNH3と加熱用ガス中のN
Oxとを触媒存在下で好適に反応させて除去し、装置の
小型化、省エネルギー触媒の再生による高効率運転をす
るという方法であることを特徴を有するものである。That is, in a method of removing NOx from a combustion exhaust gas containing sulfur oxides and nitrogen oxides using a denitrification catalyst reactor having a catalyst, part of the combustion exhaust gas is The sample is taken out and heated as exhaust gas at a temperature suitable for catalyst regeneration in a catalyst heating device that accommodates a part of the catalyst in the denitrification catalyst reactor, gasifying the attached ammonium sulfate and acidic ammonium sulfate and regenerating the catalyst. At the same time, NH3 generated by decomposition and N in the heating gas are
This method is characterized by removing Ox by suitably reacting in the presence of a catalyst, reducing the size of the device, and achieving high efficiency operation by regenerating the energy-saving catalyst.
この発明を実施することによりSOx,l5NOxを含
有する排ガス発生源からの排ガスが450′C以下の高
温てあるときはそのま)、350℃以下に温度低下して
いるときは加熱し、少ない量の加熱用ガスて脱硝反応器
の触媒の一部を、順次再生することができ、しかもその
再生に際して発生するNH3ガスを加熱ガス中のNOx
と脱硝触媒の存在下で有効に反応させ有害なリーク(漏
洩)NH3,NOxのないようにするとともに、省エネ
ルギーの効果を奏せしめることができる。By carrying out this invention, the exhaust gas containing SOx and NOx from the exhaust gas generation source is left as it is when the temperature is below 450'C, and when the temperature has dropped to below 350°C, it is heated and the amount is reduced. A part of the catalyst in the denitrification reactor can be sequentially regenerated using the heating gas, and the NH3 gas generated during the regeneration can be converted into NOx in the heating gas.
In the presence of a denitrification catalyst, the reaction can be carried out effectively to prevent harmful leaks of NH3 and NOx, and to achieve an energy-saving effect.
しかも脱硝反応器の運転をしていても触媒の再生ができ
、プラント排ガスの保有熱の有効利用によるプラント熱
効率の向上、SOxとNOxを含有する排ガスが処理で
き、煙突からの排ガス中のNOxをいちぢるしく少ない
ものにすることができる等種々の効果を奏するものであ
る。Moreover, the catalyst can be regenerated even when the denitrification reactor is operating, improving plant thermal efficiency by effectively utilizing the heat retained in the plant exhaust gas, and processing exhaust gas containing SOx and NOx, reducing NOx in the exhaust gas from the chimney. It has various effects such as being able to reduce the amount of space required.
第1図はこの発明の実施にかかる装置の配置と管系統を
示す図面、第2図はこの発明を実施したときの時間の経
過に伴う脱硝率の変化を示す線図である。
1・・・・・・SOx,NOX含有ガス発生源、2・・
・・・・要処理排ガス管路、3・・・・・・触媒を収容
する反応器、4・・・・触媒層、5・・・・・・排ガス
出口ダクト、6・・・・・・ファン、7・・・・・・煙
突、8・・・・・・触媒充填装置、9・・・・触媒抜き
出し装置、10・・・・・・触媒加熱装置、11・・・
・触媒輸送装置、12・・・・・・バイパスガスダクト
、13・・・・・・ガスブースタファン、14・・・・
・・燃焼炉、15・・・・・・ガスダクト、16・・・
・・・排出ガスダクト、17・・・・・・空気ファン、
18・・・・・・熱交換器、191001バニナ。FIG. 1 is a diagram showing the arrangement of the apparatus and the pipe system according to the present invention, and FIG. 2 is a diagram showing changes in the denitrification rate over time when the present invention is implemented. 1... SOx, NOX containing gas generation source, 2...
...Exhaust gas pipe line requiring treatment, 3...Reactor containing catalyst, 4...Catalyst layer, 5...Exhaust gas outlet duct, 6... Fan, 7... Chimney, 8... Catalyst filling device, 9... Catalyst extraction device, 10... Catalyst heating device, 11...
・Catalyst transport device, 12... Bypass gas duct, 13... Gas booster fan, 14...
... Combustion furnace, 15... Gas duct, 16...
...Exhaust gas duct, 17...Air fan,
18...Heat exchanger, 191001 Banina.
Claims (1)
、アンモニアを添加したのち、脱硝反応器中の循環移動
する触媒と接触させて、排ガス中の窒素酸化物を還元す
る方法において、上記脱硝反応器中の触媒で排ガスの通
路部分に位置するものについては、上記燃焼排ガスにア
ンモニアを添加したものを供給して脱硝反応を行なわせ
るとともに、上記脱硝反応器の排ガス通路外で該脱硝反
応器の下部に位置する触媒は、触媒加熱装置に導入して
、該脱硝反応器の上流より、上記燃焼排ガスの一部を分
岐して350〜450℃に昇温したのちの排ガスのみを
触媒加熱装置に供給することにより触媒再生反応を行な
わせ、該再生反応後の排ガスを、前記脱硝反応器の後流
排ガスダクトに導くとともに、再生された前記触媒は触
媒反応器の上部より再装入し循環使用することを特徴と
する脱硝触媒の再生方法。1. A method for reducing nitrogen oxides in the exhaust gas by adding ammonia to the combustion exhaust gas containing sulfur oxides and nitrogen oxides, and then bringing the mixture into contact with a circulating catalyst in a denitrification reactor. For the catalyst in the reactor located in the exhaust gas passage, ammonia added to the combustion exhaust gas is supplied to carry out the denitrification reaction, and the denitrification reaction is performed outside the exhaust gas passage of the denitrification reactor. The catalyst located at the bottom is introduced into a catalyst heating device, and a part of the combustion exhaust gas is branched from upstream of the denitrification reactor, and only the exhaust gas after being heated to 350 to 450°C is sent to the catalyst heating device. By supplying the catalyst, a catalyst regeneration reaction is performed, and the exhaust gas after the regeneration reaction is guided to the downstream exhaust gas duct of the denitrification reactor, and the regenerated catalyst is re-charged from the upper part of the catalyst reactor for circulation use. A method for regenerating a denitrification catalyst, characterized by:
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51118510A JPS6049012B2 (en) | 1976-10-04 | 1976-10-04 | How to regenerate denitrification catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51118510A JPS6049012B2 (en) | 1976-10-04 | 1976-10-04 | How to regenerate denitrification catalyst |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5343669A JPS5343669A (en) | 1978-04-19 |
| JPS6049012B2 true JPS6049012B2 (en) | 1985-10-30 |
Family
ID=14738414
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP51118510A Expired JPS6049012B2 (en) | 1976-10-04 | 1976-10-04 | How to regenerate denitrification catalyst |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6049012B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH057513U (en) * | 1991-07-17 | 1993-02-02 | 西川化成株式会社 | Vehicle trim mounting structure |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5451970A (en) * | 1977-09-30 | 1979-04-24 | Kobe Steel Ltd | Denitration method from gas containing sulphur oxide and nitrogen oxide |
-
1976
- 1976-10-04 JP JP51118510A patent/JPS6049012B2/en not_active Expired
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH057513U (en) * | 1991-07-17 | 1993-02-02 | 西川化成株式会社 | Vehicle trim mounting structure |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5343669A (en) | 1978-04-19 |
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