JPH0433492B2 - - Google Patents
Info
- Publication number
- JPH0433492B2 JPH0433492B2 JP62225271A JP22527187A JPH0433492B2 JP H0433492 B2 JPH0433492 B2 JP H0433492B2 JP 62225271 A JP62225271 A JP 62225271A JP 22527187 A JP22527187 A JP 22527187A JP H0433492 B2 JPH0433492 B2 JP H0433492B2
- Authority
- JP
- Japan
- Prior art keywords
- adsorbent
- inactivated
- heat exchange
- area
- inert 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 - Lifetime
Links
- 239000003463 adsorbent Substances 0.000 claims description 97
- 239000007789 gas Substances 0.000 claims description 47
- 239000011261 inert gas Substances 0.000 claims description 46
- 238000000926 separation method Methods 0.000 claims description 30
- 238000000034 method Methods 0.000 claims description 25
- 238000011069 regeneration method Methods 0.000 claims description 22
- 238000010438 heat treatment Methods 0.000 claims description 20
- 230000008929 regeneration Effects 0.000 claims description 14
- 230000001172 regenerating effect Effects 0.000 claims description 11
- 239000000126 substance Substances 0.000 claims description 10
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 8
- 239000003546 flue gas Substances 0.000 claims description 8
- 238000010926 purge Methods 0.000 claims description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 58
- 229910021529 ammonia Inorganic materials 0.000 description 29
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 16
- -1 hydrogen halides Chemical class 0.000 description 16
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 14
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 10
- 230000007797 corrosion Effects 0.000 description 10
- 238000005260 corrosion Methods 0.000 description 10
- 229910000039 hydrogen halide Inorganic materials 0.000 description 10
- 239000012433 hydrogen halide Substances 0.000 description 10
- 239000000047 product Substances 0.000 description 10
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 9
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 8
- 235000019270 ammonium chloride Nutrition 0.000 description 8
- 239000000463 material Substances 0.000 description 6
- 229910052736 halogen Inorganic materials 0.000 description 5
- 150000002367 halogens Chemical class 0.000 description 5
- 229910052739 hydrogen Inorganic materials 0.000 description 5
- 239000001257 hydrogen Substances 0.000 description 5
- 238000003860 storage Methods 0.000 description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 239000006227 byproduct Substances 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 238000001816 cooling Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- 150000003863 ammonium salts Chemical class 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 2
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 229910052815 sulfur oxide Inorganic materials 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- 230000005856 abnormality Effects 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 239000002826 coolant Substances 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 238000007689 inspection Methods 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000012261 overproduction Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Landscapes
- Separation Of Gases By Adsorption (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Carbon And Carbon Compounds (AREA)
Description
[産業上の利用分野]
本発明は燃焼排ガスを乾式脱硫又は乾式脱硝す
る装置に使用されて不活化した炭素質吸着剤の再
生方法に関する。さらに詳しくは、疲弊不活化し
た炭素質吸着剤がハロゲン成分を吸着している場
合でも、その炭素質吸着剤を支障なく安定に再生
できる方法に関する。
[従来技術とその問題点]
硫黄酸化物、窒素酸化物及びハロゲン化水素を
含有する排ガスにアンモニアを注入混合し、この
ガスを活性炭で代表される炭素質吸着剤と接触さ
せる乾式排煙処理法は、排ガスから硫黄酸化物、
窒素酸化物及びハロゲン化水素を同時に除去でき
る利点がある。この場合、排ガス中の硫黄酸化物
は硫酸又はそのアンモニウム塩として、ハロゲン
化水素はハロゲン化アンモニウムとしてそれぞれ
吸着剤に吸着され、一方、窒素酸化物は吸着剤の
触媒作用でアンモニアと反応し、窒素と水に転化
される。吸着剤は排ガスと長時間接触すると、上
記のような硫酸及びアンモニウム塩が吸着剤表面
に蓄積されるため、次第に不活化する。しかし、
この不活化吸着剤はこれを加熱することで再生す
ることができ、再生された吸着剤は前記した非煙
処理に再度使用することができる。そして、不活
化吸着剤の加熱再生に際しては、高濃度の二酸化
硫黄ガスが副生され、このガスからは硫酸、単体
硫黄などを回収することもできる。
ところで、排煙処理に使用されて疲弊不活化し
た炭素質吸着剤の再生方法としては、その吸着剤
を不活性ガス雰囲気中で加熱する方法が一般的で
あるが、そうした再生方法の好ましい一例は特許
第1315878号(特公昭60−37047号)で提案されて
いる。この特許の再生方法は、不活化吸着剤に不
活性ガスを混合し、この混合物を加熱領域に下向
きに流しながら当該領域を上向きに流れる加熱ガ
スと間接的に熱交換させて前記の混合物を加熱
し、この加熱によつて不活化吸着剤から離れる脱
離物を混合物中の不活性ガスでパージし、前記加
熱領域の下方に位置する分離領域に於いて、脱離
物含有不活性ガスと再生吸着剤とを分離するもの
である。
この再生方法によれば、不活化吸着剤からの脱
離物が、吸着剤と並流で流れる不活性ガスでパー
ジされ、より高温側に移動するので、脱離物中に
ハロゲン化水素が含まれている場合でも、ハロゲ
ン化アンモニウムの生成によつて再生装置が閉塞
される心配もなく、また腐食される虞れもない。
しかしながら、この再生方法では、再生吸着剤か
ら分離される脱離物含有不活性ガス中に、比較的
高濃度のアンモニアが混在してしまう不都合があ
る。ちなみに、不活化吸着剤の加熱再生時に副生
される上記の脱離物含有不活性ガスは、既述した
通り、これを硫酸乃至は単体硫黄回収プロセスに
供するのが通常であるが、ガス中にアンモニアが
混在している場合は、硫酸乃至は単体硫黄の回収
に先立つて、予め水洗等の手段によりガス中のア
ンモニアを除去しなければならない面倒がある。
特許第1313219号(特公昭60−34413号)には、
不活化吸着剤を上下2段の移動床として流下させ
ながら、上段の移動床では不活化吸着剤と第1ガ
ス流とを約150〜350℃の温度で接触させて第1ガ
ス流中のSO3とアンモニアを不活化吸着剤に捕捉
させることにより、実質的にSO3とアンモニアを
含まない高濃度二酸化硫黄ガスを回収すると共
に、SO3とアンモニアを捕捉した不活化吸着剤は
これを下段の移動床に移行させ、約300〜650℃の
昇温下に不活性ガスと接触させて再生し、再生時
に吸着剤から脱離するSO2、SO3及びアンモニア
等を不活性ガスに同伴させて、前記の第1ガス流
として上段の移動床に供給する不活化吸着剤の再
生方法が開示されている。
この方法の狙いの一つは、下段側移動床で不活
化吸着剤から脱離したSO3及びアンモニアを、上
段側の移動床で不活化吸着剤に捕捉させることに
より、上段側移動床から得られる高濃度二酸化硫
黄ガス中へのSO3及びアンモニアの混入を防止す
ることにあるが、ハロゲン成分を含有する不活化
吸着剤の再生にこの方法を適用した場合には、再
生装置の閉塞乃至は腐食を懸念しなければならな
い。何故なら、不活化吸着剤がハロゲン成分を含
有している場合は、不活化吸着剤の加熱再生時に
ハロゲン化水素が脱離するので、前記の第1ガス
流には当然のことながらハロゲン化水素も混在す
る。そして、この第1ガス流は上段の移動床に於
いて不活化吸着剤と約150〜350℃の温度で接触せ
しめられるが、再生に供する不活化吸着剤の温度
は、一般に90〜110℃程度であるため、上段の移
動床では部分的に設定温度より温度領域が発生し
易く、これが発生すると第1ガス流のハロゲン化
水素はアンモニアと反応してハロゲン化アンモニ
ウムが生成されて再生装置の閉塞又は腐食の原因
になるからである。
特開昭62−23440号には、また、不活化吸着剤
の加熱再生時に副生される二酸化硫黄含有ガス
を、アンモニアが混在しない状態で取得すること
ができる不活化吸着剤の再生方法が提案されてい
る。この方法は不活化吸着剤を熱交換領域の被加
熱側に下向きに通過させ、当該領域の加熱側を上
向きに流れる加熱ガスとの間接的熱交換により不
活化吸着剤を加熱再生し、再生された吸着剤を前
記熱交換領域の下方に位置する不活性ガス導入領
域に流下させ、この領域に供給される不活性ガス
にて吸着剤からの脱離物をパージし、脱離物を伴
う不活性ガスを熱交換領域の被加熱側を上昇さ
せ、熱交換領域の上方に位置する分離領域にて脱
離物を伴なう不活性ガスを吸着剤から分離するこ
とを特徴とする。
しかし、この方法もハロゲン成分を含有する不
活化吸着剤の再生に適用した場合には、先の特許
第1313219号に記載された再生方法の場合と同様、
ハロゲン化アンモニウムの生成に原因する再生装
置の閉塞乃至は腐食を心配しなければならない。
すなわち、特開昭62−23440号の再生方法は、吸
着剤からの脱離物を含有する不活性ガスを、温度
が低い分離領域に移行させて吸着剤から分離して
いるために、当該領域に於いて、ガス中のハロゲ
ン化水素とアンモニアが再び反応し、ハロゲン化
アンモニウムを生成し易いからである。
つまり、ハロゲン化水素を含有する燃焼排ガス
の処理に使用して不活化した吸着剤の再生法に於
いては、不活化吸着剤からの脱離物を含有する不
活性ガスを、比較的高温側で吸着剤から分離した
場合には、ハロゲン化アンモニウムの生成に原因
する再生装置の閉塞や腐食を心配する要がないも
のの、数千〜数万ppmの多量のアンモニアが前記
の不活性ガスに同伴されてしまう欠点がある。こ
れに対して、不活化吸着剤からの脱離物を含有す
る不活性ガスを、比較的低温側で吸着剤から分離
した場合には、このガスに伴われるアンモニア量
を低下させることができるものの、再生装置の閉
塞乃至は腐食を引き起こすハロゲン化アンモニウ
ムの生成を充分抑制することができないのであ
る。
しかして、本発明の目的は、再生せんとする不
活化吸着剤がハロゲン成分を含有している場合で
も、装置の閉塞乃至は腐食を懸念せずに、その不
活化吸着剤を安定的に再生することができ、しか
も再生時に副生される脱離物含有不活性ガス中の
アンモニア量も、これを500ppm程度以下の低水
準に保持できる不活化吸着剤の再生方法を提供す
ることにある。
[問題点を解決するための手段]
本発明の方法は、乾式排煙処理法に使用されて
不活化した炭素質吸着剤の再生方法に於いて、前
記の不活化吸着剤を第1熱交換領域の被加熱側に
下向きに流しながら、この領域の加熱側を流れる
加熱ガスとの間接的熱交換によつて不活化吸着剤
を予熱し、この不活化吸着剤を第1熱交換領域の
下方に位置する分離領域を介してその下方に位置
する第2熱交換領域の被加熱側に流下させ、この
領域の加熱側を上向きに流れる加熱ガスとの間接
的熱交換によつて不活化吸着剤を加熱再生した
後、第2熱交換領域の下方に位置する不活性ガス
導入領域に移行させ、この領域に導入される不活
性ガスにて、不活性吸着剤の加熱再生時に生ずる
脱離物をパージさせながら再生吸着剤を不活性ガ
ス導入領域の下部から取り出し、脱離物を伴う不
活性ガスを第2熱交換領域の被加熱側を上昇させ
て前記の分離領域に導き、ここで脱離物を伴う不
活性ガスを不活化吸着剤から分離することを特徴
とする。
本発明の一具体例を第1図にそつてさらに詳し
く説明すると、排煙の乾式処理に使用された不活
化した活性炭等の炭素質吸着剤は、再生器1の頂
部バルブV1を通して再生器内に供給される。こ
の不活化吸着剤は貯留領域2を経て、第1熱交換
領域3に流下するが、この熱交換領域にはほぼ垂
直に複数本の伝熱管4が配置されており、不活化
吸着剤はこの伝熱管内を、換言すれば第1熱交換
領域3の被加熱側を移動床として流下する。一
方、この熱交換領域の加熱側、すなわち伝熱管の
外側にはライン5から供給される加熱ガスが上向
きに通過せしめられるので、伝熱管4内を流下す
る不活化吸着剤は、この加熱ガスとの間接的熱交
換によつて約150〜220℃に予熱される。
予熱された不活化吸着剤は、次いで分離領域6
を経て第2熱交換領域7に流下する。この領域に
は第1熱交換領域と同様、複数本の伝熱管8がほ
ぼ垂直に配置され、不活化吸着剤はその伝熱管内
を移動床として流下する。一方、伝熱管8の外
側、すなわち、第2熱交換領域の加熱側には、ラ
イン9から供給される加熱ガスが上向きに通過せ
しめられるので、この加熱ガスとの間接的熱交換
によつて、管内の不活化吸着剤は約350〜500℃の
再生温度に加熱される。従つて、不活化吸着剤は
管内を流下する間にSO2,SO3,ハロゲン化水素
及びアンモニア等を離して再生され、不活性ガス
導入領域10に移行する。領域10にはライン1
1から不活性ガスが供給され、この不活性ガスは
SO2,SO3,ハロゲン化水素及びアンモニア等の
脱離物を吸着剤からパージし、これらを同伴しな
がら伝熱管8内を上昇し、約150〜220℃の不活化
吸着剤が滞留する分離領域6に供給された後、ラ
イン12から装置外に取り出される。
尚、脱離物を伴つて分離領域3に上昇したガス
が伝熱管4を経て貯留領域2に侵入した場合は、
結露などによる再生器の腐食が心配されるが、そ
うした場合には貯留領域2内に設けた整流体13
に近傍に、ライン14から不活性ガスを付加的に
供給することにより、脱離物を伴うガスの貯留領
域への侵入を防止することができる。
不活性ガス導入領域10で脱離物から開放され
た再生吸着剤は冷却領域15に流下し、適当な冷
却媒との間接的熱交換によつて冷却された後、バ
ルブV2を経て取り出され、排煙処理に再使用さ
れる。
[作用]
本発明方法の最大の特徴は、不活化吸着剤から
の脱離物を含有する不活性ガスが、第1熱交換領
域と第2熱交換領域との間に位置する分離領域に
於いて、吸着剤から分離される点にある。既述し
たところから明らかな通り、脱離物含有不活性ガ
スを吸着剤から分離する領域の温度は、再生装置
の閉塞及び腐食を防止し、且つ脱離物含有不活性
ガス中のアンモニア量を低水準に抑えるうえで重
要なフアクターであるが、本発明者等は、当該分
離領域の温度を150〜220℃、好ましくは170〜190
℃の範囲に保持することによつて、所期の目的が
達成されることを確認した。
本発明の方法によれば、不活化吸着剤は第1熱
交換領域で150〜220℃、好ましく170〜190℃に予
熱され、次いで分離領域を通過した後、第2熱交
換領域に流下し、ここで350〜500℃の再生温度に
加熱される。この加熱で不活化吸着剤中の硫酸、
硫酸アンモニウム、ハロゲン化アンモニウムなど
は次式に従つて分解し、吸着剤から脱離する。
2H2SO4+C→2SO2+CO2+2H2O (1)
3NH4HSO4→NH3+3SO2+N2+6H2O (2)
3(NH4)2SO4→4NH3+3SO2+N2+6H2O (3)
NH4X→NH3+HX (4)
また、ここで、分解生成したアンモニアは式(5)
に従う反応で、部分的に窒素に転化すると考えら
れる。
2NH3+3(0)→N2+3H2O (5)
第2熱交換領域から不活性ガス導入領域に流下
した吸着剤は、この領域に導入される不活性ガス
によつて脱離物からパージされ、冷却領域を経て
再生器の底部から取り出される。この吸着剤は吸
着能を回復しているので、再度排煙処理に使用す
ることができる。
一方、不活化吸着剤からの脱離物は不活性ガス
に伴われて第2熱交換領域を上昇し、分離領域に
達するが、この領域は第1熱交換領域と第2熱交
換領域にはさまれている関係で、150〜220℃の温
度範囲から外れることがない。従つて、この分離
領域に達したアンモニアは、第1熱交換領域から
流下する不活化吸着剤中の硫酸と次式に従つて反
応し、その一部は不活化吸着剤に吸収
NH3+H2SO4→NH4HSO4
NH4HSO4+NH3→(NH4)2SO4
される。ちなみに、第2図は分離領域の温度と当
該領域から系外に排出されるガス中のアンモニア
濃度との関係を示すグラフであつて、このグラフ
からも明らかな通り、本発明の方法に従う限り、
分離領域でのガス中のアンモニア濃度は、これを
実用上支障のない500ppmの範囲に保持すること
ができるのである。
また、分離領域に於けるガス中のハロゲン化水
素について言えば、一般に不活化吸着剤の加熱再
生法に於いて、パージに使用した不活性ガスに含
まれるハロゲン化水素の濃度は、燃焼排ガス中に
存在するハロゲン化水素濃度、排煙処理装置等に
よつても相違するが、数千〜数万ppm程度の範囲
にある。そして、ハロゲン化水素、典型的には塩
化水素とアンモニアから塩化アンモニウムが生成
される反応の理論平衡温度と、塩化アンモニウム
の生成率との関係は、第3図に示す通りであつ
て、温度の低下に伴なつて塩化アンモニウムの生
成率は上昇する。しかし、本発明の再生方法によ
れば、分離領域の気相中のアンモニア濃度は、上
記の通り、500ppm程度以下の範囲に保持され、
しかも分離領域の温度は150〜220℃、好ましく
170〜190℃の範囲に保持されるので、当該領域で
生成される塩化アンモニウムは、最大でもガス中
のアンモニアの数%程度に過ぎない。従つて、ハ
ロゲン化アンモニウムが分離領域で多量に生成さ
れることに原因する再生装置の閉塞及び腐食を、
本発明では実質的に回避することができる。
[実施例]
3000Nm3/hrのボイラ排ガスの排煙処理装置に
第1図に示す構成の再生装置を組み込み、活性炭
を65Kg/hrの割合で系内を循環させ、第2熱交換
領域7下端での活性炭の温度を390℃に、またラ
イン11及び14に供給する不活性ガス量を合計
で10Nm3/hrに保持して、排煙処理装置及び再生
装置の長期運転を行なつた。
この場合、ケース1,2では第1熱交換領域3
への加熱ガスの供給を止めて、ここを通過する不
活化活性炭の温度を90℃とし、ケース2,3,
4,5,6では第1熱交換領域3へ加熱ガスを供
給して、不活化活性炭をそれぞれ140℃,150℃,
170℃,190℃,220℃に予熱した。
ケース1,2ではそれぞれ約1ケ月及び約2ケ
月で第2熱交換領域の内圧が急上昇し、運転に支
障を来したので、運転を停止して分離領域の開放
点検を行なつた結果、当該領域及びガス出口ライ
ンに大量の塩化アンモニウムの結晶折出による閉
塞が認められた。
ケース3では約2ケ月後に分離領域の開放点検
を行なつたところ、この部分の塩化アンモニウム
の析出は運転に支障を来すほどのものではなかつ
た。
ケース4では約3ケ月後に、ケース5及び6で
はそれぞれ約1ケ月後に分離領域の開放点検をい
ずれの場合とも、異状は認められなかつた。
上記各ケースに於いて、分離領域から排出され
るガスの分析結果を、不活化活性炭の予熱温度と
共に次第に示す。
[Industrial Application Field] The present invention relates to a method for regenerating a carbonaceous adsorbent that has been inactivated and used in an apparatus for dry desulfurization or dry denitrification of combustion exhaust gas. More specifically, the present invention relates to a method that can stably regenerate a carbonaceous adsorbent without any trouble even when the carbonaceous adsorbent that has been exhausted and inactivated has adsorbed a halogen component. [Prior art and its problems] A dry flue gas treatment method in which ammonia is injected and mixed into exhaust gas containing sulfur oxides, nitrogen oxides, and hydrogen halides, and this gas is brought into contact with a carbonaceous adsorbent such as activated carbon. is sulfur oxide from exhaust gas,
It has the advantage of being able to remove nitrogen oxides and hydrogen halides at the same time. In this case, sulfur oxides in the exhaust gas are adsorbed as sulfuric acid or its ammonium salt, and hydrogen halides are adsorbed as ammonium halides, respectively, while nitrogen oxides react with ammonia due to the catalytic action of the adsorbent, resulting in nitrogen and is converted into water. When an adsorbent comes into contact with exhaust gas for a long period of time, the above-mentioned sulfuric acid and ammonium salts accumulate on the surface of the adsorbent, so that it becomes gradually inactivated. but,
This inactivated adsorbent can be regenerated by heating it, and the regenerated adsorbent can be used again for the non-smoke treatment described above. When the inactivated adsorbent is heated and regenerated, high-concentration sulfur dioxide gas is produced as a by-product, and sulfuric acid, elemental sulfur, and the like can also be recovered from this gas. By the way, a common method for regenerating carbonaceous adsorbents that have been exhausted and inactivated during flue gas treatment is to heat the adsorbents in an inert gas atmosphere.One preferred example of such a regeneration method is This was proposed in Patent No. 1315878 (Special Publication No. 60-37047). The regeneration method of this patent involves mixing an inert adsorbent with an inert gas and heating the mixture by flowing the mixture downward into a heating zone while indirectly exchanging heat with the heating gas flowing upward through the zone. The desorbed substances that leave the inactivated adsorbent due to this heating are purged with an inert gas in the mixture, and in the separation area located below the heating area, the desorbed substances are regenerated with the inert gas containing the desorbed substances. This separates the adsorbent from the adsorbent. According to this regeneration method, the desorbed material from the inactivated adsorbent is purged with an inert gas flowing in parallel with the adsorbent and moves to a higher temperature side, so hydrogen halide is contained in the desorbed material. Even in the case where the regenerator is used, there is no fear that the regenerator will be clogged by the formation of ammonium halides, and there is no risk of corrosion.
However, this regeneration method has the disadvantage that a relatively high concentration of ammonia is mixed in the desorbed product-containing inert gas separated from the regenerated adsorbent. Incidentally, as mentioned above, the above-mentioned inert gas containing desorbed products, which is produced as a by-product during thermal regeneration of the inactivated adsorbent, is normally subjected to a sulfuric acid or elemental sulfur recovery process. If ammonia is present in the gas, it is troublesome that the ammonia in the gas must be removed by washing with water or the like before recovering sulfuric acid or elemental sulfur. Patent No. 1313219 (Special Publication No. 60-34413)
While the inactivated adsorbent is flowing down in two moving beds, upper and lower, the inactivated adsorbent and the first gas stream are brought into contact with each other at a temperature of about 150 to 350°C in the upper moving bed to remove SO in the first gas stream. By trapping 3 and ammonia in the inactivated adsorbent, highly concentrated sulfur dioxide gas that does not substantially contain SO 3 and ammonia is recovered. The adsorbent is transferred to a moving bed and regenerated by contacting it with an inert gas at an elevated temperature of about 300 to 650°C, and SO 2 , SO 3 and ammonia, etc., which are desorbed from the adsorbent during regeneration, are entrained in the inert gas. , discloses a method for regenerating inactivated adsorbent which is fed to the upper moving bed as the first gas stream. One of the aims of this method is to capture SO 3 and ammonia desorbed from the inactivated adsorbent in the lower moving bed into the inactivated adsorbent in the upper moving bed. The purpose of this method is to prevent SO 3 and ammonia from being mixed into the high-concentration sulfur dioxide gas that is generated. However, when this method is applied to regenerating inactivated adsorbents containing halogen components, it may cause clogging of the regenerator or Corrosion must be a concern. This is because if the inactivated adsorbent contains a halogen component, the hydrogen halide will be desorbed during heating and regeneration of the inactivated adsorbent, so naturally the first gas flow will contain hydrogen halide. are also mixed. This first gas stream is brought into contact with the inactivated adsorbent in the upper moving bed at a temperature of about 150 to 350°C, but the temperature of the inactivated adsorbent used for regeneration is generally about 90 to 110°C. Therefore, in the upper moving bed, a temperature region that is higher than the set temperature tends to occur in some parts, and when this occurs, the hydrogen halide in the first gas stream reacts with ammonia to generate ammonium halide, which can clog the regenerator. Otherwise, it may cause corrosion. JP-A No. 62-23440 also proposes a method for regenerating inactivated adsorbents that can obtain sulfur dioxide-containing gas, which is produced as a by-product during heating and regeneration of inactivated adsorbents, without ammonia being mixed therein. has been done. In this method, the inactivated adsorbent is passed downward to the heated side of the heat exchange area, and the inactivated adsorbent is heated and regenerated by indirect heat exchange with the heated gas flowing upward in the heated side of the area. The adsorbent is caused to flow down into the inert gas introduction area located below the heat exchange area, and the inert gas supplied to this area purges the desorbed substances from the adsorbent, and the inert gas accompanied by the desorbed substances is removed. The method is characterized in that the active gas is raised on the heated side of the heat exchange region, and the inert gas accompanied by desorbed products is separated from the adsorbent in the separation region located above the heat exchange region. However, when this method is applied to the regeneration of an inactivated adsorbent containing a halogen component, as in the case of the regeneration method described in the previous patent No. 1313219,
There is concern about blockage or corrosion of the regenerator due to the formation of ammonium halides.
In other words, in the regeneration method of JP-A No. 62-23440, the inert gas containing desorbed substances from the adsorbent is separated from the adsorbent by moving it to the separation area where the temperature is lower. This is because the hydrogen halide and ammonia in the gas react again and tend to generate ammonium halide. In other words, in a method for regenerating an inactivated adsorbent used to treat combustion exhaust gas containing hydrogen halides, inert gas containing desorbed products from the inactivated adsorbent is transferred to a relatively high temperature side. If the inert gas is separated from the adsorbent, there is no need to worry about clogging or corrosion of the regenerator caused by the formation of ammonium halides, but a large amount of ammonia (several thousand to tens of thousands of ppm) will be entrained in the inert gas. There is a drawback that it can be done. On the other hand, if the inert gas containing desorbed products from the inactivated adsorbent is separated from the adsorbent at a relatively low temperature, the amount of ammonia accompanying this gas can be reduced. However, it is not possible to sufficiently suppress the production of ammonium halides that cause blockage or corrosion of the regenerator. Therefore, an object of the present invention is to regenerate the inactivated adsorbent stably without worrying about clogging or corrosion of the equipment, even if the inactivated adsorbent to be regenerated contains a halogen component. The object of the present invention is to provide a method for regenerating an inactivated adsorbent, which can also maintain the amount of ammonia in the desorbed inert gas by-produced during regeneration at a low level of about 500 ppm or less. [Means for Solving the Problems] The method of the present invention is a method for regenerating a carbonaceous adsorbent that has been inactivated by being used in a dry flue gas treatment method. Flowing downward into the heated side of the zone, the inactivated adsorbent is preheated by indirect heat exchange with the heated gas flowing on the heated side of this zone, and the inactivated adsorbent is transferred below the first heat exchange zone. The inactivated adsorbent is made to flow down through a separation region located at After heating and regenerating the adsorbent, the inert adsorbent is transferred to the inert gas introduction area located below the second heat exchange area, and the inert gas introduced into this area removes the desorbed substances generated during the heating regeneration of the inert adsorbent. While purging, the regenerated adsorbent is taken out from the lower part of the inert gas introduction region, and the inert gas with desorbed products is guided to the separation region by raising the heated side of the second heat exchange region, where it is desorbed. It is characterized by the separation of inert gases accompanied by substances from inert adsorbents. A specific example of the present invention will be explained in more detail with reference to FIG . supplied within. This inactivated adsorbent passes through the storage area 2 and flows down to the first heat exchange area 3. In this heat exchange area, a plurality of heat transfer tubes 4 are arranged almost vertically, and the inactivated adsorbent flows down into the first heat exchange area 3. In other words, it flows down the inside of the heat exchanger tube, using the heated side of the first heat exchange area 3 as a moving bed. On the other hand, the heated gas supplied from the line 5 is allowed to pass upward through the heating side of this heat exchange region, that is, the outside of the heat transfer tube, so that the inactivated adsorbent flowing down inside the heat transfer tube 4 is mixed with this heated gas. preheated to approximately 150-220°C by indirect heat exchange. The preheated inactivated adsorbent is then transferred to separation zone 6
and flows down to the second heat exchange area 7. In this region, like the first heat exchange region, a plurality of heat exchanger tubes 8 are arranged substantially vertically, and the inactivated adsorbent flows down as a moving bed inside the heat exchanger tubes. On the other hand, since the heated gas supplied from the line 9 is allowed to pass upwardly to the outside of the heat transfer tube 8, that is, to the heating side of the second heat exchange area, by indirect heat exchange with this heated gas, The inactivated adsorbent within the tube is heated to a regeneration temperature of approximately 350-500°C. Therefore, the inactivated adsorbent is regenerated by releasing SO 2 , SO 3 , hydrogen halide, ammonia, etc. while flowing down the pipe, and moves to the inert gas introduction region 10 . Line 1 in area 10
Inert gas is supplied from 1, and this inert gas is
Separation in which desorbed substances such as SO 2 , SO 3 , hydrogen halides, and ammonia are purged from the adsorbent, and they rise in the heat exchanger tube 8 while being accompanied by them, and the inactivated adsorbent remains at about 150 to 220°C. After being supplied to the region 6, it is taken out from the apparatus through a line 12. In addition, if the gas that has risen to the separation region 3 along with the desorbed materials enters the storage region 2 through the heat transfer tube 4,
There is a concern that the regenerator will corrode due to dew condensation, etc., but in such a case, the flow regulator 13 installed in the storage area 2
By additionally supplying an inert gas from the line 14 in the vicinity of the inert gas, it is possible to prevent gases accompanied by desorbed products from entering the storage region. The regenerated adsorbent freed from the desorbed material in the inert gas introduction zone 10 flows down to the cooling zone 15, where it is cooled by indirect heat exchange with a suitable coolant and then removed via valve V2 . , reused for flue gas treatment. [Operation] The most important feature of the method of the present invention is that the inert gas containing the desorbed product from the inactivated adsorbent is removed in the separation region located between the first heat exchange region and the second heat exchange region. at the point where it is separated from the adsorbent. As is clear from the above, the temperature in the area where the inert gas containing desorbed products is separated from the adsorbent is set to prevent clogging and corrosion of the regenerator and to reduce the amount of ammonia in the inert gas containing desorbed products. Although this is an important factor in keeping the temperature to a low level, the present inventors have determined that the temperature of the separation region is 150 to 220°C, preferably 170 to 190°C.
It was confirmed that the intended purpose could be achieved by maintaining the temperature within the range of ℃. According to the method of the invention, the inactivated adsorbent is preheated to 150-220°C, preferably 170-190°C in the first heat exchange zone, and then flows down into the second heat exchange zone after passing through the separation zone; Here it is heated to a regeneration temperature of 350-500°C. This heating inactivates the sulfuric acid in the adsorbent,
Ammonium sulfate, ammonium halides, etc. are decomposed according to the following formula and desorbed from the adsorbent. 2H 2 SO 4 +C→2SO 2 +CO 2 +2H 2 O (1) 3NH 4 HSO 4 →NH 3 +3SO 2 +N 2 +6H 2 O (2) 3(NH 4 ) 2 SO 4 →4NH 3 +3SO 2 +N 2 +6H 2 O ( 3 ) NH 4
It is thought that it is partially converted to nitrogen in the reaction according to the following. 2NH 3 +3(0)→N 2 +3H 2 O (5) The adsorbent that has flowed down from the second heat exchange area to the inert gas introduction area is purged from the desorbed material by the inert gas introduced into this area. is removed from the bottom of the regenerator via a cooling area. Since this adsorbent has recovered its adsorption capacity, it can be used again for flue gas treatment. On the other hand, the desorbed material from the inactivated adsorbent ascends through the second heat exchange region accompanied by the inert gas and reaches the separation region, but this region is separated from the first heat exchange region and the second heat exchange region. Because the temperature is between 150 and 220 degrees Celsius, the temperature does not exceed 150 to 220 degrees Celsius. Therefore, the ammonia that has reached this separation zone reacts with the sulfuric acid in the inactivated adsorbent flowing down from the first heat exchange zone according to the following formula, and a part of it is absorbed by the inactivated adsorbent. NH 3 + H 2 SO 4 →NH 4 HSO 4 NH 4 HSO 4 +NH 3 → (NH 4 ) 2 SO 4 . Incidentally, FIG. 2 is a graph showing the relationship between the temperature of the separation region and the ammonia concentration in the gas discharged from the region to the outside of the system, and as is clear from this graph, as long as the method of the present invention is followed,
The ammonia concentration in the gas in the separation region can be maintained within a range of 500 ppm, which does not pose a practical problem. Regarding hydrogen halide in the gas in the separation region, in general, in the heating regeneration method of inert adsorbent, the concentration of hydrogen halide contained in the inert gas used for purging is Although it varies depending on the hydrogen halide concentration present in the gas, the flue gas treatment equipment, etc., it is in the range of several thousand to tens of thousands of ppm. The relationship between the theoretical equilibrium temperature of the reaction in which ammonium chloride is produced from hydrogen halide, typically hydrogen chloride, and ammonia, and the production rate of ammonium chloride is as shown in Figure 3. As the concentration decreases, the production rate of ammonium chloride increases. However, according to the regeneration method of the present invention, the ammonia concentration in the gas phase of the separation region is maintained within a range of about 500 ppm or less, as described above.
Moreover, the temperature of the separation region is preferably 150 to 220℃.
Since the temperature is maintained in the range of 170 to 190°C, the ammonium chloride produced in this region is at most only a few percent of the ammonia in the gas. Therefore, blockage and corrosion of the regenerator due to large amounts of ammonium halides produced in the separation area can be avoided.
This can be substantially avoided with the present invention. [Example] A regenerator configured as shown in Fig. 1 was incorporated into a 3000Nm 3 /hr boiler exhaust gas treatment device, activated carbon was circulated through the system at a rate of 65Kg/hr, and the lower end of the second heat exchange area 7 was heated. The temperature of the activated carbon was maintained at 390° C., and the amount of inert gas supplied to lines 11 and 14 was maintained at a total of 10 Nm 3 /hr to carry out long-term operation of the flue gas treatment device and regeneration device. In this case, in cases 1 and 2, the first heat exchange area 3
Stop the supply of heating gas to the inactivated activated carbon passing through and set the temperature of the inactivated activated carbon to 90°C.
In steps 4, 5, and 6, heating gas is supplied to the first heat exchange area 3, and the inactivated activated carbon is heated to 140°C, 150°C, and 150°C, respectively.
Preheated to 170℃, 190℃, and 220℃. In Cases 1 and 2, the internal pressure in the second heat exchange area rose sharply after about one month and about two months, respectively, causing problems with operation.As a result of stopping operation and conducting an open inspection of the separation area, the problem occurred. Blockage due to large amounts of ammonium chloride crystal precipitation was observed in the area and gas outlet line. In Case 3, when the separation area was inspected after about two months, it was found that the ammonium chloride precipitation in this area was not large enough to cause any problems in operation. No abnormality was found in case 4 when the separated area was opened and inspected after about 3 months, and cases 5 and 6 after about 1 month. In each of the above cases, the analysis results of the gas discharged from the separation zone are shown in sequence along with the preheating temperature of the inactivated activated carbon.
【表】
[発明の効果]
本発明では不活化吸着剤の加熱再生時に不活化
吸着剤から脱離する成分を不活性ガスに同伴させ
て第2熱交換領域を上昇させ、この第2熱交換領
域より上位に位置し、第1熱交換領域より下位に
位置する分離領域にて、脱離含有不活性ガスを吸
着剤から分離しているため、当該領域でのハロゲ
ン化アンモニウムの生成を最少に留めることがで
き、従つて、ハロゲン化アンモニウムの過大生成
に原因する再生装置に閉塞乃至は腐食を回避する
ことができる。これに加えて、本発明の方法では
第2熱交換領域で不活化吸着剤から脱離したアン
モニアに一部が、上記の分離領域で不活化吸着剤
に捕捉されるので、分離領域から系外に排出され
るガス中のアンモニアは、これを低濃度に抑える
こともできる。[Table] [Effects of the Invention] In the present invention, the components desorbed from the inactivated adsorbent during heating regeneration of the inactivated adsorbent are entrained in the inert gas to raise the second heat exchange region, and the second heat exchange region is raised. Since the desorption-containing inert gas is separated from the adsorbent in the separation zone located above the first heat exchange zone and below the first heat exchange zone, the generation of ammonium halide in this zone is minimized. Therefore, blockage or corrosion of the regenerator due to overproduction of ammonium halide can be avoided. In addition, in the method of the present invention, some of the ammonia desorbed from the inactivated adsorbent in the second heat exchange area is captured by the inactivated adsorbent in the separation area, so it is removed from the system from the separation area. The concentration of ammonia in the gas emitted can also be kept low.
第1図は本発明方法を実施するのに適した再生
装置の縦断面図である。第2図は分離領域温度と
当該領域から排出されるガス中のアンモニア濃度
との関係を示すグラフである。第3図は塩化水素
とアンモニアから塩化アンモニウムが生成される
反応の理論平衡温度と、塩化アンモニウムの生成
率との関係を示すグラフである。
1……再生器、2……貯留領域、3……第1熱
交換領域、4……伝熱管、6……分離領域、7…
…第2熱交換領域、8……伝熱管、10……不活
性ガス導入領域、13……整流体、15……冷却
領域。
FIG. 1 is a longitudinal sectional view of a regeneration device suitable for carrying out the method of the invention. FIG. 2 is a graph showing the relationship between the separation region temperature and the ammonia concentration in the gas discharged from the region. FIG. 3 is a graph showing the relationship between the theoretical equilibrium temperature of the reaction in which ammonium chloride is produced from hydrogen chloride and ammonia and the production rate of ammonium chloride. DESCRIPTION OF SYMBOLS 1... Regenerator, 2... Storage area, 3... First heat exchange area, 4... Heat exchanger tube, 6... Separation area, 7...
...Second heat exchange region, 8...Heat transfer tube, 10...Inert gas introduction region, 13...Regulating fluid, 15...Cooling region.
Claims (1)
質吸着剤の再生方法に於いて、前記の不活化吸着
剤を第1熱交換領域の被加熱側に下向きに流しな
がら、この領域の加熱側を流れる加熱ガスとの間
接的熱交換によつて不活化吸着剤を予熱し、この
不活化吸着剤を第1熱交換領域の下方に位置する
分離領域を介してその下方に位置する第2熱交換
領域の被加熱側に流下させ、この領域の加熱側を
上向きに流れる加熱ガスとの間接的熱交換によつ
て不活化吸着剤を加熱再生した後、第2熱交換領
域の下方に位置する不活性ガス導入領域に移行さ
せ、この領域に導入される不活性ガスにて、不活
化吸着剤の加熱再生時に生ずる脱離物をパージさ
せながら再生吸着剤を不活性ガス導入領域の下部
から取り出し、脱離物を伴う不活性ガスを第2熱
交換領域の被加熱側を上昇させて前記の分離領域
に導き、ここで脱離物を伴う不活性ガスを不活化
吸着剤から分離することを特徴とする不活化吸着
剤の再生方法。1. In a method for regenerating a carbonaceous adsorbent that has been inactivated by being used in a dry flue gas treatment method, heating the first heat exchange area while flowing the inactivated adsorbent downward to the heated side of the first heat exchange area. The inactivated adsorbent is preheated by indirect heat exchange with a heated gas flowing along the side, and the inactivated adsorbent is transferred via a separation zone located below the first heat exchange zone to a second heat exchange zone located below it. After the inactivated adsorbent is heated and regenerated by indirect heat exchange with the heated gas flowing downward to the heated side of the heat exchange area and flowing upward on the heating side of this area, the inactivated adsorbent is placed below the second heat exchange area. The regenerated adsorbent is transferred from the lower part of the inert gas introduction area to the inert gas introduction area, and the inert gas introduced into this area purges the desorbed substances generated during heating and regeneration of the inactivated adsorbent. The inert gas accompanied by the desorbed product is guided to the separation region by raising the heated side of the second heat exchange region, where the inert gas accompanied by the desorbed product is separated from the inert adsorbent. A method for regenerating an inactivated adsorbent, characterized by:
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP62225271A JPS6470141A (en) | 1987-09-10 | 1987-09-10 | Method for regenerating flue gas treating adsorbent |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP62225271A JPS6470141A (en) | 1987-09-10 | 1987-09-10 | Method for regenerating flue gas treating adsorbent |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6470141A JPS6470141A (en) | 1989-03-15 |
| JPH0433492B2 true JPH0433492B2 (en) | 1992-06-03 |
Family
ID=16826708
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP62225271A Granted JPS6470141A (en) | 1987-09-10 | 1987-09-10 | Method for regenerating flue gas treating adsorbent |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6470141A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR2843705B1 (en) * | 2002-08-21 | 2005-07-22 | Conservatoire Nat Arts | METHOD AND DEVICE FOR REGENERATING AN ADSORBENT |
| JP2012030135A (en) * | 2008-11-28 | 2012-02-16 | J-Power Entech Inc | Regeneration tower for apparatus for dry discharge-gas treatment |
-
1987
- 1987-09-10 JP JP62225271A patent/JPS6470141A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6470141A (en) | 1989-03-15 |
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