JP2001179052A - Method and device for treating exhaust gas - Google Patents
Method and device for treating exhaust gasInfo
- Publication number
- JP2001179052A JP2001179052A JP37030599A JP37030599A JP2001179052A JP 2001179052 A JP2001179052 A JP 2001179052A JP 37030599 A JP37030599 A JP 37030599A JP 37030599 A JP37030599 A JP 37030599A JP 2001179052 A JP2001179052 A JP 2001179052A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- carbonaceous adsorbent
- powdery
- dust collector
- adsorbent
- 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
Links
- 238000000034 method Methods 0.000 title claims abstract description 18
- 239000003463 adsorbent Substances 0.000 claims abstract description 82
- 239000000428 dust Substances 0.000 claims abstract description 39
- 238000001179 sorption measurement Methods 0.000 claims abstract description 32
- 238000003795 desorption Methods 0.000 claims abstract description 14
- 239000002245 particle Substances 0.000 claims abstract description 11
- 239000003513 alkali Substances 0.000 claims abstract description 10
- 230000002378 acidificating effect Effects 0.000 claims abstract description 5
- 239000003795 chemical substances by application Substances 0.000 claims description 13
- 230000008929 regeneration Effects 0.000 claims description 13
- 238000011069 regeneration method Methods 0.000 claims description 13
- 238000002347 injection Methods 0.000 claims description 8
- 239000007924 injection Substances 0.000 claims description 8
- 230000000694 effects Effects 0.000 claims description 7
- 239000007787 solid Substances 0.000 claims description 7
- 150000004045 organic chlorine compounds Chemical class 0.000 claims description 6
- 239000007795 chemical reaction product Substances 0.000 claims description 5
- 230000001172 regenerating effect Effects 0.000 claims description 4
- 238000002485 combustion reaction Methods 0.000 claims 2
- 239000007789 gas Substances 0.000 abstract description 63
- 150000002013 dioxins Chemical class 0.000 abstract description 32
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 abstract description 6
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 abstract description 6
- 229910000041 hydrogen chloride Inorganic materials 0.000 abstract description 6
- 239000000126 substance Substances 0.000 abstract description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical class [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 64
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 12
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 7
- 239000000920 calcium hydroxide Substances 0.000 description 7
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 7
- 235000011116 calcium hydroxide Nutrition 0.000 description 7
- 159000000007 calcium salts Chemical class 0.000 description 4
- 229910052799 carbon Inorganic materials 0.000 description 4
- 230000000052 comparative effect Effects 0.000 description 4
- 230000007423 decrease Effects 0.000 description 3
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 230000000274 adsorptive effect Effects 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- 239000001110 calcium chloride Substances 0.000 description 2
- 229910001628 calcium chloride Inorganic materials 0.000 description 2
- 239000003575 carbonaceous material Substances 0.000 description 2
- 150000001805 chlorine compounds Chemical class 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000003814 drug Substances 0.000 description 2
- 229940079593 drug Drugs 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 239000011261 inert gas Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 239000010459 dolomite Substances 0.000 description 1
- 229910000514 dolomite Inorganic materials 0.000 description 1
- -1 for example Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 150000004679 hydroxides Chemical class 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 238000000465 moulding Methods 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- GPPXJZIENCGNKB-UHFFFAOYSA-N vanadium Chemical compound [V]#[V] GPPXJZIENCGNKB-UHFFFAOYSA-N 0.000 description 1
- 229910052720 vanadium Inorganic materials 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、排ガスの処理方法
及び装置に関し、特に、ダイオキシン類等の有害塩素化
合物を含有する排ガスの処理方法及び装置に関する。The present invention relates to a method and an apparatus for treating exhaust gas, and more particularly to a method and an apparatus for treating exhaust gas containing harmful chlorine compounds such as dioxins.
【0002】[0002]
【従来の技術】焼却炉、特に一般廃棄物の焼却炉の排ガ
スにはダイオキシン類やその前駆物質となる塩化水素等
が含まれる。こうした有害塩素化合物を除去する方法と
しては、特開平9−234333号公報や特開平11−
114374号公報に開示されているような消石灰と活
性炭粉を煙道内に注入し、消石灰と塩化水素との反応に
よって塩化カルシウムを生成して固形化するとともにダ
イオキシン類を活性炭によって吸着したのちに、固形物
をバグフィルター等の集塵器で除去する方法が知られて
いる。2. Description of the Related Art Exhaust gas from incinerators, particularly from general waste incinerators, contains dioxins and their precursors, such as hydrogen chloride. As a method for removing such a harmful chlorine compound, JP-A-9-234333 and JP-A-11-234333 are known.
Slaked lime and activated carbon powder as disclosed in Japanese Patent No. 114374 are injected into a flue, and calcium chloride is formed and solidified by the reaction of slaked lime and hydrogen chloride, and dioxins are adsorbed by activated carbon. A method of removing an object with a dust collector such as a bag filter is known.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、これら
の方法によれば、排ガス中のダイオキシン濃度が高い場
合には、大量の活性炭粉を注入する必要があるため、ラ
ンニングコストが増大するという欠点がある。同時に、
ダイオキシンを吸着した大量の活性炭粉の後処理も問題
となる。However, according to these methods, when the concentration of dioxin in the exhaust gas is high, a large amount of activated carbon powder needs to be injected, so that the running cost increases. . at the same time,
Post-treatment of a large amount of activated carbon powder adsorbing dioxin is also a problem.
【0004】本発明は上記の問題点に鑑みて、高濃度の
ダイオキシン類を含む排ガスからダイオキシン類を確実
に除去できるとともに、除去後の後処理も容易となる排
ガス処理方法及び装置を提供することを課題とする。[0004] In view of the above problems, the present invention provides an exhaust gas treatment method and apparatus which can surely remove dioxins from exhaust gas containing high concentrations of dioxins and also facilitate post-treatment after removal. As an issue.
【0005】[0005]
【課題を解決するための手段】上記課題を解決するた
め、本発明に係る排ガス処理方法は、(1)排ガス中に
アルカリ薬剤を添加して、この排ガス中の酸性成分と反
応させて固形の反応生成物を得る工程と、(2)この反
応生成物を含む固形分を集塵器により除去する工程と、
(3)集塵器を通過した排ガス中に粉状の炭素質吸着剤
を注入して粒子状の有機塩素化合物をこの炭素質吸着剤
に吸着させる工程と、(4)粉状の炭素質吸着剤を含む
排ガスを粒状の炭素質吸着剤が充填されている移動層式
の吸着塔に導いて通過させることにより、粉状の炭素質
吸着剤と排ガス中のガス状の有機塩素化合物を除去する
工程と、(5)吸着塔から取り出した炭素質吸着剤を脱
離・再生する工程と、(6)脱離・再生後の粒状の炭素
質吸着剤を吸着塔に返送する工程と、を備えていること
を特徴とする。In order to solve the above problems, the exhaust gas treatment method according to the present invention comprises the steps of (1) adding an alkali agent to exhaust gas and reacting with an acidic component in the exhaust gas to form a solid. A step of obtaining a reaction product; and (2) a step of removing solids containing the reaction product by a dust collector;
(3) a step of injecting a powdery carbonaceous adsorbent into the exhaust gas passing through the dust collector to adsorb particulate organic chlorine compounds onto the carbonaceous adsorbent; and (4) adsorbing the powdery carbonaceous substance. The exhaust gas containing the adsorbent is passed through a moving bed type adsorption tower filled with a granular carbonaceous adsorbent to remove the powdery carbonaceous adsorbent and gaseous organic chlorine compounds in the exhaust gas. And (5) a step of desorbing and regenerating the carbonaceous adsorbent taken out of the adsorption tower, and (6) a step of returning the desorbed and regenerated particulate carbonaceous adsorbent to the adsorption tower. It is characterized by having.
【0006】一方、本発明に係る排ガス処理装置は、
(1)排ガス中にアルカリ薬剤を添加するアルカリ薬剤
添加手段と、(2)アルカリ薬剤添加後の排ガスが導か
れる集塵器と、(3)集塵器を通過した排ガス中に粉状
の炭素質吸着剤を注入する炭素質吸着剤注入手段と、
(4)粒状の炭素質吸着剤が充填されており、粉状の炭
素質吸着剤注入後の排ガスが導かれる移動層式の吸着塔
と、(5)吸着塔から取り出された炭素質吸着剤を脱離
・再生する脱離・再生器と、(6)脱離・再生後の粒状
の炭素質吸着剤を吸着塔に返送する第一の返送手段と、
を備えていることを特徴とする。On the other hand, an exhaust gas treatment apparatus according to the present invention
(1) an alkali agent adding means for adding an alkali agent to the exhaust gas; (2) a dust collector to which the exhaust gas after the addition of the alkali agent is guided; and (3) a powdery carbon in the exhaust gas passing through the dust collector. Carbonaceous adsorbent injection means for injecting the porous adsorbent,
(4) a moving bed type adsorption tower which is filled with a granular carbonaceous adsorbent and into which exhaust gas after injection of a powdery carbonaceous adsorbent is introduced; and (5) a carbonaceous adsorbent taken out of the adsorption tower A desorber / regenerator for desorbing / regenerating carbon, (6) first returning means for returning the desorbed / regenerated granular carbonaceous adsorbent to the adsorption tower,
It is characterized by having.
【0007】本発明によれば、排ガス中にアルカリ薬剤
を添加することで、まず、塩化水素等の酸性成分がアル
カリ薬剤と反応して固形の反応生成物を生成し、集塵器
により除去される。この集塵器で集められた固形分には
ダイオキシン類はほとんど含まれないので後処理は容易
である。処理後の排ガスに粉状の炭素質吸着剤を注入す
ることで、排ガス中のダイオキシン類のうち、主として
粒子状のダイオキシン類がこの粉状の炭素質吸着剤に吸
着される。続いて、この排ガスを移動層式の吸着塔へと
導くことにより、排ガス中のダイオキシン類のうち残る
ガス状のダイオキシン類が吸着塔内の粒子状の炭素質吸
着剤に吸着されるとともに、粒子状のダイオキシン類を
吸着している粉状の炭素質吸着剤も吸着除去される。ダ
イオキシン類を吸着した炭素質吸着剤を脱離・再生塔で
加熱することで、ダイオキシン類は熱分解され、炭素質
吸着剤の再生も行われる。ダイオキシン類の全てを粉状
の炭素質吸着剤で吸着する必要がないので、ダイオキシ
ン類の濃度が高い場合でも粉状の炭素質吸着剤の投入量
が少なくて済む。また、排ガスからの除去後の固形物、
炭素質吸着剤の後処理が容易となる。According to the present invention, by adding an alkaline agent to exhaust gas, first, an acidic component such as hydrogen chloride reacts with the alkaline agent to produce a solid reaction product, which is removed by the dust collector. You. Since the solids collected by this dust collector hardly contain dioxins, post-treatment is easy. By injecting the powdery carbonaceous adsorbent into the exhaust gas after the treatment, among the dioxins in the exhaust gas, mainly particulate dioxins are adsorbed by the powdery carbonaceous adsorbent. Subsequently, by guiding this exhaust gas to a moving bed type adsorption tower, the remaining gaseous dioxins of the dioxins in the exhaust gas are adsorbed by the particulate carbonaceous adsorbent in the adsorption tower, The powdery carbonaceous adsorbent that adsorbs dioxins in the form of particles is also adsorbed and removed. By heating the carbonaceous adsorbent having adsorbed dioxins in the desorption / regeneration tower, the dioxins are thermally decomposed and the carbonaceous adsorbent is also regenerated. Since it is not necessary to adsorb all of the dioxins with the powdery carbonaceous adsorbent, even when the concentration of dioxins is high, the amount of the powdery carbonaceous adsorbent to be used is small. Also, solid matter after removal from exhaust gas,
Post-treatment of the carbonaceous adsorbent becomes easy.
【0008】本発明は、脱離・再生後の炭素質吸着剤を
粒径により区分する工程をさらに備え、分離した粉状の
炭素質吸着剤を集塵器を通過した排ガス中に注入する排
ガス処理方法、脱離・再生後の炭素質吸着剤を粒径によ
り区分する分離手段と、分離した粉状の炭素質吸着剤を
炭素質吸着剤注入手段へと導く第二の返送手段と、をさ
らに備えている排ガス処理装置であってもよい。粉状の
炭素質吸着剤を脱離・再生後に再使用することにより、
さらにランニングコストを下げることができる。[0008] The present invention further comprises a step of separating the desorbed and regenerated carbonaceous adsorbent according to the particle size, and injecting the separated powdery carbonaceous adsorbent into the exhaust gas passing through the dust collector. A treatment method, separation means for separating the desorbed / regenerated carbonaceous adsorbent by particle size, and second return means for guiding the separated powdery carbonaceous adsorbent to the carbonaceous adsorbent injection means, An exhaust gas treatment device further provided may be used. By reusing the powdery carbonaceous adsorbent after desorption and regeneration,
Further, running costs can be reduced.
【0009】集塵器を通過した排ガス中に高活性を有す
る新品の粉状炭素質吸着剤を追加注入する排ガス処理方
法、高活性を有する新品の粉状炭素質吸着剤を炭素質吸
着剤注入手段に導く炭素質吸着剤供給手段をさらに備え
ている排ガス処理装置であってもよい。再生された炭素
質吸着剤は、再生に伴い吸着性能が低下するが、高活性
の炭素質吸着剤を追加投入することで、全体的な吸着性
能を維持することが可能となる。An exhaust gas treatment method for additionally injecting a new powdery carbonaceous adsorbent having high activity into exhaust gas passing through a dust collector, and injecting a new powdery carbonaceous adsorbent having high activity into carbonaceous adsorbent The exhaust gas treatment apparatus may further include a carbonaceous adsorbent supply unit for leading the unit. The adsorptive performance of the regenerated carbonaceous adsorbent decreases with regeneration, but by additionally introducing a highly active carbonaceous adsorbent, the overall adsorptive performance can be maintained.
【0010】[0010]
【発明の実施の形態】以下、添付図面を参照して本発明
の好適な実施の形態について詳細に説明する。図1は、
本発明に係る排ガス処理装置の好適な実施形態を示す概
略図である。Preferred embodiments of the present invention will be described below in detail with reference to the accompanying drawings. FIG.
It is a schematic diagram showing a preferred embodiment of an exhaust gas treatment device according to the present invention.
【0011】この装置は、集塵器10と吸着反応器20
と煙突30とがラインL11とL12により直列に接続
されて構成されている。集塵器10にはラインL10を
介して処理対象の排ガスが導入されるものであり、例え
ばバグフィルタや電気式集塵器などの乾式集塵器であ
る。ラインL10には、アルカリ薬剤供給装置40から
アルカリ薬剤を導入するラインL30が接続されてい
る。このアルカリ薬剤としては例えば、消石灰(Ca(OH)
2)が用いられる。一方、ラインL11には、炭素質吸
着剤供給装置23から粉状の炭素質吸着剤、例えば平均
粒径が1mm以下の活性炭を導入するラインL25が接
続されている。そして、この炭素質吸着剤供給装置23
は、炭素質吸着剤貯留タンク24とラインL24で接続
されている。The apparatus comprises a dust collector 10 and an adsorption reactor 20.
And the chimney 30 are connected in series by lines L11 and L12. Exhaust gas to be treated is introduced into the dust collector 10 via a line L10, and is, for example, a dry dust collector such as a bag filter or an electric dust collector. The line L30 is connected to a line L30 for introducing an alkaline drug from the alkaline drug supply device 40. For example, slaked lime (Ca (OH)
2 ) is used. On the other hand, a line L25 for introducing a powdery carbonaceous adsorbent, for example, activated carbon having an average particle diameter of 1 mm or less, from the carbonaceous adsorbent supply device 23 is connected to the line L11. And this carbonaceous adsorbent supply device 23
Is connected to the carbonaceous adsorbent storage tank 24 by a line L24.
【0012】吸着反応器20は内部に粒状の炭素質吸着
剤、例えば平均粒径が4mm以上、好ましくは8〜9m
mの活性炭が充填されており、これを導入された排ガス
と直交する方向に移動させながら排ガスと接触させる直
交流移動層式の吸着反応器である。吸着反応器20の下
部はラインL20を介して脱離・再生器21へと接続さ
れる。脱離・再生器21は、導入された活性炭を移動さ
せながら不活性ガス雰囲気中で加熱する構造を有する。
この脱離・再生器21は、ラインL21を介して分離器
22に接続されている。分離器22は、導入された活性
炭を粒径に応じて粒状の活性炭と粉状の活性炭とに分離
するものであり、粒状の活性炭を吸着反応器22へ戻す
ラインL22と粉状の活性炭を炭素質吸着剤供給装置へ
と導くラインL23とが接続されている。さらに、脱離
・再生器21から延びるガスラインL40は、ラインL
10のラインL30との接続部より上流に接続されてい
る。The adsorption reactor 20 contains therein a particulate carbonaceous adsorbent, for example, having an average particle diameter of 4 mm or more, preferably 8 to 9 m.
This is a cross-flow moving bed type adsorption reactor in which m activated carbons are filled, and the activated carbon is brought into contact with the exhaust gas while being moved in a direction orthogonal to the introduced exhaust gas. The lower part of the adsorption reactor 20 is connected to a desorption / regeneration unit 21 via a line L20. The desorption / regeneration unit 21 has a structure in which the introduced activated carbon is moved and heated in an inert gas atmosphere.
The desorber / regenerator 21 is connected to a separator 22 via a line L21. The separator 22 separates the introduced activated carbon into granular activated carbon and powdered activated carbon in accordance with the particle size. A line L22 for returning the granular activated carbon to the adsorption reactor 22 and a powder L L23 leading to the adsorbent supply device. Further, the gas line L40 extending from the desorption / regeneration unit 21 is a line L40.
They are connected upstream from the connection with the ten lines L30.
【0013】続いて、本実施形態の動作、すなわち、本
発明に係る排ガス処理方法について説明する。ラインL
10を流れる排ガスにアルカリ薬剤供給装置40からラ
インL30を介して消石灰が導入される。これにより、
排ガス中の酸性ガス、特に塩化水素と消石灰が反応して
不溶性の塩化カルシウムを始めとするカルシウム塩が生
成され、ガス中で固形化する。こうして処理した排ガス
を集塵器10に導いて通過させることにより、排ガス中
のダストと固形化された酸性ガス成分が除去される。除
去したダストとカルシウム塩は別途処理される。このと
き、ダスト、カルシウム塩中には、ダイオキシン類がほ
とんど含まれないのでその後処理は容易である。Next, the operation of this embodiment, that is, the exhaust gas treatment method according to the present invention will be described. Line L
Slaked lime is introduced into the exhaust gas flowing through the line 10 from the alkaline chemical supply device 40 via the line L30. This allows
The acid gas in the exhaust gas, particularly hydrogen chloride, reacts with slaked lime to produce insoluble calcium chloride and other calcium salts, which are solidified in the gas. The exhaust gas thus treated is guided to the dust collector 10 and passed therethrough, thereby removing dust and solidified acidic gas components in the exhaust gas. The removed dust and calcium salt are treated separately. At this time, since dioxins are hardly contained in the dust and calcium salt, the subsequent treatment is easy.
【0014】集塵器10を通過した排ガスはラインL1
1を流れる間に、炭素質吸着剤供給装置23からライン
L25を介して送られる活性炭粉と混合される。これに
より、排ガス中の主として粒子状のダイオキシン類が活
性炭粉に吸着される。処理後の排ガスは吸着反応器20
へと導入され、活性炭粉と排ガス中に残っているガス状
のダイオキシン類が吸着反応器20内の粒状の活性炭の
表面に付着あるいは吸着される。この結果、ダイオキシ
ン類の大部分を除去することができる。こうして処理さ
れた排ガスは、ラインL12、煙突30を介して大気中
へと放出される。The exhaust gas passing through the dust collector 10 is supplied to a line L1.
During the flow through 1, the mixture is mixed with activated carbon powder sent from the carbonaceous adsorbent supply device 23 via the line L25. Thereby, mainly particulate dioxins in the exhaust gas are adsorbed on the activated carbon powder. The exhaust gas after treatment is supplied to the adsorption reactor 20
The activated carbon powder and the gaseous dioxins remaining in the exhaust gas are adhered or adsorbed on the surface of the granular activated carbon in the adsorption reactor 20. As a result, most of the dioxins can be removed. The exhaust gas thus treated is discharged into the atmosphere via the line L12 and the chimney 30.
【0015】吸着反応器20内でダイオキシン類を吸着
した活性炭(活性炭粉を含む)は、ラインL20を介し
て脱離・再生器21へと送られ、不活性ガス中で加熱さ
れることにより、吸着されていたダイオキシン類を始め
とする有害物質が脱離・分解されることで、活性炭自体
が再生される。塩素ガス、亜硫酸ガス等を含む脱離ガス
は、ラインL40を介してラインL10へと送られ、ア
ルカリ薬剤の添加によってカルシウム塩として固形化さ
れ、集塵器10で回収・除去される。Activated carbon (including activated carbon powder) having adsorbed dioxins in the adsorption reactor 20 is sent to a desorption / regeneration unit 21 via a line L20 and is heated in an inert gas. Activated carbon itself is regenerated by desorbing and decomposing harmful substances such as adsorbed dioxins. The desorbed gas containing chlorine gas, sulfurous acid gas and the like is sent to the line L10 via the line L40, solidified as a calcium salt by the addition of an alkali agent, and collected and removed by the dust collector 10.
【0016】再生された活性炭(活性炭粉を含む)は、
分離器22へ送られ、粒状の活性炭と粉状の活性炭とに
分けられる。粒状の活性炭はラインL22を介して吸着
反応器20の上部へと戻されることで循環され、粉状の
活性炭はラインL23を介して炭素質吸着剤供給装置2
3へと戻されることで、こちらも循環される。活性炭は
脱離・再生に伴い吸着性能が低下するため、その性能低
下を補償するため、新品の高活性の活性炭粉を炭素質吸
着剤貯留タンク24からラインL24を介して炭素質吸
着剤供給装置23へと供給することが好ましい。Regenerated activated carbon (including activated carbon powder)
It is sent to the separator 22 and is divided into granular activated carbon and powdered activated carbon. The granular activated carbon is circulated by returning to the upper part of the adsorption reactor 20 via the line L22, and the powdered activated carbon is circulated through the line L23.
This is circulated by returning to 3. Since the adsorption performance of activated carbon decreases with desorption / regeneration, a new high-activity activated carbon powder is supplied from the carbonaceous adsorbent storage tank 24 to the carbonaceous adsorbent supply device via the line L24 in order to compensate for the decrease in performance. 23.
【0017】本発明では、粒状のダイオキシン類の除去
効率が高い活性炭粉とガス状のダイオキシン類の除去効
率が高い粒状の活性炭とを併用することにより、粒状、
ガス状いずれのダイオキシン類も効率良く除去すること
ができるとともに、活性炭粉、粒状の活性炭を単独で使
用する場合に比べてそれぞれの使用量を減らすことがで
き、装置もコンパクトなもので済むという利点が有る。In the present invention, the use of activated carbon powder having a high removal efficiency of particulate dioxins and granular activated carbon having a high removal efficiency of gaseous dioxins is used in combination to obtain granular,
The advantage is that gaseous dioxins can be efficiently removed, and the amount of each used can be reduced compared to the case where activated carbon powder and granular activated carbon are used alone, and the equipment can be compact. There is.
【0018】活性炭粉は本実施形態のように循環させる
ことなく、使用済みの活性炭粉を焼却炉に導いて処理し
てもよい。また、ダイオキシン濃度が高くない場合に
は、新品の活性炭の追加は省いてもよい。Instead of circulating the activated carbon powder as in this embodiment, the used activated carbon powder may be guided to an incinerator for treatment. If the dioxin concentration is not high, the addition of new activated carbon may be omitted.
【0019】炭素質吸着剤としては、石炭等の炭素含有
物質にバインダーを添加して成形後、熱処理又は水蒸
気、空気などで賦活して得られた活性炭、活性コーク
ス、活性チャー、あるいは、これらにバナジウム、鉄、
銅等の化合物を担持させた炭素質吸着剤を好適に用いる
ことができる。また、アルカリ薬剤としては、カルシウ
ム、マグネシウムの水酸化物、これらの酸化物、これら
の炭酸塩あるいは石灰石、ドロマイト等のこれらの化合
物を含む鉱物やダストを用いることができる。As the carbonaceous adsorbent, activated carbon, activated coke, activated char obtained by adding a binder to a carbon-containing substance such as coal, molding, and then heat-treating or activating with steam, air, or the like; Vanadium, iron,
A carbonaceous adsorbent supporting a compound such as copper can be suitably used. In addition, as the alkaline agent, hydroxides of calcium and magnesium, oxides thereof, carbonates thereof, and minerals and dusts containing these compounds such as limestone and dolomite can be used.
【0020】[0020]
【実施例】本発明者は、本発明に係る排ガス処理装置及
び排ガス処理方法のダイオキシン除去効率の向上及び炭
素質吸着剤の使用量低減効果を確認する比較実験を行っ
たので、以下、その結果について説明する。EXAMPLE The present inventor conducted a comparative experiment to confirm the improvement of dioxin removal efficiency and the effect of reducing the amount of carbonaceous adsorbent of the exhaust gas treatment apparatus and the exhaust gas treatment method according to the present invention. Will be described.
【0021】実施例 図1に示される装置でダイオキシン類を80ng/m3
(Normal)含む排ガス(約40000m3/h)に消石
灰を0.8〜1.6g/m3(Normal)投入し、活性炭
粉(平均粒径15μm)を80〜100mg/m3(Nor
mal)投入して処理した。吸着反応器には、平均粒径4
mmの粒状活性炭を40000リットル充填し、その滞
留時間は300〜600時間とした。脱離・再生器で
は、400〜450℃で滞留時間1〜2時間で処理し
た。Example 1 Dioxins were 80 ng / m 3 in the apparatus shown in FIG.
(Normal) including an exhaust gas (about 40000m 3 / h) to the slaked lime 0.8~1.6g / m 3 (Normal) was charged activated carbon powder (average particle diameter 15μm) 80~100mg / m 3 (Nor
mal) Input and processed. The adsorption reactor has an average particle size of 4
40000 liters of granular activated carbon having a diameter of 3 mm were filled, and the residence time was 300 to 600 hours. In the desorption / regeneration unit, the treatment was performed at 400 to 450 ° C. for a residence time of 1 to 2 hours.
【0022】集塵器で回収したダスト中のダイオキシン
濃度は0.05〜0.1ng/gダスト、吸着反応器通
過後のダイオキシン濃度は検出限界の0.016ng/
m3(Normal)以下であり、脱離・再生器での分解率は
99.9%であった。The dioxin concentration in the dust collected by the dust collector is 0.05 to 0.1 ng / g dust, and the dioxin concentration after passing through the adsorption reactor is 0.016 ng / g, which is the detection limit.
m 3 (Normal) or less, and the decomposition rate in the desorption / regeneration unit was 99.9%.
【0023】比較例1 消石灰と活性炭粉を混合して実施例と同一組成、流量の
排ガスに導入して集塵器で回収処理した。集塵器で回収
したダスト中のダイオキシン濃度は0.5ng/gダス
ト、集塵器通過後のダイオキシン濃度は3〜8ng/m
3(Normal)であった。処理後の排ガス中のダイオキシ
ン濃度を実施例と同等に低下させるために、必要な活性
炭粉の注入量は300〜350mg/m3(Normal)
で、実施例の3〜4倍必要であった。Comparative Example 1 Slaked lime and activated carbon powder were mixed, introduced into an exhaust gas having the same composition and flow rate as in the example, and recovered by a dust collector. The dioxin concentration in the dust collected by the dust collector is 0.5 ng / g dust, and the dioxin concentration after passing through the dust collector is 3 to 8 ng / m.
3 (Normal). In order to reduce the dioxin concentration in the exhaust gas after the treatment to the same level as in the examples, the required injection amount of activated carbon powder is 300 to 350 mg / m 3 (Normal).
Therefore, it was required to be three to four times as large as in the example.
【0024】比較例2 図1の装置において、活性炭粉を導入せずに排ガス処理
を行った。その他の条件は実施例と同じに設定した。Comparative Example 2 Exhaust gas treatment was carried out in the apparatus shown in FIG. 1 without introducing activated carbon powder. Other conditions were set the same as in the example.
【0025】集塵器で回収したダスト中のダイオキシン
濃度は0.05〜0.1ng/gダスト、吸着反応器通
過後のダイオキシン濃度は0.1ng/m3(Normal)
であり、脱離・再生器での分解率は99.9%であっ
た。The dioxin concentration in the dust collected by the dust collector is 0.05 to 0.1 ng / g dust, and the dioxin concentration after passing through the adsorption reactor is 0.1 ng / m 3 (Normal).
And the decomposition rate in the desorption / regeneration unit was 99.9%.
【0026】以上の比較実験結果から、本発明によるダ
イオキシン除去効率の向上及び活性炭(炭素質吸着剤)
の使用量低減効果が確認された。From the results of the above comparative experiments, it can be seen that the present invention improves the dioxin removal efficiency and activates carbon (carbonaceous adsorbent).
The effect of reducing the amount of used was confirmed.
【0027】[0027]
【発明の効果】以上説明したように本発明によれば、排
ガスにアルカリ薬剤を添加して塩化水素を始めとする酸
性ガスを固形化して集塵器で除去した後に、粉状の炭素
質吸着剤を導入して排ガス中の粒状のダイオキシン類を
吸着せしめ、粉状の炭素質吸着剤とガス状のダイオキシ
ン類とを移動層式の吸着反応器に充填された粒状の炭素
質吸着剤に吸着若しくは付着させて除去するので、ダイ
オキシン類を効率良く除去することができるとともに、
後処理も容易でかつ、吸着剤等の使用量を低減すること
ができる。As described above, according to the present invention, powdery carbonaceous material is adsorbed after adding an alkaline agent to exhaust gas to solidify acid gas such as hydrogen chloride and removing it by a dust collector. Adsorbent to adsorb particulate dioxins in exhaust gas, and adsorb powdery carbonaceous adsorbent and gaseous dioxins to particulate carbonaceous adsorbent packed in a moving bed type adsorption reactor Or because it is attached and removed, dioxins can be removed efficiently,
Post-treatment is also easy, and the amount of adsorbent or the like used can be reduced.
【図1】本発明に係る排ガス処理装置の構成を示す概略
図である。FIG. 1 is a schematic diagram showing a configuration of an exhaust gas treatment apparatus according to the present invention.
10…集塵器、20…吸着反応器、21…脱離・再生
器、22…分離器、23…炭素質吸着剤供給装置、30
…煙突、40…アルカリ薬剤供給装置。DESCRIPTION OF SYMBOLS 10 ... Dust collector, 20 ... Adsorption reactor, 21 ... Desorption / regenerator, 22 ... Separator, 23 ... Carbonaceous adsorbent supply apparatus, 30
... Chimney, 40 ... Alkaline chemical supply device.
Claims (6)
る排ガス処理方法であって、 前記排ガス中にアルカリ薬剤を添加して、前記排ガス中
の酸性成分と反応させて固形の反応生成物を得る工程
と、 前記反応生成物を含む固形分を集塵器により除去する工
程と、 前記集塵器を通過した排ガス中に粉状の炭素質吸着剤を
注入して粒子状の有機塩素化合物を該炭素質吸着剤に吸
着させる工程と、 前記粉状の炭素質吸着剤を含む排ガスを粒状の炭素質吸
着剤が充填されている移動層式の吸着塔に導いて通過さ
せることにより、前記粉状の炭素質吸着剤と前記排ガス
中のガス状の有機塩素化合物を除去する工程と、 前記吸着塔から取り出した前記炭素質吸着剤を脱離・再
生する工程と、 脱離・再生後の粒状の炭素質吸着剤を前記吸着塔に返送
する工程と、 を備えている排ガス処理方法。An exhaust gas treatment method for removing an organic chlorine compound in a combustion exhaust gas, wherein an alkali agent is added to the exhaust gas and reacted with an acidic component in the exhaust gas to obtain a solid reaction product. Removing the solid content containing the reaction product by a dust collector; and injecting a powdery carbonaceous adsorbent into the exhaust gas passing through the dust collector to remove the particulate organic chlorine compound. A step of adsorbing the powdery carbonaceous adsorbent onto the carbonaceous adsorbent, and passing the exhaust gas containing the powdery carbonaceous adsorbent through a moving bed type adsorption tower filled with a granular carbonaceous adsorbent, thereby passing the powdery carbonaceous adsorbent. Removing the carbonaceous adsorbent and the gaseous organochlorine compound in the exhaust gas; desorbing and regenerating the carbonaceous adsorbent taken out of the adsorption tower; Returning the carbonaceous adsorbent to the adsorption tower An exhaust gas treatment method comprising:
により区分する工程をさらに備え、分離した粉状の炭素
質吸着剤を前記集塵器を通過した排ガス中に注入する請
求項1記載の排ガス処理方法。2. The method according to claim 1, further comprising the step of separating the desorbed / regenerated carbonaceous adsorbent according to particle diameter, and injecting the separated powdery carbonaceous adsorbent into the exhaust gas passing through the dust collector. Item 7. An exhaust gas treatment method according to Item 1.
を有する粉状の炭素質吸着剤を追加注入する請求項1あ
るいは2に記載の排ガス処理方法。3. The exhaust gas treatment method according to claim 1, wherein a powdery carbonaceous adsorbent having high activity is additionally injected into the exhaust gas passing through the dust collector.
る排ガス処理装置であって、 前記排ガス中にアルカリ薬剤を添加するアルカリ薬剤添
加手段と、 前記アルカリ薬剤添加後の排ガスが導かれる集塵器と、 前記集塵器を通過した排ガス中に粉状の炭素質吸着剤を
注入する炭素質吸着剤注入手段と、 粒状の炭素質吸着剤が充填されており、前記粉状の炭素
質吸着剤注入後の排ガスが導かれる移動層式の吸着塔
と、 前記吸着塔内の炭素質吸着剤を脱離・再生する脱離・再
生器と、 脱離・再生後の粒状の炭素質吸着剤を前記吸着塔に返送
する第一の返送手段と、 を備えている排ガス処理装置。4. An exhaust gas treatment device for removing an organic chlorine compound in a combustion exhaust gas, comprising: an alkali agent adding means for adding an alkaline agent to the exhaust gas; and a dust collector to which the exhaust gas after the addition of the alkali agent is guided. A carbonaceous adsorbent injection means for injecting a powdery carbonaceous adsorbent into the exhaust gas passing through the dust collector; and a granular carbonaceous adsorbent filled with the particulate carbonaceous adsorbent, A moving bed type adsorption tower into which exhaust gas after injection is introduced, a desorption / regeneration device for desorbing / regenerating the carbonaceous adsorbent in the adsorption tower, and a granular carbonaceous adsorbent after desorption / regeneration. An exhaust gas treatment device comprising: first return means for returning to the adsorption tower.
により区分する分離手段と、 分離した粉状の炭素質吸着剤を前記炭素質吸着剤注入手
段へと導く第二の返送手段と、 をさらに備えている請求項4記載の排ガス処理装置。5. A separating means for separating the desorbed / regenerated carbonaceous adsorbent according to particle diameter, and a second return for guiding the separated powdery carbonaceous adsorbent to the carbonaceous adsorbent injection means. The exhaust gas treatment device according to claim 4, further comprising: means.
記炭素質吸着剤注入手段に導く炭素質吸着剤供給手段を
さらに備えている請求項4あるいは5に記載の排ガス処
理装置。6. The exhaust gas treatment apparatus according to claim 4, further comprising a carbonaceous adsorbent supply unit for guiding a powdery carbonaceous adsorbent having high activity to the carbonaceous adsorbent injection unit.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP37030599A JP2001179052A (en) | 1999-12-27 | 1999-12-27 | Method and device for treating exhaust gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP37030599A JP2001179052A (en) | 1999-12-27 | 1999-12-27 | Method and device for treating exhaust gas |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2001179052A true JP2001179052A (en) | 2001-07-03 |
Family
ID=18496575
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP37030599A Pending JP2001179052A (en) | 1999-12-27 | 1999-12-27 | Method and device for treating exhaust gas |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2001179052A (en) |
-
1999
- 1999-12-27 JP JP37030599A patent/JP2001179052A/en active Pending
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