JPS59329A - Moving layer type packed tower for granular substance - Google Patents
Moving layer type packed tower for granular substanceInfo
- Publication number
- JPS59329A JPS59329A JP57109393A JP10939382A JPS59329A JP S59329 A JPS59329 A JP S59329A JP 57109393 A JP57109393 A JP 57109393A JP 10939382 A JP10939382 A JP 10939382A JP S59329 A JPS59329 A JP S59329A
- Authority
- JP
- Japan
- Prior art keywords
- adsorbent
- gas
- louver
- moving bed
- dust
- 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
- 239000000126 substance Substances 0.000 title 1
- 239000013618 particulate matter Substances 0.000 claims description 18
- 239000011236 particulate material Substances 0.000 claims description 17
- 238000001179 sorption measurement Methods 0.000 claims description 12
- 238000005192 partition Methods 0.000 claims description 7
- 239000008187 granular material Substances 0.000 claims description 2
- 239000003463 adsorbent Substances 0.000 abstract description 22
- 239000000428 dust Substances 0.000 abstract description 15
- 239000002245 particle Substances 0.000 abstract description 8
- 239000007789 gas Substances 0.000 description 37
- 239000000463 material Substances 0.000 description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 5
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 5
- 229910052815 sulfur oxide Inorganic materials 0.000 description 5
- 230000005484 gravity Effects 0.000 description 4
- 229910052799 carbon Inorganic materials 0.000 description 3
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000006477 desulfuration reaction Methods 0.000 description 2
- 230000023556 desulfurization Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000003546 flue gas Substances 0.000 description 2
- 238000004080 punching Methods 0.000 description 2
- 238000009825 accumulation Methods 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000000284 extract Substances 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 238000009423 ventilation 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)
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
- Devices And Processes Conducted In The Presence Of Fluids And Solid Particles (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は移動層型粒状物質充填塔に係り、特に充填層か
ら飛散したダストおよび粒状物質と捕集して粒状物質充
填層に戻すのに好適な移動層型粒状物質充填塔に関する
。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a moving bed type particulate material packed column, and particularly to a moving bed type particulate material suitable for collecting dust and particulate matter scattered from the packed bed and returning them to the particulate material packed bed. Regarding packed towers.
従来、移動層型粒状物質充填塔では、粒状の吸着剤、触
媒あるいはその他の粒状物質の充填層に排ガスを通気し
、排ガス中の成分と粒状物質を接触させ、吸着、反応あ
るいは捕集を行う。このような充填塔として1例えば移
動層吸着塔の場合、第1図に示すようにガス人口】側と
ガス出口側2にそれぞれルーパー3およびシーパー4を
設置し、その間に粒状物質5が充填された移動層型の充
填層が使用されている。Conventionally, in a moving bed type particulate material packed column, exhaust gas is vented through a bed packed with particulate adsorbents, catalysts, or other particulate materials, and components in the exhaust gas are brought into contact with the particulate materials to perform adsorption, reaction, or collection. . In the case of such a packed tower 1, for example, a moving bed adsorption tower, a looper 3 and a seaper 4 are installed on the gas population side and the gas outlet side 2, respectively, as shown in FIG. A moving bed type packed bed is used.
しか1.2、このような移動層吸着塔では、排ガスの流
速、ガス性状および粒状物質の移動速度などによって、
ルーパー内部での粒状物質の非移動部分が形成される。However, 1.2, in such a moving bed adsorption tower, depending on the flow rate of exhaust gas, gas properties, movement speed of particulate matter, etc.
A non-moving part of the particulate material inside the looper is formed.
そのため、非移動粒状物質中にダストが次第に蓄積して
2通風損失を増大させるという問題がある。また、ガス
中の硫黄酸化物を活性炭などの炭素系吸着剤で吸着する
場合には、非移動部分にhる吸着剤は長時間にわたって
硫黄酸化物を飽和以上に吸着し、吸着剤の表面が吸着し
た硫黄酸化物よ如生成した硫酸で濡れてくるようになり
、ルーパー3および4を腐食式せるという問題がある。Therefore, there is a problem in that dust gradually accumulates in the non-moving particulate matter, increasing the ventilation loss. In addition, when sulfur oxides in gas are adsorbed using a carbon-based adsorbent such as activated carbon, the adsorbent that remains on the non-moving part adsorbs sulfur oxides to a level exceeding saturation over a long period of time, causing the surface of the adsorbent to become There is a problem in that the loopers 3 and 4 become wet due to the sulfuric acid generated from the adsorbed sulfur oxides, and corrode the loopers 3 and 4.
さらに、充填1−内の粒状物質の移動速度が遅く、排ガ
ス流蓋が多くなって、ガス速度が大きくなった場合には
、充填j部内のダストおよびガス出口ルーバー4部の粒
状物質の飛散が生ずる。これらの飛散物はガス出口ルー
パー4部の最ド部より次第に堆積するという問題を生ず
る。Furthermore, if the moving speed of the particulate matter in the filling 1- is slow and the number of exhaust gas flow lids increases and the gas velocity increases, the dust in the filling part J and the particulate matter in the gas outlet louver part 4 will be scattered. arise. A problem arises in that these scattered objects gradually accumulate from the outermost part of the gas outlet looper 4.
本発明の目的は、上記した従来技術の問題点を解消し、
排ガスの流速、ダストおよび粒状物質の移動速度にかか
わりなく、安定した運転を5丁能にした移動層型粒状物
質光横塔を提供することにある。The purpose of the present invention is to solve the problems of the prior art described above,
It is an object of the present invention to provide a moving bed type particulate material optical horizontal tower capable of stable operation regardless of the flow rate of exhaust gas and the moving speed of dust and particulate matter.
要するに本発明は、充填層内に堆積したダストおよびガ
へ出ロ側への粒状物質の飛散をある程度許容し、これら
の飛散物を粒状物質充填層と間隔をもって設置した多数
の開口部を有する後流部隔壁との空間部で重力落下させ
、また飛び上り速度が犬さく飛距離の長い飛散物は後流
部隔壁に衝突させて捕集し、捕集物を充填層に戻すよう
にしたものである。In short, the present invention allows dust accumulated in the packed bed and particulate matter to scatter to the gas outlet side to a certain extent, and allows these scattered matters to be dispersed in the bed with a large number of openings spaced apart from the particulate material packed bed. The material is allowed to fall by gravity in the space between it and the flow bulkhead, and the flying objects that fly at long distances are collected by colliding with the wake bulkhead, and the collected material is returned to the packed bed. It is.
以下、添付図面に基いて本発明の詳細な説明する。Hereinafter, the present invention will be described in detail based on the accompanying drawings.
第2図は本発明を排煙脱硫用の移動層型ガス吸4梧に適
用した例を示す。FIG. 2 shows an example in which the present invention is applied to a moving bed type gas suction system for flue gas desulfurization.
第2図において、ガス吸着塔はガス人口1側とガス出0
.1!l 2との間に二列のルーパー3およびルーパー
4が塔底部から塔頂部に垂直に配置され、これらのルー
パー3.4の間に粒状vIJ質5である〜
吸着剤が充填されている点は第1図に示す従来装置と同
じである。In Figure 2, the gas adsorption tower is on the gas population 1 side and on the gas output side 0.
.. 1! Two rows of loopers 3 and 4 are arranged vertically from the bottom of the column to the top of the column between the loopers 3 and 2, and a granular vIJ material 5 is filled between these loopers 3 and 4. is the same as the conventional device shown in FIG.
本実施例において、ルーパー4と間隔をもって塔底部か
ら塔頂部に垂直状にルーパー6が配置され、ガス出口空
間部内に空間部Aが形成されている。したがって本実施
例では、ガス出口空間郡全体の容積は第1図に示す従来
装置の場合よりも大きくなっている。さらにルーパー4
の最下部は垂直部4Aと傾斜部4Bとにより充填層用の
下部ホッパを構成し、これらの垂直部4Aおよび傾斜部
4Bと間隔Bをもって塔本体の塔底部壁が配置され、こ
の間隔Bによって空間部Aの下部ホッパが構成するよう
になっている。In this embodiment, a looper 6 is disposed vertically from the bottom of the column to the top of the column with an interval from the looper 4, and a space A is formed in the gas outlet space. Therefore, in this embodiment, the volume of the entire group of gas outlet spaces is larger than in the case of the conventional device shown in FIG. Furthermore, looper 4
The lowest part of the column constitutes a lower hopper for the packed bed by a vertical part 4A and an inclined part 4B, and the bottom wall of the column main body is arranged with a distance B from these vertical parts 4A and inclined part 4B, and by this distance B. The lower hopper of the space A constitutes the lower hopper.
ここで塔本体の塔底部壁は傾斜部7A、垂直部7Bおよ
び傾斜部7Cが順次形成されている。なお第2図中8は
吸着剤ホッパ、9は抜き出し機である。Here, an inclined part 7A, a vertical part 7B, and an inclined part 7C are sequentially formed on the bottom wall of the tower body. In FIG. 2, 8 is an adsorbent hopper, and 9 is an extractor.
このような移動層−型ガス吸着塔において、ボイラ等の
排ガスはガス人口1より吸着塔に流入し、ルーパー3の
間隙より吸着剤充填層に入り、ガス出口部のルーパー4
より流出するが、この間にガス中の硫黄酸化物は吸着、
除去される。硫黄酸化物を吸着した粒状物質(吸着剤)
5は充填層最下部に設置した抜き出し機9により、充填
層から一定量ずつ連続的に抜き出し、再生装置(ここで
は図示されていない)へ移送し、再生吸着剤をホッパ8
より、充填層内へ供給し、循瀬使用する。In such a moving bed type gas adsorption tower, the exhaust gas from the boiler, etc. flows into the adsorption tower from the gas population 1, enters the adsorbent packed bed through the gap in the looper 3, and passes through the gas outlet through the looper 4.
However, during this time, sulfur oxides in the gas are adsorbed and
removed. Particulate matter that adsorbs sulfur oxides (adsorbent)
Reference numeral 5 indicates that an extractor 9 installed at the bottom of the packed bed continuously extracts a certain amount of adsorbent from the packed bed, transfers it to a regenerator (not shown here), and transfers the regenerated adsorbent to a hopper 8.
Then, it is supplied into the packed bed and used for circulation.
ここでルーパー4の間隙から飛散したダストおよび粒状
物質は、空間部Aで重力落下し、これらのダストおよび
粒状物質のうち飛散距離の大きいA−散物はルーパー6
に衝突して捕集され、間隙Bからなる下部ホッパに通り
、充填層吸着剤の主流に捕集物として合流する。Here, the dust and particulate matter scattered from the gaps in the looper 4 fall due to gravity in the space A, and among these dust and particulate matter, the A-scattered matter having a larger scattering distance is sent to the looper 6.
It collides with and is collected, passes through the lower hopper formed by gap B, and joins the mainstream of the packed bed adsorbent as a collected material.
次にガス出口ルーバー4後流のルーパー6付近における
飛散物の挙動を第3図に示す。Next, the behavior of scattered objects in the vicinity of the looper 6 downstream of the gas outlet louver 4 is shown in FIG.
ルーパー4より飛散した比較的大きな粒子aは重力落下
し、また、飛び上り速度の大きな粒子すは軌跡で示した
ように、ルーパー6に衝突して補集され、下方に落下し
て、最下部に集められる。Relatively large particles a scattered from the looper 4 fall due to gravity, and particles with high jump speed collide with the looper 6 and are collected, as shown in the trajectory, and fall downward to the bottom. are collected in.
ルーパー4とルーパー6の空間幅1.は粒状物質の種類
、粒径、比重およびガスの流速によって異なるが、排煙
脱硫用の吸着塔に充填する炭素系吸着剤では、モデルテ
ストで300〜600+a+が適切であった。Space width of looper 4 and looper 6 1. varies depending on the type of particulate material, particle size, specific gravity, and gas flow rate, but a model test showed that 300 to 600+a+ was appropriate for carbon-based adsorbents packed in adsorption towers for flue gas desulfurization.
マタ、ルーパー6の羽根の形状については、粒状物質の
性状およびガス流速などによp異なるが、ルーパー長さ
1.およびルーパー間N t、は圧力損失を考慮して決
定される。またルーパー6の傾斜角度αはルーパー4の
傾斜角度より太きくし、また、上段ルーパー羽根と続く
下段ルーパーの重なりhをもたせることにより、良好な
捕集効果が得られる。The shape of the blades of the looper 6 varies depending on the properties of the particulate matter and the gas flow rate, but the looper length is 1. and N t between the loopers are determined in consideration of pressure loss. Further, by making the inclination angle α of the looper 6 larger than the inclination angle of the looper 4, and by providing an overlap h between the upper looper blade and the lower looper blade, a good collection effect can be obtained.
次に間隙Bからなる下部ホッパ付近の詳細を第4図によ
り説明する。Next, details of the vicinity of the lower hopper formed by the gap B will be explained with reference to FIG.
第4図において、傾斜部4Bの長さt4および傾斜角度
βは充填層の粒状物質の粒径、比縦および充填面圧によ
り決定されるが、傾斜角度βは傾斜部7Cの傾斜角度よ
りも大きくすることが望ましく、炭素系吸着剤では30
度が良好であった。In FIG. 4, the length t4 and the inclination angle β of the inclined part 4B are determined by the particle size, specific height, and filling surface pressure of the granular material in the packed bed, but the inclination angle β is smaller than the inclination angle of the inclined part 7C. It is desirable to increase the size, and for carbon-based adsorbents 30
The temperature was good.
また捕集物の流れ込み部において、傾斜部4Bの傾斜起
点は、下部ホッパの傾斜部7βの傾斜起点よりも傾斜起
点差t6を設けて上方に位置させることによって捕集物
の流れ込みを容易にすることができる。In addition, in the inflow portion of the collected material, the inclination starting point of the inclined portion 4B is located higher than the inclination starting point of the inclined portion 7β of the lower hopper by providing a difference t6 between the inclination starting points, thereby facilitating the flow of the collected material. be able to.
本発明において、ガス流速が速い場合、図示したルーパ
ー6の代り(二金網、パンチングプレート、又は多数の
スリット状ヶ開ロ部を有する多孔板を用いて慣性衝突を
効率よく行なわせ、充填層から飛散するダストおよび粒
状物質を効率的に捕集することができる。In the present invention, when the gas flow rate is high, instead of the looper 6 shown in the figure, a double wire mesh, a punching plate, or a perforated plate having a large number of slit-shaped openings is used to efficiently perform inertial collision, and Scattered dust and particulate matter can be efficiently collected.
また本発明において、充填層を支持するルーパー3.4
の代りに金網、パンチングプレート又は多数のスリット
状開口部を有する多孔板等の隔壁を用いることもできる
。この場合、これらの隔壁に形成される開口部の内径よ
り゛も小さい粒子はガス出口空間部に飛散するので、こ
のような飛散物を図示の例同様にして捕集し、充填層に
戻すことができる。In addition, in the present invention, the looper 3.4 supporting the packed bed
Instead, a partition wall such as a wire mesh, a punching plate, or a perforated plate having a large number of slit-like openings may be used. In this case, particles smaller than the inner diameter of the openings formed in these partition walls will scatter into the gas outlet space, so these scattered particles can be collected in the same way as in the illustrated example and returned to the packed bed. I can do it.
なお、本発明は移動層型ガス吸着塔に限らず、排ガス中
の成分と移動層型充填層内の粒状物質とを接触させて、
吸着以外の反応を行う移動層型光*塔(二も適用するこ
とができる。Note that the present invention is not limited to moving bed type gas adsorption towers, but also involves bringing components in exhaust gas into contact with particulate matter in a moving bed type packed bed.
A moving bed type light tower (2) that performs reactions other than adsorption can also be applied.
以上のように本発明によれば、充填層における粒状物質
の停滞、ダストの堆積等を避けるだめにガス流速および
粒状物質充填物の移動速度を広範囲を変化させても、充
填層から飛散したダストおよび粒状物を的確に捕集し、
かつ充填層に戻すことができるのでガス処理を安定かつ
、効率的に行うことができ、装置も簡単である。As described above, according to the present invention, even if the gas flow rate and the moving speed of the particulate material filling are varied over a wide range in order to avoid stagnation of particulate matter in the packed bed, accumulation of dust, etc., the dust scattered from the packed bed is Accurately collects and particulate matter,
Moreover, since it can be returned to the packed bed, gas treatment can be performed stably and efficiently, and the equipment is simple.
W、1図は従来の移動層型ガス吸着塔の概略的構成図、
第2図は本発明の一実施例を示す移動層型ガス吸着塔の
概略的構成図、第3図および第4図は各々第2図の要部
詳細図である。
1・・・ガス人口 2・・・ガス出口3、4.6・
・・ルーパー5・・・s状ga代理人 鵜 沼 辰
之
第1図
第2図
第3図
第4図W, Figure 1 is a schematic diagram of a conventional moving bed gas adsorption tower,
FIG. 2 is a schematic diagram of a moving bed type gas adsorption tower showing an embodiment of the present invention, and FIGS. 3 and 4 are detailed views of the main parts of FIG. 2, respectively. 1... Gas population 2... Gas outlet 3, 4.6.
... Looper 5 ... S-shaped GA agent Tatsu Unuma
Figure 1 Figure 2 Figure 3 Figure 4
Claims (4)
内に粒状物質が充填された移動層を形成]11、この移
動層によって塔内にガス入口空間部とガス出口空間部と
を区画して設けた移動層型粒状物質充填塔において、前
記ガス出口空間部内にガス出口空間部側の前記粒状物質
支持用隔壁と間隔をもって多数の開口部を有する後流部
隔壁を設けたことを特徴とする移動層型粒状物質充填塔
。(1) Forming a moving bed filled with particulate matter within two partition walls for supporting particulate matter having a large number of openings] 11. This moving bed creates a gas inlet space and a gas outlet space in the column. In the moving bed type particulate matter packed column which is provided in sections, a downstream partition wall having a large number of openings is provided in the gas outlet space at a distance from the particulate material supporting partition wall on the gas exit space side. Characteristic moving bed type granular material packed column.
であることを特徴とする特許請求の範囲第(])項記載
の移動層型粒状物質充填塔。(2) The moving bed type particulate material packed tower according to claim 1, wherein the moving bed type particulate material packed tower is a moving bed type gas adsorption tower.
徴とする特許請求の範囲第(1)項七載の移動層型粒状
物質充填塔。(3) The moving bed type particulate material packed tower according to claim (1), wherein the particulate material supporting partition wall is a sheeter.
特許請求の範囲第(1)項記載の移動層型粒状物質充填
塔。(4) The moving bed type particulate material packed column according to claim (1), wherein the downstream partition wall is a looper.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57109393A JPS59329A (en) | 1982-06-25 | 1982-06-25 | Moving layer type packed tower for granular substance |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57109393A JPS59329A (en) | 1982-06-25 | 1982-06-25 | Moving layer type packed tower for granular substance |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPS59329A true JPS59329A (en) | 1984-01-05 |
Family
ID=14509095
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57109393A Pending JPS59329A (en) | 1982-06-25 | 1982-06-25 | Moving layer type packed tower for granular substance |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS59329A (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6325138U (en) * | 1986-07-31 | 1988-02-19 | ||
| JPH02147228U (en) * | 1989-05-17 | 1990-12-13 | ||
| JP2002282630A (en) * | 2001-03-29 | 2002-10-02 | Sumitomo Heavy Ind Ltd | Device and method for treating exhaust gas with improved dust removing performance |
| WO2009038036A1 (en) * | 2007-09-20 | 2009-03-26 | J-Power Entech, Inc. | Desulfuration-denitration apparatus for exhaust gas |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4941915U (en) * | 1972-07-17 | 1974-04-12 | ||
| JPS5191914U (en) * | 1975-01-21 | 1976-07-23 |
-
1982
- 1982-06-25 JP JP57109393A patent/JPS59329A/en active Pending
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4941915U (en) * | 1972-07-17 | 1974-04-12 | ||
| JPS5191914U (en) * | 1975-01-21 | 1976-07-23 |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6325138U (en) * | 1986-07-31 | 1988-02-19 | ||
| JPH02147228U (en) * | 1989-05-17 | 1990-12-13 | ||
| JP2002282630A (en) * | 2001-03-29 | 2002-10-02 | Sumitomo Heavy Ind Ltd | Device and method for treating exhaust gas with improved dust removing performance |
| WO2009038036A1 (en) * | 2007-09-20 | 2009-03-26 | J-Power Entech, Inc. | Desulfuration-denitration apparatus for exhaust gas |
| JP2009072683A (en) * | 2007-09-20 | 2009-04-09 | J-Power Entech Inc | Exhaust gas desulfurization and denitration equipment |
| US8679414B2 (en) | 2007-09-20 | 2014-03-25 | J-Power Entech, Inc. | Desulfurization-denitration apparatus for exhaust gas |
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