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JPS6021768B2 - Cross flow type gas-solid contact device - Google Patents
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JPS6021768B2 - Cross flow type gas-solid contact device - Google Patents

Cross flow type gas-solid contact device

Info

Publication number
JPS6021768B2
JPS6021768B2 JP54048686A JP4868679A JPS6021768B2 JP S6021768 B2 JPS6021768 B2 JP S6021768B2 JP 54048686 A JP54048686 A JP 54048686A JP 4868679 A JP4868679 A JP 4868679A JP S6021768 B2 JPS6021768 B2 JP S6021768B2
Authority
JP
Japan
Prior art keywords
gas
roll
solid
flow type
contact device
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
Application number
JP54048686A
Other languages
Japanese (ja)
Other versions
JPS55139829A (en
Inventor
裕実 田中
勇 前田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sumitomo Heavy Industries Ltd
Original Assignee
Sumitomo Heavy Industries Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Sumitomo Heavy Industries Ltd filed Critical Sumitomo Heavy Industries Ltd
Priority to JP54048686A priority Critical patent/JPS6021768B2/en
Publication of JPS55139829A publication Critical patent/JPS55139829A/en
Publication of JPS6021768B2 publication Critical patent/JPS6021768B2/en
Expired legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J8/00Chemical or physical processes in general, conducted in the presence of fluids and solid particles; Apparatus for such processes
    • B01J8/08Chemical or physical processes in general, conducted in the presence of fluids and solid particles; Apparatus for such processes with moving particles
    • B01J8/12Chemical 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)
  • Separation Of Gases By Adsorption (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Devices And Processes Conducted In The Presence Of Fluids And Solid Particles (AREA)

Description

【発明の詳細な説明】 本発明はほぼ垂直下向きに移動する固体粒子床にガスを
ほぼ水平方向に流して固体粒子とガスを接触させる直交
流式気−固接触装置の改良に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in a cross-flow type gas-solid contacting device in which solid particles and gas are brought into contact by flowing a gas substantially horizontally through a bed of solid particles moving substantially vertically downward.

直交流式気−園接触装置は、従来から各種排ガスの処理
装置として広く利用され、例えばS○x及び/又はN0
xを含有する排ガスを処理する場合には、固体粒子とし
て吸着剤乃至触媒を使用した装置が、また含塵ガスの処
理に際しては固体粒子として炉過剤を使用した装置がそ
れぞれ実用化されている。
Cross-flow air contact equipment has been widely used as a treatment device for various exhaust gases, such as S○x and/or N0.
When treating exhaust gas containing .

ところで従来の直交流式気−固接触装置は、第1図にそ
の縦断正面図を示す通り、ルーバー、多孔板、網その他
の透気性保持体(図示の例ではルーバー)からなる側壁
la及びlbと、不透気性保持体からなる前後壁(図示
なし)とで断面矩形の塔体を構成させ、側壁la,lb
に額斜壁を、前後壁2a,2bに垂直壁を連続させて塔
体の下方にホッパー2を設け、さらにホッパー2の下端
部の一方に屈曲傾斜壁3を連続させ、その屈曲傾斜壁3
に接してロール4を配設した構造が一般に探られている
By the way, the conventional cross-flow type gas-solid contact device has side walls la and lb made of louvers, perforated plates, nets, and other air-permeable holders (louvers in the illustrated example), as shown in a longitudinal sectional front view in FIG. and front and rear walls (not shown) made of an air-impermeable holder to form a tower body with a rectangular cross section, and the side walls la, lb
A hopper 2 is provided below the tower body with a vertical wall continuous to the front and rear walls 2a and 2b, and a bent inclined wall 3 continuous to one of the lower ends of the hopper 2.
A structure in which the roll 4 is disposed in contact with is generally being explored.

尚、付号5は固体粒子の整流体を示す。この装置に於て
は、矢印6の方向から装置内に供給される新鮮な固体粒
子又は再生された固体粒子は順次下方に移動しながら、
矢印7の方向から装置に流入して矢印7′の方向に流出
するガスと直交流で、換言すれば十字流で接触後、ロー
ル4を介して装置から排出されるが、この装置ではガス
の入口側を通る固体粒子と、ガスの出口側を通ぬ固体粒
子がほぼ同じ移動速度で装置内を流下するため、次のよ
うな問題の発生を回避することができない。すなわち、
固体粒子に吸着剤を使用してS○x含有排ガスの処理に
、従釆の直交流式気−固接触装置を利用した場合には、
気−液援舷領域(第1図の側壁la,lb及び前後壁で
構成される繁体内領域)に入った吸着剤は、ガスの流れ
方向に関して入口側から順次S○xで飽和され、この飽
和状態は次第にガス出口側に進行するが、当該領域内に
ある吸着剤は全体として下方に移動するので、この吸着
剤移動床では第1図に示す如く、移動床下部に行く程S
○xで飽和された吸着剤Bが占める割合は増大し、逆に
未飽和の吸着剤Aが占める割合は減少する。
Incidentally, number 5 indicates the flow regulation of solid particles. In this device, fresh solid particles or recycled solid particles supplied into the device from the direction of arrow 6 are sequentially moved downward while
After coming into contact with the gas flowing into the device from the direction of arrow 7 and flowing out in the direction of arrow 7' in a cross flow, in other words, the gas is discharged from the device via the roll 4. Since the solid particles passing through the inlet side and the solid particles not passing through the gas outlet side flow down the apparatus at approximately the same moving speed, the following problems cannot be avoided. That is,
When a secondary cross-flow type gas-solid contact device is used to treat S○x-containing exhaust gas using an adsorbent for solid particles,
The adsorbent that has entered the gas-liquid support area (the internal area consisting of the side walls la, lb and the front and rear walls in Figure 1) is saturated with S○x sequentially from the inlet side in the gas flow direction, and this The saturated state gradually progresses toward the gas outlet side, but the adsorbent in this area moves downward as a whole, so in this adsorbent moving bed, as shown in Fig. 1, S decreases as it goes toward the bottom of the moving bed.
The proportion occupied by adsorbent B saturated with ○x increases, and conversely the proportion occupied by unsaturated adsorbent A decreases.

従って、移動床の下部全体がS○xで飽和された吸着剤
で占められた場合には、当該部位を通る排ガスからはS
○xを吸着除去できないという問題が生ずる。尤も移動
床の下部全体がS○xで飽和された吸着剤で占められる
情況は、例えば吸着剤の移動速度を増大させることによ
って解消させることができるが、この場合には未だ吸着
余力のある吸着剤が装置から排出される結果になるため
、吸着剤の利用率が低下してしまう欠点がある。上記の
如き好ましからざる事態は吸着剤を固体粒子とした場合
や排ガスの脱硫処理に固有のものではなく、従来の直交
流式気−固接触装置を使用する限り、触媒や炉過剤を固
体粒子とした場合でも、排ガスの脱硝処理や除塵処理の
場合でも同様に生起する。
Therefore, if the entire lower part of the moving bed is occupied by an adsorbent saturated with S○x, no S
A problem arises in that ○x cannot be removed by adsorption. Of course, the situation in which the entire lower part of the moving bed is occupied by the adsorbent saturated with S○x can be resolved by increasing the moving speed of the adsorbent, but in this case, the adsorbent that still has adsorption capacity This has the disadvantage that the utilization of the adsorbent is reduced as the result is that the agent is discharged from the device. The undesirable situation described above is not unique to the case where the adsorbent is solid particles or to the desulfurization treatment of exhaust gas. The same problem occurs even when the exhaust gas is denitrified or dust removed.

殊に険塵処理の場合には、炉過剤移動床に於ける煤塵の
橘促分布は第1図の領域Bに相当する勾配を持ち、移動
床下部では含塵ガスの通過抵抗が増大するので、含塵ガ
スは移動床上部へ偏流してしまうばかりでなく、これに
原因して装置全体の圧力損失が増大するという弊害もあ
る。而して本発明は直交流式気−固接触装置に於ける移
動床内での固体粒子の移動速度が、ガスの出口側でより
も入口側で大きくなるようにして、上記の如き好ましか
らざる事態の発生を回避できる直交流式気−固接触装置
を提案する。
Particularly in the case of dust treatment, the distribution of soot and dust in the moving bed of furnace filtration agent has a slope corresponding to region B in Figure 1, and the passage resistance of dust-containing gas increases at the bottom of the moving bed. Therefore, not only does the dust-containing gas drift toward the upper part of the moving bed, but this also has the disadvantage of increasing the pressure loss of the entire apparatus. Therefore, the present invention solves the above-mentioned undesirable problems by making the moving speed of solid particles in the moving bed of the cross-flow type gas-solid contact device larger on the gas inlet side than on the gas outlet side. We propose a cross-flow type gas-solid contact device that can avoid this situation.

すなわち本発明はほぼ垂直下向きに移動する固体粒子床
に、3ガスをほぼ水平方向に供給して両者を接触させる
直交流式気−固接触装置に於て、固体粒子床の下部に、
ガスの流れ方向に関して上流側と下流側の2つの固体粒
子排出口を設け、上流側排出口の下方には第1ロールを
設置し、下流側排出口の下方4には前記第1ロールと同
一径で回転数が低い第2ロールを設置したことを特徴と
する前記の直交流式気−固接触装置を提供するものであ
る。以下、図面にそって本発明に係る気−固接触装畳を
説明すると、第2図は本発明の一実施例たる気−固接触
装置の縦断正面図であって、図に示す実施例では固体粒
子が矢印6の方向から装置内に供給されて矢印6′の方
向に排出される。
That is, the present invention provides a cross-flow type gas-solid contact device in which three gases are supplied in a substantially horizontal direction to a bed of solid particles moving almost vertically downward so that they come into contact with each other.
Two solid particle discharge ports are provided on the upstream and downstream sides with respect to the gas flow direction, a first roll is installed below the upstream discharge port, and the same roll as the first roll is installed below the downstream discharge port. The present invention provides the above-mentioned cross-flow type gas-solid contact device characterized in that a second roll having a lower rotation speed in terms of diameter is installed. The gas-solid contact device according to the present invention will be explained below with reference to the drawings. FIG. 2 is a longitudinal sectional front view of the gas-solid contact device which is an embodiment of the present invention, and Solid particles are fed into the device in the direction of arrow 6 and discharged in the direction of arrow 6'.

固体粒子の移動床2川ま、ルーバー、多孔板、網その他
の透気性保持体からなる側壁21a及び21bと不透気
性保持体からなる前後壁(図示なし)とで構成される断
面矩形の塔体内に形成される。而して矢印7の方向から
装置内に供給されるガスは、0装鷹内を下向きに移動す
る固体粒子床20と直交流(十字流とも言う)で接触し
て、矢印7′の方向に流出する。移動床20の下方には
ガスの流れ方向に関して上流側と下流側の二方にホッパ
ー22a及び225bが設けられる。
A tower with a rectangular cross section consisting of two moving beds for solid particles, side walls 21a and 21b made of air-permeable holding bodies such as louvers, perforated plates, nets, etc., and front and rear walls (not shown) made of air-impermeable holding bodies. Formed inside the body. Thus, the gas supplied into the apparatus from the direction of arrow 7 comes into contact with the solid particle bed 20 moving downward in the zero loading tank in a cross flow (also called cross flow), and flows in the direction of arrow 7'. leak. Below the moving bed 20, hoppers 22a and 225b are provided on both the upstream and downstream sides in the gas flow direction.

これら二つのホツパーは装置の鞠線に関して互に対称で
あることを可とする。尚、各ホツバー内には必要に応じ
て整流体25a及び25bを設置することができる。こ
の整流体の設置によって、ホッパ−内での固体粒子の流
れがより一層円滑になるので、固体粒子に活性炭などの
吸着剤を用いる脱硫装置に本発明の装置を利用する場合
の如く、移動床の層厚くガスから見た移動床の厚さ)を
1.5〜2.5の程度に大きくする場合には、整流体の
設置が推奨されるが、必ずしも必須ではない。各ホッパ
ー22a及び22bにはそれぞれの下端部の一方に屈曲
額斜壁23a及び23bが設けられ、これに接して同一
径で回転数が異なるロール24a及び24bが配設され
る。
These two hoppers may be symmetrical to each other with respect to the machine markings. Incidentally, fluid regulators 25a and 25b can be installed in each hopper as necessary. By installing this flow regulator, the flow of solid particles in the hopper becomes even smoother, so it is possible to use a moving bed as in the case where the device of the present invention is used in a desulfurization device that uses an adsorbent such as activated carbon for solid particles. When increasing the moving bed thickness (as seen from the gas) to about 1.5 to 2.5, it is recommended to install a flow regulator, but it is not always essential. Each of the hoppers 22a and 22b is provided with a bent oblique wall 23a and 23b at one of its lower ends, and rolls 24a and 24b having the same diameter and different rotation speeds are disposed in contact with this.

この場合、上流側ロール24aは下流側ロールより回転
数が高い。従って、移動床20内では、ガスの流れ方向
に関して上流側にある固体粒子が、下流側にある固体粒
子に比較して遠い速度で下方に移行するが、この情況を
実験例をもって説明すれば次の通りである。実験例 整流体25a及び25bを設けなかった以外は第2図と
同一構成の装置を使用して、ガスを流通させることなく
固体粒子の流下試験を行なった。
In this case, the upstream roll 24a has a higher rotational speed than the downstream roll. Therefore, within the moving bed 20, solid particles located on the upstream side in the gas flow direction move downward at a greater speed than solid particles located on the downstream side. This situation can be explained using an experimental example as follows. It is as follows. EXPERIMENTAL EXAMPLE A solid particle flow test was conducted without gas flow using an apparatus having the same configuration as in FIG. 2 except that the fluid regulators 25a and 25b were not provided.

固体粒子には4雌Jの球状磁器ポールを使用し、粒子床
の高さ(h)を2凧、層厚(t)を1の、膚幅を0.5
の、ホッバー角度(a)を600とした。ホツパー下方
に配置されたロール24a及び24bの回転数を同一に
セットし、固体粒子の流下状況を観察したところ、装置
の前壁面に現われた粒子のフローパターンは第3図aに
示す通りであつた。
For the solid particles, 4 female J spherical porcelain poles were used, the particle bed height (h) was 2 kites, the layer thickness (t) was 1, and the skin width was 0.5.
The hover angle (a) was set to 600. When the rotational speed of the rolls 24a and 24b placed below the hopper was set to the same value and the flow of solid particles was observed, the flow pattern of the particles appearing on the front wall of the device was as shown in Figure 3a. Ta.

次にロール24aと24bとの回転数を変え、前者の回
転数を後者の1.3割こセットしてフローパターンを先
の場合と同様に観察したところ、第3図bに示す結果が
得られた。
Next, the rotational speed of the rolls 24a and 24b was changed, and the rotational speed of the former was set to 1.30% of the latter, and the flow pattern was observed in the same way as in the previous case, and the results shown in Figure 3b were obtained. It was done.

この実験結果からも明らかな通り、本発明の装置を利用
すれば、ガスの流れ方向に関して上流側にある移動床内
粒子を、下流側の固体粒子より速い速度で流下させるこ
とができるので、第1図に示す如き従来装置との対比で
移動床容積、固体粒子の種類及び給排出量並びにガス流
量が同一である場合には、従来装置で経験される諸問題
を軽減することができる。
As is clear from this experimental result, if the apparatus of the present invention is used, the particles in the moving bed on the upstream side in the gas flow direction can be caused to flow down at a faster speed than the solid particles on the downstream side. If the moving bed volume, solid particle type and supply/discharge volume, and gas flow rate are the same compared to the conventional apparatus as shown in FIG. 1, the problems experienced with the conventional apparatus can be alleviated.

また、装置に流入するガスと流出ガスとの組成変化乃至
さま圧力変化を検知し、それに応じてロール24aと2
4bとの回転数比を調節できる制御手段を本発明の装置
に付設した場合には、移動床内の固体粒子のフローパタ
ーンを処理すべき排ガスの組成に応じて最適パターンに
保持することもできる。従って本発明の装置を脱硫装置
に利用すれば、吸着剤が有効に利用できるばかりでなく
、圧力損失も少なく、また比較的煤塵濃度の高いS○x
含有排ガスを処理する場合でも、移動床のガス入口断面
積を格別拡大する必要がない。
Also, the system detects changes in the composition or pressure between the gas flowing into the device and the gas flowing out, and accordingly changes the pressure between the rolls 24a and 24a.
When the apparatus of the present invention is equipped with a control means that can adjust the rotation speed ratio with 4b, the flow pattern of solid particles in the moving bed can be maintained at an optimal pattern depending on the composition of the exhaust gas to be treated. . Therefore, if the device of the present invention is used in a desulfurization device, not only can the adsorbent be used effectively, but the pressure loss is also small, and S○x with relatively high soot and dust concentration can be used.
Even when treating contained exhaust gas, there is no need to particularly expand the cross-sectional area of the gas inlet of the moving bed.

また脱硝装置に利用すれば、たとえ媒塵濃度の高いN○
x含有排ガスを処理する場合でも、触媒が有効に利用で
きるほか、煤塵の蓄積に起因するガスの偏流が起らない
ので、経済的な空塔速度を採用できる利点がある。さら
にまた本発明の装置を集塵装置に利用した場合には、媒
塵の蓄積によるガスの偏流及び圧力損失の上昇がないの
で、炉過面積が比較的少ない経済的な装置で含塵ガスを
処理することができる。実施例 整流体25a及び25bを設置しなかった以外は第2図
に示す装置と同一構成の直交流式気−固接触装置を使用
して、S○xloo功血と蝶塵400mo/N〆を含有
する温度15ぴ0の石炭ボィラ排ガスを処理した。
In addition, if used in a denitrification device, even if the concentration of pollutants is high,
Even when treating x-containing exhaust gas, the catalyst can be used effectively, and there is no drifting of the gas due to the accumulation of soot and dust, so there is an advantage that an economical superficial velocity can be used. Furthermore, when the device of the present invention is used as a dust collector, there is no uneven flow of gas or increase in pressure loss due to accumulation of dust, so dust-containing gas can be collected using an economical device with a relatively small furnace area. can be processed. EXAMPLE Using a cross-flow type gas-solid contact device having the same configuration as the device shown in Fig. 2 except that the fluid regulators 25a and 25b were not installed, S○xloo gongketsu and butterfly dust were produced at 400 mo/N. Coal boiler exhaust gas containing a temperature of 15 psi was treated.

固体粒子には粒径5肌の粒状活性炭を使用し、移動床の
高さを4の、層厚を1.2肌、層幅を1のとした。また
、上流側ロール24aの回転数を下流側ロール24bの
それの1.5倍にセットし、粒状活性炭の移動床内平均
滞留時間を26.5時間に調整した。この孫件で上記の
石炭ボィラ排ガスを毎時300帆での割合で装置に供給
したところ、脱硫率90%、除塵率80%の結果を得た
。また移動床での圧力損失は15仇肋Aqであり、装置
から排出された活性炭の平均吸着量は8.5%であった
。比較のため、ロール24aと24bの回転数を同一と
した以外は上記と全く同じ係件で石炭ボイラ排ガスを処
理したところ、脱硫率87%、除塵率85%の成績が得
られ、移動床での圧力損失は280肋Aqとなつた。
Granular activated carbon with a particle size of 5 mm was used as the solid particles, the height of the moving bed was 4 mm, the layer thickness was 1.2 mm, and the layer width was 1 mm. Further, the rotation speed of the upstream roll 24a was set to 1.5 times that of the downstream roll 24b, and the average residence time of the granular activated carbon in the moving bed was adjusted to 26.5 hours. In this case, when the above-mentioned coal boiler exhaust gas was supplied to the device at a rate of 300 sails per hour, a desulfurization rate of 90% and a dust removal rate of 80% were obtained. The pressure loss in the moving bed was 15 Aq, and the average adsorption amount of activated carbon discharged from the device was 8.5%. For comparison, when coal boiler exhaust gas was treated in exactly the same manner as above except that the rotational speed of the rolls 24a and 24b was the same, a desulfurization rate of 87% and a dust removal rate of 85% were obtained. The pressure loss was 280 Aq.

また、ロール24aと24bの回転数の比を1に維持し
たまま、脱硫率90%が得られるよう活性炭の移動速度
を調整して同種の実験を行なったところ、移動床内での
活性炭の平均滞留時間は2油時間となり、除塵率は78
%に低下した。
In addition, when a similar experiment was conducted by adjusting the moving speed of activated carbon to obtain a desulfurization rate of 90% while maintaining the ratio of the rotational speed of rolls 24a and 24b at 1, it was found that the average amount of activated carbon in the moving bed was Residence time is 2 oil hours, dust removal rate is 78
%.

また移動床での圧力損失は16物舷Aqとなり、装置か
ら排出される活性炭の平均吸着量は7.4%であった。
The pressure loss in the moving bed was 16 Aq, and the average adsorption amount of activated carbon discharged from the device was 7.4%.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は従来の直交流式気−固接触装置の縦断正面図、
第2図は本発明の一実施例たる直交流式気−固接触装置
の縦断正面図、第3図a及びbは移動床内に於ける固体
粒子のフローパターン説明図である。 la,lb,21a,21b・・・・・・透気性側壁、
2,22a,22b……ホツパー、3,23a,夕23
b・・・・・・屈曲煩斜壁、4,24a,24b.・・
.・・ロール、5,25a,25b……整流体、20・
・・・・・移動床。 箱ー図 第2図 第3図
Figure 1 is a longitudinal sectional front view of a conventional cross-flow type gas-solid contact device.
FIG. 2 is a longitudinal sectional front view of a cross-flow type gas-solid contacting device according to an embodiment of the present invention, and FIGS. 3a and 3b are explanatory views of the flow pattern of solid particles in a moving bed. la, lb, 21a, 21b... air permeable side wall,
2, 22a, 22b...hopper, 3, 23a, evening 23
b...Bent wall, 4, 24a, 24b.・・・
.. ...Roll, 5, 25a, 25b... Rectifier, 20.
...Moving floor. Box diagram Figure 2 Figure 3

Claims (1)

【特許請求の範囲】 1 ほぼ垂直下向きに移動する固体粒子床に、ガスをほ
ぼ水平方向に供給して両者を接触させる直交流式気−固
接触装置に於て、固体粒子床の下部に、ガスの流れ方向
に関して上流側と下流側の2つの固体粒子排出口を設け
、上流側排出口の下方には第1ロールを設置し、下流側
排出口の下方には前記第1ロールと同一径で回転数が低
い第2ロールを設置したことを特徴とする前記の直交流
式気−固接触装置。 2 ガス入口部とガス出口部との間のガス組成の変化又
は圧力の変化を検知し、それに応じて第1ロールと第2
ロールとの回転数比を調節できる制御手段を付設したこ
とを特徴とする特許請求の範囲第1項記載の直交流式気
−固接触装置。
[Scope of Claims] 1. In a cross-flow type gas-solid contact device in which gas is supplied in a substantially horizontal direction to a solid particle bed moving substantially vertically downward so that they come into contact with each other, at the bottom of the solid particle bed, Two solid particle discharge ports are provided on the upstream and downstream sides with respect to the gas flow direction, a first roll is installed below the upstream discharge port, and a first roll having the same diameter as the first roll is installed below the downstream discharge port. The above-mentioned cross-flow type gas-solid contact device is characterized in that a second roll having a low rotational speed is installed. 2 Detecting a change in gas composition or a change in pressure between the gas inlet and the gas outlet, and adjusting the first and second rolls accordingly.
2. The cross-flow type gas-solid contact device according to claim 1, further comprising a control means that can adjust the rotation speed ratio with respect to the roll.
JP54048686A 1979-04-19 1979-04-19 Cross flow type gas-solid contact device Expired JPS6021768B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP54048686A JPS6021768B2 (en) 1979-04-19 1979-04-19 Cross flow type gas-solid contact device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP54048686A JPS6021768B2 (en) 1979-04-19 1979-04-19 Cross flow type gas-solid contact device

Publications (2)

Publication Number Publication Date
JPS55139829A JPS55139829A (en) 1980-11-01
JPS6021768B2 true JPS6021768B2 (en) 1985-05-29

Family

ID=12810190

Family Applications (1)

Application Number Title Priority Date Filing Date
JP54048686A Expired JPS6021768B2 (en) 1979-04-19 1979-04-19 Cross flow type gas-solid contact device

Country Status (1)

Country Link
JP (1) JPS6021768B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57177330A (en) * 1981-04-27 1982-11-01 Babcock Hitachi Kk Apparatus for adsorbing sulfur dioxide
DE3638611A1 (en) * 1986-11-12 1988-05-26 Bergwerksverband Gmbh WALKING LAYER REACTOR FOR THE REMOVAL OF UNWANTED, GAS-SHAPED COMPONENTS FROM GASES
JPS63252523A (en) * 1987-04-07 1988-10-19 Sumitomo Heavy Ind Ltd Direct and alternating current moving bed device
US5494500A (en) * 1990-11-26 1996-02-27 The Social Welfare Foundation Hokkaido Rehabily Activated carbon, production thereof and adsorption using activated carbon

Also Published As

Publication number Publication date
JPS55139829A (en) 1980-11-01

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