JPS631089B2 - - Google Patents

Info

Publication number
JPS631089B2
JPS631089B2 JP55037386A JP3738680A JPS631089B2 JP S631089 B2 JPS631089 B2 JP S631089B2 JP 55037386 A JP55037386 A JP 55037386A JP 3738680 A JP3738680 A JP 3738680A JP S631089 B2 JPS631089 B2 JP S631089B2
Authority
JP
Japan
Prior art keywords
adsorbent
exhaust gas
packed bed
cage
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
Application number
JP55037386A
Other languages
Japanese (ja)
Other versions
JPS56136621A (en
Inventor
Naoharu Shinoda
Nobutaka Maeda
Kyoji Kubo
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP3738680A priority Critical patent/JPS56136621A/en
Priority to CA000373855A priority patent/CA1151075A/en
Priority to DE19813112482 priority patent/DE3112482C2/en
Publication of JPS56136621A publication Critical patent/JPS56136621A/en
Publication of JPS631089B2 publication Critical patent/JPS631089B2/ja
Granted legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Treating Waste Gases (AREA)
  • Separation Of Gases By Adsorption (AREA)
  • Chimneys And Flues (AREA)

Description

【発明の詳細な説明】 本発明は、ボイラあるいは工業用炉などからの
排ガス中に含まれる硫黄酸化物を回収除去するた
めに使用される新規な構造を有する乾式排ガス脱
硫装置に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a dry flue gas desulfurization apparatus having a novel structure and used for collecting and removing sulfur oxides contained in flue gas from a boiler or an industrial furnace.

排煙脱硫装置の日本における普及は過去10年間
目ざましいものがある。排煙脱硫設備の開発の段
階では乾式法も含めて種々の技術が提案された
が、現在商業的に稼動しているプラント設備、特
に大容量のものは吸収液と排煙を吸収塔内で接触
させる所謂湿式法が主流である。
The spread of flue gas desulfurization equipment in Japan has been remarkable over the past 10 years. At the stage of developing flue gas desulfurization equipment, various technologies were proposed, including dry methods, but currently commercially operated plant equipment, especially large-capacity ones, do not collect the absorbent liquid and flue gas within the absorption tower. The so-called wet method, which involves contact, is the mainstream.

しかしながら湿式法には蒸発分を含めて大量の
プロセス水を必要とし、処理後の排ガスの温度が
50〜70℃と低く、かつ湿分が多いためそのまま煙
突より放出すると水蒸気が白煙となり目だつたの
で排ガスを再加熱する必要がある場合もあり、こ
の場合には可成りの余分の再加熱用燃料を必要と
する。また低温度のまま放出した場合には煙突か
ら大気への排ガスの拡散効果が悪い。
However, the wet method requires a large amount of process water, including evaporated water, and the temperature of the exhaust gas after treatment increases.
Because the temperature is low (50 to 70℃) and there is a lot of moisture, if the exhaust gas is released directly from the chimney, the water vapor will become noticeable as white smoke, so it may be necessary to reheat the exhaust gas. Requires fuel. Furthermore, if the exhaust gas is released at a low temperature, the diffusion effect of the exhaust gas from the chimney to the atmosphere is poor.

さらに、脱硫に先だち排ガスの冷却と除塵のた
めに使用した排水の処理をする設備を必要とする
等の欠点がある。特に湿式処理後の排ガスの再加
熱のために使用される燃料は、大容量発電所用ボ
イラーの場合主燃料の2〜3%に達し、省エネル
ギーの点から大きな問題となつてきた。
Further, there are drawbacks such as the need for equipment to treat wastewater used for cooling exhaust gas and removing dust prior to desulfurization. In particular, the fuel used for reheating exhaust gas after wet treatment reaches 2 to 3% of the main fuel in boilers for large-capacity power plants, and has become a major problem from the point of view of energy conservation.

一方乾式法は種々提案され、中でも活性炭によ
る吸着は脱硫効果が高いにも拘らず実用化の事例
が少ないのは、硫黄酸化物を吸着した活性炭は
250〜700℃迄加熱して、不活性ガスにより硫黄酸
化物を放出させた後、処理ガス温度迄冷却して再
使用するという吸着、加熱、脱着、冷却のサイク
ルを繰り返すが、このサイクルを自動的に繰り返
す適当な装置が開発されなかつたこと、また活性
炭の吸着性能は繰返し使用により低下するため一
定期間ごとに更新の必要があり、この補充交換に
あたつて多くの人手を要すること、さらにサイク
ル後の活性炭の粉化による粉塵爆発または燃焼等
の事故の可能性があること等の欠点があつた。更
に、排ガス中のダストが、活性炭の吸着層に付着
し、吸着層の閉塞を起し、吸着性能の低下および
吸着層でのガスの圧損失の増大をまねくなどの欠
点があつた。
On the other hand, various dry methods have been proposed, and although activated carbon adsorption has a high desulfurization effect, there are few practical applications of activated carbon that has adsorbed sulfur oxides.
The cycle of adsorption, heating, desorption, and cooling is repeated by heating to 250 to 700°C and releasing sulfur oxides using inert gas, then cooling to the processing gas temperature and reusing it. This cycle is automatically performed. Furthermore, the adsorption performance of activated carbon deteriorates with repeated use, so it needs to be updated at regular intervals, and this replenishment and replacement requires a lot of manpower. There were drawbacks such as the possibility of accidents such as dust explosions or combustion due to the powdering of the activated carbon after the cycle. Furthermore, the dust in the exhaust gas adheres to the activated carbon adsorption layer, causing clogging of the adsorption layer, leading to a decrease in adsorption performance and an increase in gas pressure loss in the adsorption layer.

本発明者らは先に、 「吸着層により排ガス中の硫黄酸化物を吸着除
去する排ガス脱硫装置において、回転自在な直立
した円筒形ケージを有し、同ケージの外周に吸着
材の充填層を形成し、同ケージの外側と内側をケ
ーシングとシール装置により、吸着、加熱、脱
着、冷却および吸着材交換の5つのゾーンに区分
し、前記吸着材交換ゾーンに対応して吸着材の供
給および排出装置を具えてなることを特徴とする
排ガス脱硫装置。」 を提案(特願昭54〜150133号)したが、本発明
はこの装置に対しても、更に排ガス中のダスト対
策に関する改良を加えたものである。
The present inventors previously proposed an exhaust gas desulfurization device that adsorbs and removes sulfur oxides from exhaust gas using an adsorption layer. The outside and inside of the cage are divided into five zones: adsorption, heating, desorption, cooling, and adsorbent exchange using a casing and sealing device, and the adsorbent is supplied and discharged corresponding to the adsorbent exchange zone. "An exhaust gas desulfurization device characterized by comprising a device" was proposed (Japanese Patent Application No. 150133/1983), but the present invention also adds improvements to this device with regard to measures against dust in the exhaust gas. It is something.

排ガス中のダストは石炭焚きボイラの排ガスで
は10〜20g/m3N程度で極めて多量である。この
排ガスを直接排ガス脱硫装置に通すと、ダストの
付着、閉塞などのトラブルが起り、安定な運転が
できない。更に、煙突からの排煙に多量のダスト
を同伴することは二次公害防止の面から許されな
い。これらの理由により、排ガス脱硫装置に排ガ
スを通す前に電気集塵器などを設置してダストを
予め除去した後、排ガス脱硫装置に通している。
しかし電気集塵器などで処理された排ガス中のダ
スト濃度は、なお100〜500Kg/m3N程度である。
The amount of dust in the exhaust gas from a coal-fired boiler is approximately 10 to 20 g/m 3 N, which is extremely large. If this exhaust gas is directly passed through the exhaust gas desulfurization equipment, problems such as dust adhesion and blockage will occur, making stable operation impossible. Furthermore, from the viewpoint of secondary pollution prevention, it is not permissible to entrain a large amount of dust into the exhaust smoke from the chimney. For these reasons, before passing the exhaust gas through the exhaust gas desulfurization device, an electrostatic precipitator or the like is installed to remove dust beforehand, and then the exhaust gas is passed through the exhaust gas desulfurization device.
However, the dust concentration in exhaust gas treated with an electrostatic precipitator or the like is still about 100 to 500 kg/m 3 N.

先に提案した排ガス脱硫装置は、いろいろな特
徴を有する装置であるが、排ガス中のダスト濃度
が多い場合には、吸着層にダストの付着、閉塞が
起り安定な運転が不可能になる危険性があつた。
The exhaust gas desulfurization equipment proposed earlier has various features, but if there is a high concentration of dust in the exhaust gas, there is a risk that dust will adhere to the adsorption layer and block it, making stable operation impossible. It was hot.

本発明は、先に提案した装置の上記欠点を解消
すべくなされたもので、吸着材の充填層の前段
に、該吸着材よりも粒度の小さい充填材よりなる
充填層(以下、この層をダミー層という)を設
け、排ガス中のダスト濃度の大小に対応して、ダ
ミー層からの充填材の交換量を加減することによ
つて、吸着材の充填層のダスト付着・閉塞のトラ
ブルを防止しようとするものである。
The present invention was made in order to eliminate the above-mentioned drawbacks of the previously proposed device, and includes a packed bed (hereinafter referred to as this layer) made of a filler with a smaller particle size than the adsorbent before the packed bed of adsorbent. By setting up a dummy layer (called a dummy layer) and adjusting the amount of filler exchanged from the dummy layer depending on the dust concentration in the exhaust gas, troubles such as dust adhesion and clogging of the adsorbent filled layer are prevented. This is what I am trying to do.

すなわち、本発明は軸線がほゞ鉛直で同軸線の
まわりに回転自在な円筒形ケージを有し、該ケー
ジに吸着材の充填層を形成し、該ケージの外側と
内側をケーシングとシール装置により円周に沿つ
て少くとも吸着、脱着、冷却及び吸着材交換の四
つのゾーンに区分され、該吸着材により排ガス中
の硫黄酸化物を吸着除去すると共に、該ケージの
回転により吸着材の充填層を上記各ゾーンに順次
移動循環させて、該吸着材の脱着、冷却及び交換
を行なうようにした装置において、上記吸着材の
充填層の外周のケージ内に該吸着材より粒度の小
さな充填材の充填層を設けて、上記排ガスが該充
填材の充填層より吸着材の充填層へ順次通過され
るようにし、かつ各充填層の吸着材及び充填材が
互に独立に交換可能なように構成したことを特徴
とする排ガス脱硫装置を要旨とするものである。
That is, the present invention has a cylindrical cage whose axis is substantially vertical and is rotatable around the coaxial line, a packed layer of adsorbent is formed in the cage, and the outside and inside of the cage are sealed by a casing and a sealing device. It is divided into at least four zones along the circumference: adsorption, desorption, cooling, and adsorbent exchange, and the adsorbent adsorbs and removes sulfur oxides in the exhaust gas, and the rotation of the cage creates a packed bed of adsorbent. In this apparatus, the adsorbent is sequentially moved and circulated through each zone for desorption, cooling, and exchange of the adsorbent, in which a packing material having a particle size smaller than that of the adsorbent is placed in a cage around the outer periphery of the packed bed of the adsorbent. A packed bed is provided so that the exhaust gas passes sequentially from the packed bed of the packing material to the packed bed of the adsorbent, and the adsorbent and the packing material of each packed bed are exchangeable independently of each other. The gist of this invention is an exhaust gas desulfurization device characterized by the following features.

本発明の改良点であるダミー層の充填材は、吸
着材より粒度の小さいものであれば不活性物質で
も、吸着材そのものでもよい。
The filler of the dummy layer, which is an improvement of the present invention, may be an inert substance or the adsorbent itself as long as the particle size is smaller than that of the adsorbent.

以下、本発明を添付図面に従つて更に詳述す
る。
Hereinafter, the present invention will be described in further detail with reference to the accompanying drawings.

第1図において、1は回転ケージで縦型円筒状
をなし、円板上の強固な回転テーブル2の上に固
定され、回転テーブル2は下部を複数個の回転自
在なローラ3により支持されている。4は中央支
柱、5はアームで回転テーブル2の中心に向つて
放射状に複数個あり、回転テーブル2に固定さ
れ、各アーム5に固定されたサイドローラ6によ
り中心が決められ、駆動ローラ7ならびに駆動装
置8により回転テーブル2および回転ケージ1は
中央支柱4を中心として緩速度(例えば5時間〜
10時間で1回転)で回転する。回転速度はガス処
理条件に合わせるように調節が可能である。回転
ケージ1の構造は大規模の商業プラント用として
使用する場合は直径10〜20m、高さ10〜25mとい
う大きさとなるので、なるべく軽量とすることが
望ましく、例えば骨組をパイプ構造とし、内外面
及び中間部に金あみ27及び27′を張り、回転
ケージ1内の内側に吸着材26、その外側に充填
材26′を充填して円筒形の充填層を形成する。
9は外部ケーシング、10は処理ガス入口、1
0′は整流板、11は処理ガス出口、12は脱着
ガス入口、13は脱着ガス出口、14及び14′
は吸着材及び充填材供給層、15及び15′は電
動又は圧気作動ゲートバルプ、16及び16′は
処理ガスの上部への洩れを防ぐマテリアルシー
ル、17及び17′は回転ケージ1に設けられた
吸着材及び充填材のブリツチ防止板、18及び1
8′は吸着材及び充填材排出ゲート、19及び1
9′は排出ホツパ、20及び20′は排出コンベ
ア、21はガスシールである。
In Fig. 1, numeral 1 denotes a rotary cage, which has a vertical cylindrical shape and is fixed on a strong rotary table 2 on a disk, and the rotary table 2 is supported at its lower part by a plurality of rotatable rollers 3. There is. Reference numeral 4 indicates a central support, and reference numeral 5 indicates a plurality of arms radially extending toward the center of the rotary table 2. The center is fixed to the rotary table 2, and the center is determined by side rollers 6 fixed to each arm 5. The drive device 8 moves the rotary table 2 and the rotary cage 1 at a slow speed (for example, for 5 hours or more) around the central column 4.
It rotates at a rate of 1 rotation in 10 hours). The rotation speed can be adjusted to suit gas processing conditions. Since the structure of the rotating cage 1 is 10 to 20 m in diameter and 10 to 25 m in height when used in a large-scale commercial plant, it is desirable to make it as light as possible. Metal threads 27 and 27' are placed in the intermediate portion, and an adsorbent 26 is filled inside the rotary cage 1, and a filler 26' is filled outside the rotating cage 1 to form a cylindrical packed bed.
9 is an external casing, 10 is a processing gas inlet, 1
0' is a current plate, 11 is a processing gas outlet, 12 is a desorption gas inlet, 13 is a desorption gas outlet, 14 and 14'
15 and 15' are electric or pressure-operated gate valves, 16 and 16' are material seals that prevent the process gas from leaking to the top, and 17 and 17' are adsorption layers installed in the rotating cage 1. Blitz prevention plate for materials and fillers, 18 and 1
8' is the adsorbent and filler discharge gate, 19 and 1
9' is a discharge hopper, 20 and 20' are discharge conveyors, and 21 is a gas seal.

第2図は第1図の―断面を示す。第2図に
おいて、bは必要に応じて設けられる予熱ゾーン
で、22は加熱ガス入口、23は加熱ガス出口で
ある。24は冷却ガス入口、25は冷却ガス出口
である。
FIG. 2 shows a - cross section of FIG. 1. In FIG. 2, b is a preheating zone provided as necessary, 22 is a heating gas inlet, and 23 is a heating gas outlet. 24 is a cooling gas inlet, and 25 is a cooling gas outlet.

なお第1図に示した吸着材及び充填材供給装置
を、第2図においては平面的に鎖線で示した1
4,14′。
In addition, the adsorbent and filler supply device shown in FIG.
4,14'.

第3図は第2図のA部を拡大して示したもの
で、回転ケージ1の構造と、ガスシールの構造を
示したものである。回転ケージ1は前記の通り骨
組はパイプの組立構造となつており、金あみ27
及び27′を張り、吸着材26及び充填材26′を
充填する。
FIG. 3 is an enlarged view of section A in FIG. 2, showing the structure of the rotating cage 1 and the structure of the gas seal. As mentioned above, the rotating cage 1 has an assembled structure of pipes, and is made of metal thread 27.
and 27', and filled with adsorbent 26 and filler 26'.

吸着材の粒度は圧力損失を考えて5〜20mm、層
厚は500〜1200mmが好適であり、充填材の粒度は
吸着材に比較して粒度の小さいものを層厚さ100
〜1000mmが好適である。
Considering pressure loss, the particle size of the adsorbent is preferably 5 to 20 mm and the layer thickness is 500 to 1200 mm.The particle size of the filler is smaller than that of the adsorbent, and the layer thickness is 100 mm.
~1000mm is suitable.

また回転ケージ1は隔壁板28によつて仕切ら
れており、隔壁板28の間には断熱材29が充填
され各区画間の伝熱を防止している。30は回転
ケージ1に設けられたアスベスト板製のシール板
で、内外ケーシング9との間のガスシールの役目
をし、さらにガスシールを良くするために、パイ
プ31よりシールガスを吹き出す。また内外ケー
シング9にも断熱材34やライニングされてお
り、高温の加熱、脱着ガスによるケーシングの熱
応力を緩和する。
Further, the rotating cage 1 is partitioned by partition plates 28, and a heat insulating material 29 is filled between the partition plates 28 to prevent heat transfer between each section. Reference numeral 30 denotes a sealing plate made of an asbestos plate provided on the rotating cage 1, which serves as a gas seal between the inner and outer casings 9, and sealing gas is blown out from a pipe 31 in order to further improve the gas sealing. In addition, the inner and outer casings 9 are also lined with a heat insulating material 34 to relieve thermal stress on the casing due to high temperature heating and desorption gas.

第4図は吸着材及び充填材の排出装置を示す。
32及び32′は排出ゲート18及び18′の作動
用エヤシリンダで、排出ホツパ19及び19′の
位置でゲート18及び18′を開いて、吸着材及
び充填材を排出する。
FIG. 4 shows a device for discharging the adsorbent and filler.
32 and 32' are air cylinders for operating the discharge gates 18 and 18', which open the gates 18 and 18' at the positions of the discharge hoppers 19 and 19' to discharge the adsorbent and filler.

なお33は回転テーブル2の補強材である。 Note that 33 is a reinforcing material for the rotary table 2.

次に第2図について作用を説明すると、処理ガ
スは入口10より入り、整流板10′によつて整
流されて回転ケージ1の充填層中の充填材26′
及び吸着材26を貫通して出口11より出る。回
転ケージ1は回転矢印の方向に緩速度で回転する
が、充填層の充填材及び吸着材は一回転の間に吸
着ゾーンaにおいて充填層を貫通する処理ガスよ
りダストの除去及び硫黄酸化物を吸着し、ついで
加熱ゾーンbにおいて22よりの不活性高温ガス
により脱着の適温迄加熱され、ついで、脱着ゾー
ンcにおいて、12よりの不活性ガスおよび水蒸
気の混合物よりなる脱着ガスにより吸着した硫黄
酸化物を放出し、脱着ガスは硫黄酸化物を濃厚に
含んだガスとなり、出口13より図示されていな
い硫黄分回収装置へ送られる。又、排出される加
熱ガスも硫黄分回収装置に送られることは云うま
でもない。次に脱着後の吸着材は冷却ゾーンdに
入り24よりの低温の不活性ガスにより処理ガス
と同程度の温度迄冷却され、再びゲージの回転に
より吸着ゾーンaに入る。前記第1図及び第2図
に関しての説明では、加熱ゾーンbについての説
明がなされているが、脱着ゾーンcでの脱着ガス
を加熱しておけば加熱ゾーンbは必ずしも必要で
はないことは当業者には自明であろう。
Next, to explain the operation with reference to FIG.
and passes through the adsorbent 26 and exits from the outlet 11. The rotating cage 1 rotates at a slow speed in the direction of the rotation arrow, but the filler and adsorbent of the packed bed remove dust and sulfur oxides from the process gas passing through the packed bed in the adsorption zone a during one rotation. The sulfur oxides are adsorbed and then heated in heating zone b by an inert hot gas from 22 to the appropriate temperature for desorption, and then adsorbed in desorption zone c by a desorption gas consisting of a mixture of an inert gas and water vapor from 12. The desorbed gas becomes a gas rich in sulfur oxides, and is sent from the outlet 13 to a sulfur recovery device (not shown). It goes without saying that the heated gas discharged is also sent to the sulfur recovery device. Next, the adsorbent after desorption enters the cooling zone d, where it is cooled down to the same temperature as the process gas by an inert gas at a lower temperature than 24, and then enters the adsorption zone a again by rotation of the gauge. In the explanation regarding FIGS. 1 and 2, heating zone b is explained, but those skilled in the art will understand that heating zone b is not necessarily necessary if the desorption gas in desorption zone c is heated. It should be obvious.

以上説明したように吸着材はケージ1の回転に
ともない吸着、(必要に応じて加熱)、脱着、冷却
のサイクルを繰返すが、吸着材の性能は繰返し使
用回数とともに低下してくる。従つて例えば5〜
15回の繰返し使用後、古い吸着材を排出ゲート1
8より抜き出し、新しい吸着剤を供給槽14より
供給して性能低下を防ぐ。そのため吸着材交換ゾ
ーンeが設けられており、吸着材の性能低下を考
慮しながら更新する。
As explained above, as the cage 1 rotates, the adsorbent repeats the cycle of adsorption, (heating if necessary), desorption, and cooling, but the performance of the adsorbent decreases with the number of repeated uses. Therefore, for example 5~
After 15 repeated uses, the old adsorbent is discharged from gate 1.
8, and new adsorbent is supplied from the supply tank 14 to prevent performance deterioration. Therefore, an adsorbent exchange zone e is provided, and the adsorbent is updated while taking into account the performance deterioration of the adsorbent.

同様に、排ガス中のダストが付着した充填材
も、該交換ゾーンeで排ガス通過時の圧力損失の
増大を防止するに適した量が交換される。回転ケ
ージ1の回転は連続でもよく、また、隔壁板28
によつて仕切られた1区画だけ回転しては停止す
る間けつ回転でもよい。吸着材としては、本発明
による装置の場合、広い通過面積にともない比較
的長い通過時間が得られるので、高級な活性炭を
使用する必要がなく、安価な半成コークス等が使
用できるので、コスト的に有利であり、さらに吸
着材の廃材を燃料として使用すれば、さらに脱硫
コストの低減を図ることができる。また吸着材は
サイクル中補充交換以外は静止しているので相互
の摩擦による粉化ロスが少ない。
Similarly, the filler to which dust in the exhaust gas has adhered is also replaced in the exchange zone e in an amount suitable for preventing an increase in pressure loss when the exhaust gas passes through. The rotation of the rotating cage 1 may be continuous, and the partition plate 28 may be rotated continuously.
Intermittent rotation may also be used, in which only one section partitioned by is rotated and then stopped. As for the adsorbent, in the case of the device according to the present invention, a relatively long passage time can be obtained due to the large passage area, so there is no need to use high-grade activated carbon, and inexpensive semi-formed coke etc. can be used, so the cost is reduced. Furthermore, if adsorbent waste is used as fuel, desulfurization costs can be further reduced. In addition, since the adsorbent remains stationary except for replenishment during the cycle, there is little powdering loss due to mutual friction.

以上詳細説明した本発明に係る装置の特長を整
理して次に示す。
The features of the device according to the present invention explained in detail above are summarized below.

(1) 縦型であり敷地面積が少くてすむ。(1) It is vertical and requires less site area.

(2) 本質的に連続式であり処理ガスの圧力変動が
ないので燃焼装置への影響がない。
(2) Since it is essentially a continuous type and there is no pressure fluctuation of the processing gas, there is no effect on the combustion equipment.

(3) 酸化硫黄ガスの濃度及びダスト濃度の変動に
対しては回転数の制御により最適の脱硫条件を
確保できる。
(3) Optimum desulfurization conditions can be ensured by controlling the rotation speed in response to fluctuations in the concentration of sulfur oxide gas and dust concentration.

(4) 吸着材はサイクル中、大気に触れることがな
いので粉塵爆発や燃焼等の事故の発生を防止で
きる。
(4) Since the adsorbent does not come into contact with the atmosphere during the cycle, accidents such as dust explosions and combustion can be prevented.

(5) 充填材は一定期間後定期的に交換されるため
ダストによる目塞りを未然に防ぐことができ、
処理ガス中にダストを含有している場合でも支
障がなく、またダストによる圧力変動が少な
い。
(5) Since the filling material is replaced periodically after a certain period of time, clogging due to dust can be prevented.
There is no problem even if the processing gas contains dust, and pressure fluctuations due to dust are small.

(6) 吸着材及び充填材の変換は機械化することが
容易で、無人運転も可能である。
(6) The conversion of adsorbents and fillers is easy to mechanize, and unmanned operation is also possible.

(7) ガスの通過面積を大きくとることができるの
で、高級な吸着材を使用する必要がなく、安価
な半成コークスなどが吸着材として使用でき、
また使用済の吸着材を燃料として使用すること
ができるため、脱硫コストを低減することがで
きる。
(7) Since the gas passage area can be large, there is no need to use high-grade adsorbents, and inexpensive semi-formed coke can be used as the adsorbent.
Furthermore, since used adsorbent can be used as fuel, desulfurization costs can be reduced.

(8) 湿式法のような多量の水や再加熱用燃料を必
要としない。
(8) It does not require large amounts of water or reheating fuel like the wet method.

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

第1図及び第2図は本発明の一実施例の側面図
及び平面図、第3図は第2図のA部の拡大説明
図、第4図は本発明の吸着材及び充填材の排出装
置の部分図である。
Figures 1 and 2 are a side view and a plan view of an embodiment of the present invention, Figure 3 is an enlarged explanatory view of section A in Figure 2, and Figure 4 is the discharge of the adsorbent and filler of the present invention. FIG. 3 is a partial diagram of the device.

Claims (1)

【特許請求の範囲】[Claims] 1 軸線がほゞ鉛直で同軸線のまわりに回転自在
な円筒形ケージを有し、該ケージに吸着材の充填
層を形成し、該ケージの外側と内側をケーシング
とシール装置により円周に沿つて少くとも吸着、
脱着、冷却及び吸着材交換の四つのゾーンに区分
され、該吸着材により排ガス中の硫黄酸化物を吸
着除去すると共に、該ケージの回転により吸着材
の充填層を上記各ゾーンに順次移動循環させて、
該吸着材の脱着、冷却及び交換を行なうようにし
た装置において、上記吸着材の充填層の外周のケ
ージ内に該吸着材より粒度の小さな充填材の充填
層を設けて、上記排ガスが該充填材の充填層より
吸着材の充填層へ順次通過されるようにし、かつ
各充填層の吸着材及び充填材が互に独立に交換可
能なように構成したことを特徴とする排ガス脱硫
装置。
1. It has a cylindrical cage whose axis is almost vertical and is rotatable around the coaxial line, a packed layer of adsorbent is formed in the cage, and the outside and inside of the cage are sealed along the circumference by a casing and a sealing device. At least it absorbs,
Divided into four zones: desorption, cooling, and adsorbent exchange, the adsorbent adsorbs and removes sulfur oxides from exhaust gas, and the rotation of the cage sequentially moves and circulates the packed bed of adsorbent to each zone. hand,
In an apparatus for desorbing, cooling, and exchanging the adsorbent, a packed bed of a filler having a particle size smaller than that of the adsorbent is provided in a cage around the outer periphery of the packed bed of the adsorbent, so that the exhaust gas is absorbed by the packed bed. 1. An exhaust gas desulfurization apparatus characterized in that the exhaust gas is sequentially passed from a packed bed of material to a packed bed of adsorbent, and that the adsorbent and filler of each packed bed are exchangeable independently of each other.
JP3738680A 1980-03-26 1980-03-26 Desulfurizer of waste gas Granted JPS56136621A (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
JP3738680A JPS56136621A (en) 1980-03-26 1980-03-26 Desulfurizer of waste gas
CA000373855A CA1151075A (en) 1980-03-26 1981-03-25 Exhaust gas desulfurization apparatus
DE19813112482 DE3112482C2 (en) 1980-03-26 1981-03-26 Device for desulphurising exhaust gases

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3738680A JPS56136621A (en) 1980-03-26 1980-03-26 Desulfurizer of waste gas

Publications (2)

Publication Number Publication Date
JPS56136621A JPS56136621A (en) 1981-10-26
JPS631089B2 true JPS631089B2 (en) 1988-01-11

Family

ID=12496084

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3738680A Granted JPS56136621A (en) 1980-03-26 1980-03-26 Desulfurizer of waste gas

Country Status (3)

Country Link
JP (1) JPS56136621A (en)
CA (1) CA1151075A (en)
DE (1) DE3112482C2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07331684A (en) * 1994-06-14 1995-12-19 Keiji Otsuka Piping fitting and piping method
JPH08165668A (en) * 1994-12-12 1996-06-25 Nichikon:Kk Assembly manhole

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4880985A (en) * 1988-10-05 1989-11-14 Douglas Jones Detached collimator apparatus for radiation therapy
CN102049176A (en) * 2009-11-06 2011-05-11 成都华西工业气体有限公司 Flue gas desulfurization process adopting high-gravity solvent cycle absorption method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07331684A (en) * 1994-06-14 1995-12-19 Keiji Otsuka Piping fitting and piping method
JPH08165668A (en) * 1994-12-12 1996-06-25 Nichikon:Kk Assembly manhole

Also Published As

Publication number Publication date
DE3112482C2 (en) 1985-04-18
CA1151075A (en) 1983-08-02
JPS56136621A (en) 1981-10-26
DE3112482A1 (en) 1982-01-07

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