JPS62282625A - Agitating circulation apparatus - Google Patents

Agitating circulation apparatus

Info

Publication number
JPS62282625A
JPS62282625A JP61123450A JP12345086A JPS62282625A JP S62282625 A JPS62282625 A JP S62282625A JP 61123450 A JP61123450 A JP 61123450A JP 12345086 A JP12345086 A JP 12345086A JP S62282625 A JPS62282625 A JP S62282625A
Authority
JP
Japan
Prior art keywords
slurry
bubbles
tank
partition plate
supply pipe
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
Application number
JP61123450A
Other languages
Japanese (ja)
Inventor
Takanori Nakamoto
隆則 中本
Ryoichi Miyataka
宮高 良一
Masakatsu Nishimura
西村 正勝
Tsukasa Nishimura
西村 士
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 Power Ltd
Original Assignee
Babcock Hitachi KK
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 Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP61123450A priority Critical patent/JPS62282625A/en
Publication of JPS62282625A publication Critical patent/JPS62282625A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01FMIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F33/00Other mixers; Mixing plants; Combinations of mixers
    • B01F33/40Mixers using gas or liquid agitation, e.g. with air supply tubes
    • B01F33/402Mixers using gas or liquid agitation, e.g. with air supply tubes comprising supplementary stirring elements

Abstract

PURPOSE:To carry out the continuous operation of a circulating pump and the stable treatment operation of a waste gas by providing an opening of gas supply pipe in the stream just behind agitating blades, a partition plate which is also served as a support of the supply pipe, and a discharge stud on the tank wall behind the partition plate. CONSTITUTION:Air 103 supplied through an oxidizing air supply 102 near agitating blades 105 of an air blowing agitator 101 is changed into fine bubbles by the shearing force generated by the rotation of the agitating blades, and a mixed stream of slurry and the bubbles are dispersed by the propelling force of the agitator toward the center part of a corculating tank 104. In the rear part of the agitating blades least bubbles are contained thereby, concretely, speaking the bubbles are scarest in the near part of the discharge stud 107 of the circulating slurry. Moreover, as the partition plate 106 is provided in front of the discharge stud 107 of the circulating slurry, bubbles are not contained in the slurry discharged from the discharge stud 107 of the circulating slurry, and the cavitation in a pump does not therefore occur.

Description

【発明の詳細な説明】 3、発明の詳細な説明 〔産業上の利用分野〕 本発明は脱硫装置に係り、副生品として石膏を回収する
1塔式湿式排煙脱硫装置の攪拌循環装置に関するもので
ある。
Detailed Description of the Invention 3. Detailed Description of the Invention [Field of Industrial Application] The present invention relates to a desulfurization device, and more particularly, to a stirring circulation device for a single-column wet flue gas desulfurization device that recovers gypsum as a by-product. It is something.

〔従来の技術〕[Conventional technology]

現在実用化されている湿式排煙脱硫装置はカルシウム系
の吸収剤を使用し副生品として石膏を回収するものが主
流となっている。
The mainstream wet flue gas desulfurization equipment currently in practical use uses a calcium-based absorbent and recovers gypsum as a byproduct.

第5図はカルシウム系吸収剤を用いて石膏を回収するフ
ローシートであって、同図により従来技術について説明
する。ボイラ等からの排ガス201′は除塵塔入口ダク
ト202を通って除塵塔203に導かれ、ここで除塵塔
1i m ! 204からのスラリがスプレノズル20
5からスプレされることによって除塵冷却され、吸収塔
206に送られる。吸収塔206内では吸収塔循環槽2
07から吸収塔循環ポンプ208を介して管路209を
経て供給されるカルシウム系吸収剤スラリがノズル21
0からスプレされ、排ガス中の硫黄酸化物が吸収除去さ
れる。排ガス中にある同伴ミストはデミスタ211によ
って除去され、清浄ガス212がダクト213を介して
図示しない煙道へ導かれる。一方硫黄酸化物を吸収した
カルシウム系吸収剤を含む循環液スラリは吸収塔206
及び吸収塔循環槽207内で亜硫酸カルシウムに変化す
るがこの一部は吸収塔206内において排ガス中の酸素
によって酸化され石膏になる。この吸収剤スラリは吸収
塔循環ポンプ208を介して管路209から吸収塔20
6内へ、または連結管214を介して除塵塔循環槽20
4へ供給される。除塵塔循環槽204内のスラリは除塵
塔203内で排ガスと接触し、排ガス中の硫黄酸化物を
除去することによりスラリ中の未反応の石灰石の量を減
少させて副生石膏回収系へ抜き出される。すなわちまず
反応槽215に送られ、ここで硫酸216を添加するこ
とによって含有される未反応炭酸カルシウムが石膏に転
換され、また亜硫酸カルシウムの酸化に好適なPHに調
整される。
FIG. 5 is a flow sheet for recovering gypsum using a calcium-based absorbent, and the prior art will be explained with reference to the same figure. Exhaust gas 201' from a boiler or the like is led to a dust removal tower 203 through a dust removal tower inlet duct 202, where the dust removal tower 1i m! Slurry from 204 is sent to spray nozzle 20
5 to remove dust and cool it, and then sent to an absorption tower 206. In the absorption tower 206, the absorption tower circulation tank 2
Calcium-based absorbent slurry is supplied from 07 through an absorption tower circulation pump 208 to a pipe 209 to a nozzle 21.
It is sprayed from zero to absorb and remove sulfur oxides in the exhaust gas. Entrained mist in the exhaust gas is removed by a demister 211, and clean gas 212 is guided to a flue (not shown) via a duct 213. On the other hand, the circulating fluid slurry containing the calcium-based absorbent that has absorbed sulfur oxides is stored in the absorption tower 206.
It changes into calcium sulfite in the absorption tower circulation tank 207, but a part of this is oxidized by oxygen in the exhaust gas in the absorption tower 206 and becomes gypsum. This absorbent slurry is transferred to the absorption tower 20 from a pipe 209 via an absorption tower circulation pump 208.
6 or through the connecting pipe 214 to the dust removal tower circulation tank 20.
4. The slurry in the dust removal tower circulation tank 204 comes into contact with exhaust gas in the dust removal tower 203, and by removing sulfur oxides from the exhaust gas, the amount of unreacted limestone in the slurry is reduced, and the slurry is extracted to the by-product gypsum recovery system. It will be done. That is, it is first sent to a reaction tank 215, where the unreacted calcium carbonate contained therein is converted into gypsum by adding sulfuric acid 216, and the pH is adjusted to a value suitable for oxidizing calcium sulfite.

このスラリは酸化塔供給ポンプ217により酸化塔21
8に供給され、ここで亜硫酸カルシウムは空気219に
よって石膏に転換される。得られた石膏スラリはシラフ
ナ220へ導かれ、固液分離された後に遠心分離機22
]で脱水され、石膏222が回収される。固液分離及び
脱水時の濾過水223は石灰石スラリの調整型に再使用
される。なお硫黄酸化物の吸収剤である石灰石スラリは
石灰石スラリタンク224において、石灰石225、濾
過水223及び補給水226により調整され、ブリード
ポンプ227により吸収塔循環N!207内に供給され
る。
This slurry is supplied to the oxidation tower 21 by the oxidation tower supply pump 217.
8, where the calcium sulfite is converted to gypsum by air 219. The obtained gypsum slurry is led to Shirafuna 220, where it is separated into solid and liquid, and then sent to a centrifuge 22.
], and gypsum 222 is recovered. The filtered water 223 during solid-liquid separation and dewatering is reused to prepare limestone slurry. Note that the limestone slurry, which is an absorbent for sulfur oxides, is adjusted in a limestone slurry tank 224 with limestone 225, filtered water 223, and make-up water 226, and is circulated in the absorption tower by a bleed pump 227. 207.

このように従来法においては硫黄酸化物の吸収過程で完
全に石膏を得ることは困難であるため、通常は吸収系で
生ずる亜硫酸塩を別途に設けた酸化塔218において石
膏にする方法が採用されてきた。しかし近年酸化塔21
8を省略し、吸収部において硫黄酸化物の硫酸塩への酸
化を進めようとする多くの方法が提案されている。これ
らは酸化触媒を利用する方法(特公昭58−36619
号)、吸収塔循環槽207や別に設けた反応槽に空気を
吹き込む方法(特開昭58−92452、同じ< 95
543)あるいは二段脱硫法(特開昭58−74126
)等を挙げることができる。しかし触媒を使用する方法
では、これを効率よ(回収しなければ経済的には成り立
たず、また空気吹込法においては多量の空気を微細気泡
として供給しない限り、従来の酸化塔218に代りうる
ほどの速度で亜硫酸塩を酸化するのは困難であった。
In this way, in the conventional method, it is difficult to completely obtain gypsum in the process of absorbing sulfur oxides, so a method is usually adopted in which sulfites generated in the absorption system are turned into gypsum in a separate oxidation tower 218. It's here. However, in recent years oxidation tower 21
Many methods have been proposed in which oxidation of sulfur oxides to sulfates is proceeded in the absorption section by omitting step 8. These methods utilize oxidation catalysts (Japanese Patent Publication No. 58-36619
No.), a method of blowing air into the absorption tower circulation tank 207 or a separately provided reaction tank (JP-A-58-92452, same <95
543) or two-stage desulfurization method (JP-A-58-74126)
) etc. However, the method using a catalyst is not economically viable unless it is efficiently (recovered), and the air blowing method cannot replace the conventional oxidation tower 218 unless a large amount of air is supplied as fine bubbles. It was difficult to oxidize sulfite at a rate of .

これに対して本発明者らは湿式排煙脱硫方法の合理化を
目的にして新たなプロセスを提案したが、これは第3〜
4図に示すものであって、111は排ガス流入方向、1
12は除塵器、113は吸収部、114はデミスタ、1
15は石灰石スラリ供給管、116は吸収部循環槽、1
17は吸収部循環ポンプ、119は除塵部循環槽、12
2はスラリ排出管、123は集水器、101は空気吹込
用攪拌機、102は空気供給管、103は空気流入方向
、104は除塵部循環槽、105は攪拌翼、108はス
ラリ送出方向である。従来ベンチュリ型で行なってきた
除塵をスプレ方式にして吸収塔下部に組入れ除塵部11
2を設けるとともに、塔底部を除塵用循環槽104とし
除塵に供されたスラリは直接この循環槽104中に落下
させる。また除塵後の排ガスは塔上部の吸収部113に
到り、スプレされたカルシウム系スラリと自流接触する
ことにより含有される硫黄酸化物が除去される。吸収部
113のスラリは集水器123によって捕集され、別途
に設けられた吸収部循環槽116に戻される。除塵塔循
環槽104中に空気を供給して石膏を生成させ、専用酸
化塔を省略する。また吸収剤である石灰石スラリは吸収
部循環槽116に供給し、この槽内スラリの一部を抜き
出して除塵部循環槽104へ供給するものである。
In response, the present inventors proposed a new process with the aim of streamlining the wet flue gas desulfurization method, but this
4, 111 is the exhaust gas inflow direction, 1
12 is a dust remover, 113 is an absorption section, 114 is a demister, 1
15 is a limestone slurry supply pipe, 116 is an absorption section circulation tank, 1
17 is an absorption section circulation pump, 119 is a dust removal section circulation tank, 12
2 is a slurry discharge pipe, 123 is a water collector, 101 is an air blowing agitator, 102 is an air supply pipe, 103 is an air inflow direction, 104 is a dust removal section circulation tank, 105 is an agitation blade, and 108 is a slurry delivery direction. . Dust removal, which was conventionally carried out using a venturi type, has been changed to a spray method and incorporated into the lower part of the absorption tower.
2 is provided, and the bottom of the tower is used as a circulation tank 104 for dust removal, and the slurry used for dust removal is directly dropped into this circulation tank 104. Further, the exhaust gas after dust removal reaches the absorption section 113 in the upper part of the tower, and the sulfur oxides contained therein are removed by self-flow contact with the sprayed calcium-based slurry. The slurry in the absorption section 113 is collected by a water collector 123 and returned to the absorption section circulation tank 116 provided separately. Air is supplied into the dust removal tower circulation tank 104 to generate gypsum, and a dedicated oxidation tower is omitted. Limestone slurry, which is an absorbent, is supplied to the absorption section circulation tank 116, and a part of the slurry in this tank is extracted and supplied to the dust removal section circulation tank 104.

本発明者らの知見によれば一般に、循環槽内における亜
硫酸塩の酸化手段としてこの循環槽に設置された攪拌機
の翼近傍に空気を供給することによりよい酸化結果が得
られる。このとき塔内にスプレあるいは石膏を回収する
ために気泡を強制的に分散させた吸収液をポンプによっ
て循環槽から送り出さなければならないが、このときポ
ンプが空気を吸い込むことによって空回り(キャビテー
ションという)を起すという問題が生ずる。よく知られ
るようにポンプがキャビテーションを起すと、ポンプの
運転が不可能となり脱硫装置の運転に支障を来すことに
なる。上記のように循環槽内に空気を供給して亜硫酸塩
の酸化を促進させようとする提案はすでしこいくつか見
られるが、キャビテーション対策を講したものは見当ら
ない。一方ポンプのキャビテーションとは別に空気供給
管の先端を攪拌機翼近傍にまで到達させるためには、通
常長さ0.3〜2mの供給管が必要で、タンク内の攪拌
流で振動あるいは破損の恐れがあるため、安定した微細
気泡を供給することは困鑑性があった。
According to the findings of the present inventors, good oxidation results can generally be obtained by supplying air near the blades of an agitator installed in the circulation tank as a means for oxidizing sulfite in the circulation tank. At this time, in order to collect the spray or gypsum in the tower, the absorption liquid in which air bubbles are forcibly dispersed must be sent out from the circulation tank by a pump, but at this time, the pump sucks in air, which prevents it from idling (called cavitation). The problem arises. As is well known, when cavitation occurs in the pump, it becomes impossible to operate the pump, causing problems in the operation of the desulfurization equipment. As mentioned above, there have been several proposals to promote the oxidation of sulfites by supplying air into the circulation tank, but none have been found to take measures against cavitation. On the other hand, apart from pump cavitation, in order to reach the tip of the air supply pipe close to the agitator blade, a supply pipe with a length of 0.3 to 2 m is usually required, and there is a risk of vibration or damage due to the stirring flow in the tank. Therefore, it has been difficult to supply stable microbubbles.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

上記のように循環槽内に安定した微細気泡を供給するこ
とと、一方ポンプのキャビテーションを防止するために
ポンプの吸込み側に対し気泡の少ない流動物を送り込む
という問題を解決する必要があった。本発明は上記の問
題点を解決するためになされたものである。
As mentioned above, it was necessary to solve the problems of supplying stable microbubbles into the circulation tank and, on the other hand, feeding a fluid with few bubbles to the suction side of the pump in order to prevent cavitation of the pump. The present invention has been made to solve the above problems.

〔問題点を解決するための手段〕[Means for solving problems]

上記の目的は攪拌機翼の直近背後位置に前記空気供給管
を設けるとともに、微細気泡が最も少ない撹拌機背後の
循環槽側壁から、前記空気供給管の支持を兼ねる仕切板
を隔ててから前記吸収液スラリを槽外へ送出することに
より達成される。
The purpose of the above is to install the air supply pipe immediately behind the stirrer blade, and to separate the absorbent liquid from the side wall of the circulation tank behind the stirrer with the least amount of microbubbles through a partition plate that also serves as support for the air supply pipe. This is accomplished by pumping the slurry out of the tank.

〔作用〕[Effect]

上記により気泡は定常的かつ安定的に循環槽内に供給さ
れ、仕切板を設けて気泡の少な位置から液を抜き出すた
め循環ポンプに気泡が巻き込まれることなく、キャビテ
ーションを起す恐れもない。
As a result of the above, air bubbles are constantly and stably supplied into the circulation tank, and since the partition plate is provided and the liquid is extracted from a position where there are few air bubbles, air bubbles are not caught in the circulation pump, and there is no fear of cavitation.

〔実施例〕〔Example〕

第1〜2図は本発明の一実施例を示す湿式排煙脱硫装置
の循環槽104における空気吹込攪拌機101回りの断
面を示した図である。
FIGS. 1 and 2 are cross-sectional views of the area around the air blowing agitator 101 in the circulation tank 104 of a wet flue gas desulfurization apparatus showing an embodiment of the present invention.

101は空気吹込用攪拌機、102は空気供給管、10
3は空気流入方向、104は除塵部循環槽、105は攪
拌翼、 106は仕切板、107は抜出し座、108は
スラリ送出方向である。
101 is an air blowing agitator, 102 is an air supply pipe, 10
3 is an air inflow direction, 104 is a dust removal section circulation tank, 105 is an agitation blade, 106 is a partition plate, 107 is an extraction seat, and 108 is a slurry delivery direction.

空気吹込攪拌機101の攪拌翼105近傍に酸化用空気
供給管102から供給された空気103は攪拌翼の回転
により生ずる剪断力で微細な気泡となり、さらに攪拌機
の推力によりスラリと気泡の混合流体は循環槽104中
心部に向かって分散されるにのため攪拌翼105の背後
は最も気泡が少ない。これは本発明者らが0.8m直径
の槽及び2.2m直径の槽での実験によって得られたも
のである。このように攪拌翼105の背後に設けられた
循環スラリ抜出し座107近傍が最も気泡が少なく、さ
らに循環スラリ抜出し座107の手前には仕切板106
が取り付けられているため、循環スラリ抜出し座107
から抜き出されるスラリ中には気泡が含まれておらず、
ポンプのキャビテーションは起らない。また循環槽10
4内にはスラリ固形物のタンク底部への沈積を防止する
ための攪拌流れがあり、空気供給管102はかなりの流
体抵抗を受けるが、この仕切板106が支持するために
振動が起きず良好に気泡を発生させることができる6も
し仕切板がなければ振動が発生し、安定的に翼近傍に空
気を供給できず粗大な気泡ができ、気泡の分散効率を著
しく低下させることになる。
Air 103 supplied from the oxidizing air supply pipe 102 near the stirring blades 105 of the air blowing stirrer 101 becomes fine bubbles due to the shear force generated by the rotation of the stirring blades, and the mixed fluid of slurry and bubbles is further circulated by the thrust of the stirrer. Since the air bubbles are dispersed toward the center of the tank 104, there are the fewest air bubbles behind the stirring blades 105. This was obtained by the inventors through experiments in a 0.8 m diameter tank and a 2.2 m diameter tank. In this way, the vicinity of the circulating slurry extracting seat 107 provided behind the stirring blade 105 has the least amount of air bubbles, and furthermore, in front of the circulating slurry extracting seat 107, there is a partition plate 106.
is installed, the circulation slurry extraction seat 107
There are no air bubbles in the slurry extracted from the
Pump cavitation does not occur. Also, the circulation tank 10
4 has an agitating flow to prevent slurry solids from settling at the bottom of the tank, and the air supply pipe 102 is subject to considerable fluid resistance, but because it is supported by this partition plate 106, vibration does not occur and the flow is smooth. 6. If there is no partition plate, vibrations will occur, and air cannot be stably supplied near the blades, resulting in the formation of coarse bubbles, which will significantly reduce the bubble dispersion efficiency.

〔発明の効果〕〔Effect of the invention〕

本発明の実施により吸収酸化を1塔で行なう湿式排煙脱
硫装置において、空気供給管の支持が安定し、しかも循
環ポンプのキャビテーションがなくなり循環ポンプの連
続運転ができ、排ガス処理操作を安定的に実施すること
が可能となり、酸化効果が著しく向上した。
By implementing the present invention, in a wet flue gas desulfurization system that performs absorption oxidation in one tower, the support of the air supply pipe is stable, cavitation of the circulation pump is eliminated, the circulation pump can be operated continuously, and the flue gas treatment operation is stable. The oxidation effect was significantly improved.

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

第1〜2図は本発明に係る攪拌循環槽の一実施例を示す
側面図及び平面図、第3〜4図は本発明の適用が可能な
排煙脱硫装置のフローシート図、第5図は従来技術の排
煙脱硫装置のフローシートを示す図である。本発明に係
る攪拌循環槽を適用可能な装置のフローシートを示す。
Figures 1 and 2 are a side view and a plan view showing an embodiment of the stirring circulation tank according to the present invention, Figures 3 and 4 are flow sheet diagrams of a flue gas desulfurization apparatus to which the present invention can be applied, and Figure 5. 1 is a diagram showing a flow sheet of a conventional flue gas desulfurization device. 1 shows a flow sheet of an apparatus to which the stirring circulation tank according to the present invention can be applied.

Claims (1)

【特許請求の範囲】[Claims] 1、スラリ状流動物を収容する槽と、気体を流動物内に
供給する供給管と、前記流動物と前記気体とを分散攪拌
する攪拌翼を備える攪拌機と、前記流動物を槽外に送出
させる抜出し座並びに循環ポンプとを具有する攪拌循環
装置において、前記攪拌翼の直近後方の流路に前記気体
供給管の開口と、この供給管の支持を兼ねる仕切板と、
この仕切板のさらに後方の槽壁に前記抜出し座を設けた
ことを特徴とする攪拌循環装置。
1. A tank containing a slurry-like fluid, a supply pipe for supplying gas into the fluid, an agitator equipped with stirring blades for dispersing and stirring the fluid and the gas, and sending the fluid out of the tank. In the agitation circulation device comprising an extraction seat and a circulation pump, an opening of the gas supply pipe is provided in a flow path immediately behind the agitation blade, and a partition plate that also serves as support for the supply pipe;
A stirring circulation device characterized in that the extraction seat is provided on a tank wall further behind the partition plate.
JP61123450A 1986-05-30 1986-05-30 Agitating circulation apparatus Pending JPS62282625A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61123450A JPS62282625A (en) 1986-05-30 1986-05-30 Agitating circulation apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61123450A JPS62282625A (en) 1986-05-30 1986-05-30 Agitating circulation apparatus

Publications (1)

Publication Number Publication Date
JPS62282625A true JPS62282625A (en) 1987-12-08

Family

ID=14860907

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61123450A Pending JPS62282625A (en) 1986-05-30 1986-05-30 Agitating circulation apparatus

Country Status (1)

Country Link
JP (1) JPS62282625A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1995033552A1 (en) * 1994-06-09 1995-12-14 Abb Environmental Systems Improved entrainment separator for high velocity gases and reheating of scrubber gases
US5486341A (en) * 1994-06-09 1996-01-23 Abb Environmental Systems, Div. Of Abb Flakt, Inc. Entrainment separator for high velocity gases
US5820831A (en) * 1994-06-09 1998-10-13 Abb Environmental Systems, Div. Of Abb Flakt, Inc. Method and apparatus for preparing calcium carbonate for scrubbing sulfur oxides from combustion effluents

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1995033552A1 (en) * 1994-06-09 1995-12-14 Abb Environmental Systems Improved entrainment separator for high velocity gases and reheating of scrubber gases
US5486341A (en) * 1994-06-09 1996-01-23 Abb Environmental Systems, Div. Of Abb Flakt, Inc. Entrainment separator for high velocity gases
US5662721A (en) * 1994-06-09 1997-09-02 Abb Environmental Systems, Div.Of Abb Flakt, Inc. Entrainment separator for high velocity gases
US5820831A (en) * 1994-06-09 1998-10-13 Abb Environmental Systems, Div. Of Abb Flakt, Inc. Method and apparatus for preparing calcium carbonate for scrubbing sulfur oxides from combustion effluents
CN1094069C (en) * 1994-06-09 2002-11-13 阿尔斯托姆动力公司 Improved entrainment separator for high velocity gases and reheating of scrubber gases

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