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JPS6143087B2 - - Google Patents
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JPS6143087B2 - - Google Patents

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Publication number
JPS6143087B2
JPS6143087B2 JP53118375A JP11837578A JPS6143087B2 JP S6143087 B2 JPS6143087 B2 JP S6143087B2 JP 53118375 A JP53118375 A JP 53118375A JP 11837578 A JP11837578 A JP 11837578A JP S6143087 B2 JPS6143087 B2 JP S6143087B2
Authority
JP
Japan
Prior art keywords
gas
duct
cooling tower
degrees
angle
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
JP53118375A
Other languages
Japanese (ja)
Other versions
JPS5544366A (en
Inventor
Shigeru Nozawa
Osamu Kanda
Tsukasa Nishimura
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 JP11837578A priority Critical patent/JPS5544366A/en
Publication of JPS5544366A publication Critical patent/JPS5544366A/en
Publication of JPS6143087B2 publication Critical patent/JPS6143087B2/ja
Granted legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Gas Separation By Absorption (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明は湿式排煙脱硫装置に関し、さらに詳し
くは、冷却塔と吸収塔を有する湿式排煙脱硫装置
において、冷却塔以降の装置内のガスの偏流を改
善した前記装置に関する。 冷却塔および吸収塔を備えた排煙脱硫装置の一
般的な構成を第1図に基いて説明する。図におい
て、被処理ガスはライン1から冷却塔10に導入
され、ここでライン14から供給される冷却液と
接触させ、一部のSO2の吸収と除じんを行なつた
後、ダクト2および該ダクト内のミストエリミネ
ータ4を通つて吸収塔20に送られる。吸収塔2
0で被処理ガスはライン24から供給される吸収
液(例えば石灰スラリー)と接触し、ガス中の
SO2が除去された後、ライン3を通つて排出され
る。吸収液は、吸収塔循環タンク40から循環ポ
ンプ60により、ライン21および24を通つて
吸収塔20へ送られ、一部はライン23から系外
へ排出されるか、または冷却塔循環タンク30に
送られる。吸収塔20からは吸収液がライン25
を通つて再び吸収塔循環タンク40に戻される。
冷却塔10においては、冷却水が冷却塔循環タン
ク30からライン11、冷却塔循環ポンプ50、
ライン12、ライン14を通つて冷却塔10内に
戻され、一部はライン13から系外に排出され
る。一方、吸収塔循環タンク40には、吸収剤が
ライン26から補給されるが、この吸収塔循環タ
ンク40内で吸収液は吸収剤の溶解によつてPHを
回復し、前記のように再び吸収塔20に送られ
る。 上記冷却塔10において被処理ガス中のダスト
を分離除去する場合、除去されたダストを含む冷
却液は冷却塔循環タンク30を介して冷却塔10
に再循環されるが、この際、冷却塔10でスプレ
された循環液の液滴、またはスプレされた循環液
をガスとの混合、接触により発生する微細なミス
トは、ガス流に同伴されて飛散する。これらのダ
ストを含むミストを除去するために、吸収塔20
に到る連通部にミストエリミネータ4が設置され
ている。このミストエリミネータ4のミスト除去
性能を充分に発揮させるためには、被処理ガスを
ミストエリミネータ4の型式に合つたガス流速に
整流してミストエリミネータ4に流入させる必要
がある。これはミストエリミネータ4のミスト捕
集原理が慣性衝突を利用していること、および捕
集されたミストが所定量以上のガス流速になれば
再飛散されるのを防止することによる。 従来、ミストエリミネータ4の入口部のガス流
速を単に整流するために、ガス流路に整流板(バ
ツフルプレート等)を挿入することが行なわれて
いるが、被処理ガスが石炭焚ボイラ排ガスのよう
にフライアツシユ等の固形物が多く含まれるガス
の場合には、冷却塔循環液中の固形物濃度が高く
なり、整流板およびダクト2内にフライアツシ
ユ、硫酸カルシウム等の固形物が多く付着し、ド
ラフト損失の急激な上昇を生じ、装置の連続運転
が困難になるという問題がある。このようなダク
ト2内の固形物の付着は、整流板を設けない場で
も問題となり、特にダクト2の天井部、底面部に
多く付着するので、長期連続運転の場合には、ド
ラフト損失が過大になるという欠点がある。 本発明の目的は、上記従来技術の欠点を除去
し、冷却塔で冷却された被処理ガスがミストエリ
ミネータに入る際のダクト内のガスの偏流を可及
的に小さくし、ミストエリミネータの分離効率を
向上させるとともに、ダクト内の固形物の付着を
防止することができる湿式排煙脱硫装置を提供す
ることにある。 上記目的を達成するため、本発明は、冷却塔か
らミストエリミネータに到るダクトを、フライア
ツシユ等の固形物の付着、堆積およびドラフト損
失が少なくなるような形状にしたものである。 すなわち、本発明は、被処理ガスを冷却液のス
プレ手段を備えた冷却塔を通過させ、冷却された
前記ガスを該冷却塔の側部からミストエリミネー
タを有するダクトを介して吸収塔に導入し、該吸
収塔内の吸収液と反応させて前記ガス中の硫黄酸
化物を吸収する湿式排煙脱硫装置において、前記
冷却塔からミストエリミネータに到るダクト内壁
の水平から傾斜角度を天井面部で約5度、底面部
で約15度とすることを特徴とするものである。 以下、本発明を図面によりさらに詳細に説明す
る。 第2図は、本発明における冷却塔からミストエ
リミネータに到るダクトの形状を示す概略断面図
である。ガス中のダストの付着または堆積を防止
するためには、ダクト2内壁の天井面部の水平面
となす角度Aを5度、またダクト内壁底面の水平
面となす角度Bを15度とすることが最も好まし
い。上記角度は、本発明の目的を達成する範囲に
おいて若干変化させてもよお、条件によつては上
記角度±3度の範囲を許容し得る。なお、上記角
度の他に、流路断面積、流路長さ、等がダスト付
着に関与するが、上記角度設定に適合したダクト
寸法が選択される。 以下、上記角度が選択された根拠について種々
の実験例をもとに説明する。図示した脱硫装置に
おいて、ダクト2の天井角度Aおよび底面角度B
をそれぞれ5度ないし15度と変化させてダクト内
のガスの偏流率および圧力損失△Pを測定した結
果を第1表に示す。
The present invention relates to a wet flue gas desulfurization system, and more particularly to a wet flue gas desulfurization system having a cooling tower and an absorption tower, in which uneven flow of gas in the equipment after the cooling tower is improved. The general configuration of a flue gas desulfurization apparatus equipped with a cooling tower and an absorption tower will be explained based on FIG. 1. In the figure, the gas to be treated is introduced into the cooling tower 10 from line 1, where it is brought into contact with the cooling liquid supplied from line 14, and after absorbing some SO 2 and removing dust, the gas is introduced into duct 2 and It is sent to the absorption tower 20 through the mist eliminator 4 in the duct. Absorption tower 2
At 0, the gas to be treated comes into contact with an absorbing liquid (e.g. lime slurry) supplied from line 24, and the gas in the gas is
After the SO 2 is removed, it is discharged through line 3. The absorption liquid is sent from the absorption tower circulation tank 40 to the absorption tower 20 via the lines 21 and 24 by the circulation pump 60, and a part is discharged outside the system from the line 23 or is sent to the cooling tower circulation tank 30. Sent. Absorbing liquid flows from the absorption tower 20 to the line 25
It is returned to the absorption tower circulation tank 40 again through the absorption tower circulation tank 40.
In the cooling tower 10, cooling water is passed from the cooling tower circulation tank 30 to the line 11, the cooling tower circulation pump 50,
It is returned to the cooling tower 10 through lines 12 and 14, and a portion is discharged from the system through line 13. On the other hand, the absorbent is replenished from the line 26 to the absorption tower circulation tank 40, and in this absorption tower circulation tank 40, the pH of the absorption liquid is restored by dissolving the absorbent, and the absorbent is absorbed again as described above. Sent to Tower 20. When the dust in the gas to be treated is separated and removed in the cooling tower 10, the cooling liquid containing the removed dust is passed through the cooling tower circulation tank 30 to the cooling tower 10.
At this time, the droplets of the circulating fluid sprayed in the cooling tower 10 or the fine mist generated by mixing and contacting the sprayed circulating fluid with the gas are entrained in the gas flow. scatter. In order to remove the mist containing these dusts, an absorption tower 20
A mist eliminator 4 is installed in the communication section leading to. In order to fully demonstrate the mist removal performance of the mist eliminator 4, it is necessary to rectify the gas to be treated at a gas flow rate suitable for the type of the mist eliminator 4 and flow it into the mist eliminator 4. This is because the mist collecting principle of the mist eliminator 4 utilizes inertial collision, and the collected mist is prevented from being scattered again if the gas flow velocity exceeds a predetermined amount. Conventionally, a rectifier plate (such as a buttful plate) has been inserted into the gas flow path in order to simply rectify the gas flow velocity at the inlet of the mist eliminator 4. In the case of gas containing a large amount of solid matter such as fly ash, the concentration of solid matter in the circulating fluid of the cooling tower increases, and a large amount of solid matter such as fly ash and calcium sulfate adheres to the rectifying plate and inside the duct 2. There is a problem in that draft loss suddenly increases, making continuous operation of the device difficult. This kind of solid matter adhesion inside the duct 2 becomes a problem even when a current plate is not installed, and especially a lot of solid matter adheres to the ceiling and bottom of the duct 2, so in the case of long-term continuous operation, the draft loss may be excessive. It has the disadvantage of becoming The purpose of the present invention is to eliminate the drawbacks of the above-mentioned prior art, to minimize the uneven flow of gas in the duct when the treated gas cooled in the cooling tower enters the mist eliminator, and to improve the separation efficiency of the mist eliminator. It is an object of the present invention to provide a wet type flue gas desulfurization device that can prevent solid matter from adhering to the inside of a duct. In order to achieve the above object, the present invention provides a duct leading from a cooling tower to a mist eliminator in a shape that reduces adhesion and accumulation of solid matter such as fly ash and draft loss. That is, the present invention allows the gas to be treated to pass through a cooling tower equipped with a cooling liquid spraying means, and introduces the cooled gas from the side of the cooling tower into an absorption tower through a duct having a mist eliminator. In a wet flue gas desulfurization device that absorbs sulfur oxides in the gas by reacting with the absorption liquid in the absorption tower, the inclination angle from the horizontal of the inner wall of the duct from the cooling tower to the mist eliminator is approximately at the ceiling surface. 5 degrees, and approximately 15 degrees at the bottom. Hereinafter, the present invention will be explained in more detail with reference to the drawings. FIG. 2 is a schematic cross-sectional view showing the shape of the duct from the cooling tower to the mist eliminator in the present invention. In order to prevent the adhesion or accumulation of dust in the gas, it is most preferable that the angle A between the ceiling surface of the inner wall of the duct 2 and the horizontal plane be 5 degrees, and the angle B between the bottom surface of the duct inner wall and the horizontal plane be 15 degrees. . The above-mentioned angle may be slightly changed as long as the object of the present invention is achieved, and depending on the conditions, a range of ±3 degrees from the above-mentioned angle may be allowed. In addition to the above-mentioned angle, the cross-sectional area of the flow passage, the length of the flow passage, etc. are involved in dust adhesion, and the duct dimensions that match the above-mentioned angle setting are selected. The basis for selecting the above angle will be explained below based on various experimental examples. In the illustrated desulfurization equipment, the ceiling angle A and the bottom angle B of the duct 2
Table 1 shows the results of measuring the unbalanced flow rate and pressure loss ΔP of the gas in the duct while changing the angle from 5 degrees to 15 degrees, respectively.

【表】 上記結果から、多少のバラツキがあるが、天井
角度Aが5度、底面角度Bが15度の組合わせが最
も好適であることが明らかである。なお、天井角
度Aが30〜45度、底面角度Bが0度または60度の
組合せでは、ガス偏流率が20%以上となつた。さ
らに比較のために、従来の角度A、Bがそれぞれ
0度、およびAを45度、Bを60度とした場合のダ
クト2の偏流率および圧力損失を第2表に示す。
[Table] From the above results, although there is some variation, it is clear that the combination of ceiling angle A of 5 degrees and bottom angle B of 15 degrees is the most suitable. In addition, in combinations where the ceiling angle A was 30 to 45 degrees and the bottom angle B was 0 degrees or 60 degrees, the gas drift ratio was 20% or more. Furthermore, for comparison, Table 2 shows the uneven flow rate and pressure loss of the duct 2 when the conventional angles A and B are respectively 0 degrees, A is 45 degrees, and B is 60 degrees.

【表】 次に、本発明のダクト形状を用いた場合(冷却
塔の循環液量7.5m3/hr)のガス量に対するダクト
の圧力損失の関係の一例を第3図に示す。図にお
いて、Cは、天井部角度Aを5度、底面部の角度
Bを15度とした本発明の実施例の場合、Dは、角
度Aを45度、角度Bを60度とした場合の比較例の
場合をそれぞれ示す。図の結果から、本発明のダ
クト形状を用いた場合には、ダクトのドラフト損
失が比較例の場合よりも著しく小さくなることが
明らかである。 上記実施例によれば、冷却塔からミストエリミ
ネータに到るダクトの天井角度を約5度、底面角
度を約15度とすることにより、定格負荷時におい
てガス偏流率を約5%、ドラフト損失を約10%に
抑えることができる。なお、除じん性能はダクト
の形状によつてほとんど影響されないことが確認
された。 以上の実施例は、冷却塔の下部と吸収塔をダク
トで連通させた場合についてのものであるが、吸
収塔にダクトを設け、さらにミストエリミネータ
を配置して処理ガスを取出す場合には、このダク
トを前記実施例の場合と同様の形状にすることに
より、同様な効果を得ることができる。 以上、本発明によれば、エリミネータに到るダ
クト内のガス偏流率を小さくし、かつ圧力損失を
抑えつつ、かつダクト内のダストの付着、堆積を
低減することができる。
[Table] Next, FIG. 3 shows an example of the relationship between the pressure loss of the duct and the gas amount when the duct shape of the present invention is used (the amount of circulating fluid in the cooling tower is 7.5 m 3 /hr). In the figure, C represents the embodiment of the present invention in which the ceiling angle A is 5 degrees and the bottom angle B is 15 degrees, and D represents the case in which the angle A is 45 degrees and the angle B is 60 degrees. Comparative examples are shown below. From the results shown in the figure, it is clear that when the duct shape of the present invention is used, the draft loss of the duct is significantly smaller than that of the comparative example. According to the above embodiment, by setting the ceiling angle of the duct from the cooling tower to the mist eliminator to about 5 degrees and the bottom angle to about 15 degrees, the gas unbalance rate can be reduced by about 5% and the draft loss can be reduced at rated load. It can be suppressed to about 10%. It was confirmed that the dust removal performance was hardly affected by the shape of the duct. The above example deals with the case where the lower part of the cooling tower and the absorption tower are connected through a duct. A similar effect can be obtained by making the duct the same shape as in the previous embodiment. As described above, according to the present invention, it is possible to reduce the gas unbalanced flow rate in the duct leading to the eliminator, suppress the pressure loss, and reduce the adhesion and accumulation of dust in the duct.

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

第1図は、排煙脱硫装置の一般的な装置系統
図、第2図は、本発明に用いる冷却塔からミスト
エリミネータに到るダクト形状を示す断面図、第
3図は、本発明の実施例の結果を示す図である。 1,3……ライン、2……ダクト、4……ミス
トエリミネータ、30……冷却塔循環タンク。
Fig. 1 is a general equipment system diagram of a flue gas desulfurization equipment, Fig. 2 is a sectional view showing the shape of the duct from the cooling tower to the mist eliminator used in the present invention, and Fig. 3 is a diagram showing the implementation of the present invention. FIG. 4 is a diagram showing example results. 1, 3... Line, 2... Duct, 4... Mist eliminator, 30... Cooling tower circulation tank.

Claims (1)

【特許請求の範囲】[Claims] 1 被処理ガスを冷却液のスプレ手段を備えた冷
却塔を通過させ、冷却された前記ガスを該冷却塔
の側部からミストエリミネータを有するダクトを
介して吸収塔に導入し、該吸収塔内の吸収液と反
応させて前記ガス中の硫黄酸化物を吸収除去する
湿式排煙脱硫装置において、前記冷却塔からミス
トエリミネータに至るダクト内壁の水平からの傾
斜角度を天井面部で約5度、底面部で約15度とす
ることを特徴とする湿式排煙脱硫装置。
1. The gas to be treated is passed through a cooling tower equipped with a cooling liquid spraying means, and the cooled gas is introduced into the absorption tower from the side of the cooling tower through a duct having a mist eliminator, and the gas is introduced into the absorption tower. In a wet flue gas desulfurization equipment that absorbs and removes sulfur oxides in the gas by reacting with an absorption liquid of Wet type flue gas desulfurization equipment that is characterized by a temperature of approximately 15 degrees.
JP11837578A 1978-09-25 1978-09-25 Wet type stack gas desulfurization apparatus Granted JPS5544366A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11837578A JPS5544366A (en) 1978-09-25 1978-09-25 Wet type stack gas desulfurization apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11837578A JPS5544366A (en) 1978-09-25 1978-09-25 Wet type stack gas desulfurization apparatus

Publications (2)

Publication Number Publication Date
JPS5544366A JPS5544366A (en) 1980-03-28
JPS6143087B2 true JPS6143087B2 (en) 1986-09-25

Family

ID=14735138

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11837578A Granted JPS5544366A (en) 1978-09-25 1978-09-25 Wet type stack gas desulfurization apparatus

Country Status (1)

Country Link
JP (1) JPS5544366A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0520422Y2 (en) * 1986-02-28 1993-05-27
JPH0829218B2 (en) * 1987-02-23 1996-03-27 バブコツク日立株式会社 Cooling tower sump structure

Also Published As

Publication number Publication date
JPS5544366A (en) 1980-03-28

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