JP3332760B2 - Absorbent regeneration and recovery system in flue gas desulfurization system - Google Patents

Absorbent regeneration and recovery system in flue gas desulfurization system

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Publication number
JP3332760B2
JP3332760B2 JP29366696A JP29366696A JP3332760B2 JP 3332760 B2 JP3332760 B2 JP 3332760B2 JP 29366696 A JP29366696 A JP 29366696A JP 29366696 A JP29366696 A JP 29366696A JP 3332760 B2 JP3332760 B2 JP 3332760B2
Authority
JP
Japan
Prior art keywords
gypsum
flow
water
draft tube
magnesium hydroxide
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 - Fee Related
Application number
JP29366696A
Other languages
Japanese (ja)
Other versions
JPH10128052A (en
Inventor
由尚 小松
秀夫 縄田
新一 滝本
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
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Filing date
Publication date
Application filed by Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP29366696A priority Critical patent/JP3332760B2/en
Publication of JPH10128052A publication Critical patent/JPH10128052A/en
Application granted granted Critical
Publication of JP3332760B2 publication Critical patent/JP3332760B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
  • Treating Waste Gases (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、水酸化マグネシウ
ム法(以下、水マグ法という。)による脱硫排水から吸
収剤Mg(OH)2 (以下、水マグという。)を再生
し、副産物としてCaSO4 ・2H2 O(以下、二水石
膏という。)を生成する反応晶析装置に、上記水マグ
二水石膏とを分級する沈降分級装置を設けた水マグ再生
回収システムに関する。
The present invention relates to a method for regenerating an absorbent Mg (OH) 2 (hereinafter, referred to as a water mug) from desulfurization wastewater by a magnesium hydroxide method (hereinafter, referred to as a water mug method), and producing CaSO as a by-product. 4 · 2H 2 O (hereinafter, referred to as gypsum.) to the reaction crystallizer for generating, on water mug regeneration recovery system having a sedimentation classification apparatus for classifying and the water mug and <br/> gypsum dihydrate .

【0002】[0002]

【従来の技術】水マグ法により排煙脱硫を行った脱硫排
水からSOX の吸収剤である水マグを再生する装置およ
び再生水マグ回収システムは、従来存在しない。しか
し、本発明も反応晶析装置を用いるので、従来の反応晶
析装置を図7、図8に示す。図7は該反応晶析装置の縦
断概略図、図8は図7の平面図である。これらの図にお
いて、供給口101より原液を流入させ、プロペラ10
2によりドラフトチューブ103内に上昇流104を発
生させ、それにより装置内の液に循環流を起こすことで
原液を装置内全体に均一に攪拌し、反応晶析を行う。
BACKGROUND OF THE INVENTION Apparatus and recycled water mug recovery system to reform water mug is absorbent SO X from desulfurization effluent of performing flue gas desulfurization by the water mug method, no conventional. However, since the present invention also uses a reaction crystallization apparatus, a conventional reaction crystallization apparatus is shown in FIGS. FIG. 7 is a schematic longitudinal section of the reaction crystallization apparatus, and FIG. 8 is a plan view of FIG. In these figures, an undiluted solution flows in from a supply port 101 and a propeller 10
By 2, an ascending flow 104 is generated in the draft tube 103, thereby causing a circulating flow in the liquid in the apparatus, thereby uniformly stirring the stock solution throughout the apparatus and performing reaction crystallization.

【0003】ドラフトチューブ103内の上昇流104
は、旋回成分を持っており、旋回流が存在する状態では
ドラフトチューブ103への液の吸込み105に要する
所要動力が増加してしまうので、その旋回成分を打ち消
すために整流板106を設けてある。また、排出孔10
7は保守・点検の際に装置内の液を排出するために用い
る。
The upward flow 104 in the draft tube 103
Has a swirling component, and in a state where a swirling flow is present, the power required for sucking the liquid 105 into the draft tube 103 increases. Therefore, a rectifying plate 106 is provided to cancel the swirling component. . Also, the discharge hole 10
Numeral 7 is used to drain the liquid in the apparatus during maintenance and inspection.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、上記従
来の反応晶析装置では、図7および図8に示すように装
置の塔径に対してプロペラ102およびドラフトチュー
ブ103がかなり大きく、装置内全体に二水石膏を分散
させるために必要な所要動力および所要トルクが非常に
大きく、高コストであった。また、ドラフトチューブ1
03と底面部108がかなり離れているので、底面部1
08に堆積した二水石膏を持ち上げることができなかっ
た。さらに、とい109の合流部110において流水1
11がぶつかり乱れが発生するという不具合があった。
However, in the above-mentioned conventional reaction crystallization apparatus, as shown in FIGS. 7 and 8, the propeller 102 and the draft tube 103 are considerably large with respect to the tower diameter of the apparatus. The required power and torque required to disperse gypsum were very large and costly. Draft tube 1
03 and the bottom portion 108 are considerably separated, so that the bottom portion 1
The dihydrate gypsum deposited at 08 could not be lifted. Further, the flowing water 1
There was a problem that the bumper 11 collided and caused disturbance.

【0005】本発明は、上記事情に鑑みてなされたもの
で、所要動力および所要トルクが小さく、コストが安価
吸収剤の再生回収システムを提供することにある。
The present invention has been made in view of the above circumstances, and it is an object of the present invention to provide an absorbent regeneration / recovery system which requires a small amount of power and torque and is inexpensive.

【0006】[0006]

【課題を解決するための手段】本発明は、上記目的を解
決するためになされたものであり、その要旨は、水酸化
マグネシウム法による脱硫排水より吸収剤である水酸化
マグネシウム(Mg(OH 2 ))を再生し、副産物とし
て二水石膏(CaSO 4 ・2H 2 O)を生成する反応晶
析装置に、前記水酸化マグネシウムと二水石膏とを分離
回収する沈降分級装置を設けた水マグ脱硫法における吸
収剤の再生回収システムであって、上記沈降分級装置
が、該沈降分級装置内の上部に粒子を含む液の水平流を
発生させる液の流入口及び流出口と、上記水平流の下方
において水平流の上流側及び下流側にそれぞれ設けられ
た第1選別室及び第2選別室と、上記第1選別室の下方
に連設され同第1選別室に沈降した粒子を受入れる分級
脚と、該分級脚の上部より上方へ延び前記水平流に合流
する流路と、上記第2選別室内の液を前記流路内へ上方
へ向って吹出す手段とを備えてなり、水酸化マグネシウ
ムと二水石膏との混合スラリーを反応晶析装置から沈降
分級装置内に上記流入口を介して流入させ、粒径の大き
な二水石膏を第1選別室に沈降させ、粒径の小さな水酸
化マグネシウムを第2選別室に沈降させるように構成し
たことにある。 また、本発明に係る再生回収システムの
一態様では、上記反応晶析装置において、ドラフトチュ
ーブを反応晶析装置の底面近傍まで延長し、ドラフトチ
ューブ下部に整流板を取り付けて反応晶析装置内に旋回
流を発生させるようにしている。 さらに、本発明に係る
再生回収システムの別の態様では、上記ドラフトチュー
ブの内側底部にコーンを配置し、かつ、といの合流部に
案内板を設けている。
SUMMARY OF THE INVENTION The present invention has been made to solve the above object, the gist, hydroxide
Hydroxidation as absorbent from desulfurization wastewater by magnesium method
Regenerates magnesium (Mg (OH 2 )) as a by-product
Reactive crystallization to produce gypsum (CaSO 4 · 2H 2 O) Te
Separation of the magnesium hydroxide and gypsum in a precipitation apparatus
In the water mag desulfurization method equipped with a sedimentation classifier for recovery,
A system for reclaiming and recovering a collecting agent, wherein the sedimentation classification device
Provides a horizontal flow of liquid containing particles at the top in the settling classifier.
The inlet and outlet of the liquid to be generated and below the horizontal flow
At the upstream and downstream of the horizontal flow
The first sorting room and the second sorting room, and below the first sorting room.
Classified to receive particles settled in the first sorting room
A leg, extending upward from the upper part of the classifying leg and joining the horizontal flow
And the liquid in the second sorting chamber is moved upward into the flow path.
Means for blowing toward
Of the mixed slurry of gypsum and gypsum from the reaction crystallizer
Flow into the classifier through the above inlet, and
Gypsum is settled in the first sorting room, and small particle size hydroxy
Configured to settle magnesium iodide into the second sorting chamber
That is. In addition, the recycling and recovery system according to the present invention
In one embodiment, the reaction crystallization apparatus includes a draft tube.
Extend the probe to near the bottom of the reaction crystallizer, and
Attach a current plate under the tube and swirl into the reaction crystallizer
The current is generated. Further according to the invention
In another aspect of the reclaim system, the draft tube
Place a cone on the inside bottom of the tube and at the junction
A guide plate is provided.

【0007】[0007]

【発明の実施の形態】以下に図面を参照しながら、本発
明に係る再生回収システム、及びこのシステムを構成す
反応晶析装置を詳細に説明する。図1は本発明に係る
再生回収システムを構成する反応晶析装置の縦断概略
図、図2は図1の平面図、図3は図1の側面図である。
BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a block diagram showing the structure of a recycling system according to the present invention .
The reaction crystallization apparatus will be described in detail. FIG. 1 relates to the present invention.
FIG. 2 is a schematic longitudinal cross-sectional view of a reaction crystallization apparatus constituting the regeneration and recovery system , FIG. 2 is a plan view of FIG. 1, and FIG. 3 is a side view of FIG.

【0008】図1において、プロペラ1を回転させるこ
とでドラフトチューブ2内に上昇流3を発生させ、この
流れにより二水石膏および水マグを上昇させる。図1に
示した反応晶析装置では、水マグの再生とともに副産物
の二水石膏を成長させるため、種晶石膏が反応晶析装置
全体に均等に分布するように攪拌を行う必要がある。そ
こで、ドラフトチューブ2上端部にベルマウス4を設け
ることで、二水石膏および水マグを装置全体に分散させ
る。
In FIG. 1, by rotating a propeller 1, an ascending flow 3 is generated in a draft tube 2, and this flow raises gypsum and water mug. In the reaction crystallization apparatus shown in FIG. 1, it is necessary to perform stirring so that the seed gypsum is evenly distributed throughout the reaction crystallization apparatus in order to grow by-product gypsum together with the regeneration of the water mug. Therefore, by providing a bell mouth 4 at the upper end of the draft tube 2, the dihydrate gypsum and the water mug are dispersed throughout the apparatus.

【0009】上昇流3にはプロペラ1の回転によって発
生する旋回成分があり、これを用いて図2に示す旋回流
5を発生させれば、プロペラ1によって発生した上昇流
3が弱くても反応晶析装置の底面部6への二水石膏の堆
積を防止することができる。また、ドラフトチューブ2
を底面部6付近まで延長して設ける。16は整流板であ
る。それによって液の吸込み流速が大きくなり、二水石
膏および水マグをドラフトチューブ2内へ吸い込むこと
のできる範囲が広くなる。したがって、装置外径に対し
てかなり小径のプロペラ1、ドラフトチューブ2を用い
ても、二水石膏および水マグを装置全体に分散させ、か
つ、底面部6への堆積を防止することができる。
The upward flow 3 has a swirl component generated by the rotation of the propeller 1. If this is used to generate the swirl flow 5 shown in FIG. 2, even if the upward flow 3 generated by the propeller 1 is weak, a reaction will occur. It is possible to prevent the accumulation of gypsum on the bottom portion 6 of the crystallizer. Draft tube 2
Is extended to the vicinity of the bottom part 6. Reference numeral 16 denotes a current plate. As a result, the suction flow rate of the liquid is increased, and the range in which gypsum and water mug can be sucked into the draft tube 2 is widened. Therefore, even if the propeller 1 and the draft tube 2 having diameters considerably smaller than the outer diameter of the apparatus are used, the dihydrate gypsum and the water mug can be dispersed throughout the apparatus, and deposition on the bottom surface 6 can be prevented.

【0010】また、二水石膏の実質の成長速度を大きく
するために二水石膏の磨耗速度をおさえ、かつ、攪拌所
要動力も低減させる必要がある。そこで、ドラフトチュ
ーブ2内の底部にコーン7を配置し、それにより、ドラ
フトチューブ2内に流入した液をスムーズに合流させ、
プロペラ1の所要動力および所要トルクを低減すること
ができる。また、供給口8より脱硫排水をドラフトチュ
ーブ2内へ、供給口9より水酸化カルシウム(Ca(O
H)2 )を液面上へ供給することにより、局所的な濃度
の違いを抑え、実質的な種晶石膏の成長速度を大きく
し、連続的に反応晶析を行う。このとき、Ca(OH)
2 の粉末が直接とい10へ流出することを防ぐためにバ
ッフル11を設ける。
Further, in order to increase the substantial growth rate of gypsum, it is necessary to reduce the wear rate of gypsum and to reduce the power required for stirring. Therefore, the cone 7 is arranged at the bottom in the draft tube 2, whereby the liquids flowing into the draft tube 2 are smoothly merged,
The required power and required torque of the propeller 1 can be reduced. Further, desulfurized wastewater is supplied from the supply port 8 into the draft tube 2, and calcium hydroxide (Ca (O
By supplying H) 2 ) onto the liquid surface, a local difference in concentration is suppressed, a substantial growth rate of seed gypsum is increased, and reaction crystallization is continuously performed. At this time, Ca (OH)
A baffle (11) is provided to prevent the powder of ( 2 ) from flowing out directly to the cutter (10).

【0011】また、オーバーフロー部12からオーバー
フローした液は、とい10を流れて後段の分級装置(図
示せず)に流入するが、流入時の乱れが少ない方が分級
性能が向上するので、流水13をスムーズに合流させて
乱れの発生を抑えるために、合流部14に案内板15を
設けてある。さらに、整流板16は、ドラフトチューブ
2の支持台を兼ねて、該ドラフトチューブ2の下部に設
置してある。また、コーン7の下部には排出口17を設
けている。
The liquid overflowing from the overflow section 12 flows through the shank 10 and flows into a classification device (not shown) at the subsequent stage. The smaller the disturbance at the time of the flow, the better the classification performance. The guide plate 15 is provided at the confluence portion 14 in order to smoothly merge and suppress the occurrence of turbulence. In addition, the current plate 16 is provided below the draft tube 2 and also serves as a support for the draft tube 2. Further, a discharge port 17 is provided at a lower portion of the cone 7.

【0012】次いで、上記反応晶析装置による作用につ
いて詳述する。図1において、プロペラ1を用いること
でドラフトチューブ2内に上昇流3を発生させる。ドラ
フトチューブ2上端部にベルマウス4を取り付けること
で、上昇流3により持ち上げた二水石膏および水マグを
装置全体に分散させる。また、上昇流3には旋回成分が
あるので、これを用いることで旋回流5を発生させる。
この流れにより、底面部6に堆積した二水石膏を滑落さ
せることができ、ドラフトチューブ2内へ吸い込まれる
流れにのせることができる。ドラフトチューブ2は底面
部6付近まで延長してあるので、ドラフトチューブ2内
へ吸い込む液の流速が上がり、底面部6における二水石
膏および水マグの吸込み可能範囲が広がる。また、この
ドラフトチューブ2の下部に設置した整流板16によ
り、装置内に旋回流を発生させる。
[0012] Next, will be described in detail operation of the above reaction crystallizer. In FIG. 1, an upward flow 3 is generated in a draft tube 2 by using a propeller 1. By attaching the bell mouth 4 to the upper end of the draft tube 2, the dihydrate gypsum and the water mug lifted by the upflow 3 are dispersed throughout the apparatus. Since the upward flow 3 has a swirl component, the swirl flow 5 is generated by using the swirl component.
By this flow, gypsum plaster deposited on the bottom part 6 can be slid down, and can be put on the flow sucked into the draft tube 2. Since the draft tube 2 is extended to the vicinity of the bottom surface 6, the flow rate of the liquid sucked into the draft tube 2 is increased, and the area where the dihydrate gypsum and the water mug can be sucked in the bottom surface 6 is widened. In addition, a swirling flow is generated in the apparatus by the rectifying plate 16 installed below the draft tube 2.

【0013】さらに、ドラフトチューブ2内の底部に設
けられたコーン7は周囲から吸い込んだ流れをスムーズ
に合流させることができ、プロペラ1の所要動力および
所要トルクの低減が図れる。また、とい10の合流部1
4に設けた案内板15によって流水13の合流がスムー
ズになり、乱れを極力抑えることができる。
Further, the cone 7 provided at the bottom in the draft tube 2 can smoothly merge the flows sucked from the surroundings, and the required power and torque of the propeller 1 can be reduced. In addition, confluence part 1
By the guide plate 15 provided in 4, the merging of the running water 13 becomes smooth, and turbulence can be suppressed as much as possible.

【0014】実施の他の形態 次に、図4〜図6を用いて、本発明に係る吸収剤の再生
回収システムを説明する。図4は沈降分級装置を備えた
反応晶析装置の縦断概略図、図5は図4の平面図、図6
は図4の側面図である。図中、図1〜図3と同一部分は
同一符号をもって示す。これらの図において、沈降分級
装置18では、水マグと二水石膏の分級を行うが、流入
口19から水マグと二水石膏の混合スラリーを流入さ
せ、水平流20に乗せる。水平流20が流出口21から
流出するまでの間に粒径の大きな二水石膏は第1選別室
22に、粒径の小さな水マグの一部は第2選別室23に
沈降し、残りの水マグは液と共に流出口21より流出す
る。
Another Embodiment of the Invention Next, a system for regenerating and recovering an absorbent according to the present invention will be described with reference to FIGS. FIG. 4 is a schematic longitudinal sectional view of a reaction crystallization apparatus provided with a sedimentation classifier, FIG. 5 is a plan view of FIG.
FIG. 5 is a side view of FIG. 4. In the drawings, the same parts as those in FIGS. 1 to 3 are denoted by the same reference numerals. In these figures, a sedimentation classifier 18 classifies water mug and gypsum, and a mixed slurry of water mug and gypsum is introduced from an inlet 19 and placed on a horizontal flow 20. Until the horizontal flow 20 flows out of the outlet 21, gypsum gypsum having a large particle diameter is settled in the first sorting chamber 22, and a part of the water mug having a small particle diameter is settled in the second sorting chamber 23, and the remaining water mug is separated. The water mug flows out of the outlet 21 together with the liquid.

【0015】第1選別室22に沈降した二水石膏は分級
脚24に堆積する。堆積した二水石膏の圧密を防ぐため
に分級脚24内の液をスクリュー(図示せず)で流動化
させることで二水石膏を流動化させ、粒子抜出口25よ
り抜き出す。このとき、流動化させることで二水石膏同
士が接触し、表面に付着している水マグが遊離し、分級
脚上部26に浮遊する。第2選別室23に沈降した水マ
グはポンプ27を用いて液と共に導水管28より流路2
9に吹き出し、上昇流30を発生させる。この上昇流3
0により、分級脚上部26に浮遊している水マグおよび
第2選別室23内の水マグを合流点31まで持ち上げ、
再度水平流20に乗せ、流出口21から抜き出す。ここ
で、回収した水マグはSOX の吸収剤として再利用する
ので、特に水マグは高純度、高回収率でなければならな
い。なお、32は流路30と第1選別室22を仕切って
いる仕切板である。
The dihydrate gypsum that has settled in the first sorting chamber 22 accumulates on the classification leg 24. The liquid in the classification leg 24 is fluidized with a screw (not shown) in order to prevent the condensed dihydrate gypsum from being compacted, so that the dihydrate gypsum is fluidized and extracted from the particle outlet 25. At this time, due to the fluidization, the dihydrate gypsum comes into contact with each other, the water mug adhering to the surface is released, and floats on the classifying leg upper portion 26. The water mug that has settled in the second sorting chamber 23 is passed through a water pipe 28 together with the liquid using a pump 27 to flow through a second passage 2.
9 and an upward flow 30 is generated. This ascending flow 3
By 0, the water mug floating on the classifying leg upper part 26 and the water mug in the second sorting chamber 23 are lifted to the junction 31,
It is placed on the horizontal flow 20 again and extracted from the outlet 21. Here, since the recovered water mug is reused as an absorbent for SO X , particularly, the water mug must have high purity and a high recovery rate. Reference numeral 32 denotes a partition plate that partitions the flow path 30 and the first sorting chamber 22.

【0016】次いで、本発明に係る吸収剤の再生回収シ
ステムによる作用について詳述する。沈降分級装置18
では、水マグは流入口19から流入する水平流20によ
り流出口21から流出する。一方、二水石膏は第1選別
室22を経て分級脚24に堆積し、粒子抜出口25より
抜き出す。分級脚24内の液を流動させることで、二水
石膏同士を接触させ、石膏表面に付着している水マグを
遊離させて、分級脚上部26に浮遊させる。ここで、第
2選別室23内の液をポンプ27を用いて導水管28か
ら流路29に吹き出すことで上昇流30を発生させ、分
級脚上部26に浮遊している水マグを合流部31まで持
ち上げ、再度水マグを水平流20にのせることで、水マ
グの回収率および二水石膏の純度を向上させる。また、
二水石膏の表面に付着した水マグを遊離させて、その水
マグを回収するために分級脚24内の液をスクリューま
たは振動膜(図示せず)で流動させる。
Next, the operation of the absorbent recovery and recovery system according to the present invention will be described in detail. Sedimentation classifier 18
Then, the water mug flows out of the outlet 21 by the horizontal flow 20 flowing from the inlet 19. On the other hand, gypsum is deposited on the classification leg 24 through the first sorting chamber 22 and is extracted from the particle outlet 25. By making the liquid in the classification leg 24 flow, the gypsums are brought into contact with each other to release the water mug adhering to the gypsum surface and float on the classification leg upper portion 26. Here, the liquid in the second sorting chamber 23 is blown out from the water guide pipe 28 to the flow path 29 by using the pump 27 to generate the upward flow 30, and the water mug floating on the classification leg upper part 26 is combined with the merging part 31. Then, the water mug is placed on the horizontal flow 20 again, thereby improving the recovery rate of the water mug and the purity of the gypsum. Also,
The water mug adhering to the surface of the gypsum is released, and the liquid in the classification leg 24 is caused to flow by a screw or a vibrating membrane (not shown) in order to collect the water mug.

【0017】[0017]

【発明の効果】上述したように、本発明に係る再生回収
システムによれば、 (1) 粒子を装置全体に分散させ、かつ、底面部への
堆積を防止するための所要動力および所要トルクの低減
が図れ、コストが安価ですむ。 (2) 水マグ法による脱硫排水からの吸収剤である水
マグの再生が低動力、低トルクで行えるため、コストが
安価ですむ。また、水マグの回収率を高くすることがで
きる。
As described above, the regeneration and recovery according to the present invention
According to the system , (1) the power required and the torque required for dispersing the particles throughout the apparatus and preventing accumulation on the bottom surface can be reduced, and the cost can be reduced. (2) Water mug, which is an absorbent from desulfurization effluent by the water mug method, can be regenerated with low power and low torque, resulting in low cost. Further, the recovery rate of the water mug can be increased.

【図面の簡単な説明】[Brief description of the drawings]

【図1】 本発明に係る再生回収システムを構成する
応晶析装置の縦断概略図である。
FIG. 1 is a schematic longitudinal sectional view of a reaction crystallization apparatus constituting a regeneration and recovery system according to the present invention.

【図2】 図1の平面図である。FIG. 2 is a plan view of FIG.

【図3】 本発明に係る再生回収システムを構成する
応晶析装置の側面図で、一部を切開して示す図である。
FIG. 3 is a side view, partially cut away, of the reaction crystallization apparatus constituting the regeneration and recovery system according to the present invention.

【図4】 他の実施の形態に係る再生回収システムの縦
断概略図である。
FIG. 4 is a schematic vertical sectional view of a regeneration and recovery system according to another embodiment.

【図5】 図4の平面図である。FIG. 5 is a plan view of FIG. 4;

【図6】 図4の側面図である。FIG. 6 is a side view of FIG. 4;

【図7】 従来の反応晶析装置を示す縦断概略図であ
る。
FIG. 7 is a schematic longitudinal sectional view showing a conventional reaction crystallization apparatus.

【図8】 図7の平面図である。FIG. 8 is a plan view of FIG. 7;

フロントページの続き (51)Int.Cl.7 識別記号 FI B01D 9/02 619 C01F 5/14 53/77 11/46 Z C01F 5/14 B01D 53/34 125R 11/46 125D (56)参考文献 特開 昭49−25557(JP,A) 特開 昭53−32469(JP,A) 特開 平10−66895(JP,A) 特公 昭48−1301(JP,B1) 特公 平5−54361(JP,B2) 特公 昭55−23771(JP,B2) 特公 昭56−17123(JP,B2) 実公 昭41−22547(JP,Y1) 実公 平3−34243(JP,Y2) (58)調査した分野(Int.Cl.7,DB名) B01D 9/02 B01D 53/34 Continued on the front page (51) Int.Cl. 7 Identification symbol FI B01D 9/02 619 C01F 5/14 53/77 11/46 Z C01F 5/14 B01D 53/34 125R 11/46 125D (56) References Features JP-A-49-25557 (JP, A) JP-A-53-32469 (JP, A) JP-A-10-66895 (JP, A) JP-B-48-1301 (JP, B1) JP-B-5-54361 ( JP, B2) Japanese Patent Publication No. 55-23771 (JP, B2) Japanese Patent Publication No. 56-17123 (JP, B2) Japanese Utility Model Publication No. 41-22547 (JP, Y1) Japanese Utility Model Publication No. 3-34243 (JP, Y2) (58) ) Surveyed field (Int.Cl. 7 , DB name) B01D 9/02 B01D 53/34

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 水酸化マグネシウム法による脱硫排水よ
り吸収剤である水酸化マグネシウム(Mg(OH2 ))
を再生し、副産物として二水石膏(CaSO4 ・2H2
O)を生成する反応晶析装置に、前記水酸化マグネシウ
ムと二水石膏とを分離回収する沈降分級装置を設けた
マグ脱硫法における吸収剤の再生回収システムであっ
て、 上記沈降分級装置が、該沈降分級装置内の上部に粒子を
含む液の水平流を発生させる液の流入口及び流出口と、
上記水平流の下方において水平流の上流側及び下流側に
それぞれ設けられた第1選別室及び第2選別室と、上記
第1選別室の下方に連設され同第1選別室に沈降した粒
子を受入れる分級脚と、該分級脚の上部より上方へ延び
前記水平流に合流する流路と、上記第2選別室内の液を
前記流路内へ上方へ向って吹出す手段とを備えてなり、 水酸化マグネシウムと二水石膏との混合スラリーを反応
晶析装置から沈降分級装置内に上記流入口を介して流入
させ、粒径の大きな二水石膏を第1選別室に沈降させ、
粒径の小さな水酸化マグネシウムを第2選別室に沈降さ
せるように構成したことを特徴とする水マグ脱硫法にお
ける吸収剤の再生回収システム。
1. Magnesium hydroxide (Mg (OH 2 )) as an absorbent from desulfurized wastewater by the magnesium hydroxide method
Play the dihydrate gypsum as a by-product (CaSO 4 · 2H 2
Water provided with a sedimentation classifier for separating and recovering the magnesium hydroxide and gypsum from the reaction crystallization apparatus for producing O)
It is a regeneration and recovery system for absorbents in the mag desulfurization process.
Thus, the sedimentation classifier causes the particles in the upper part of the sedimentation classifier
An inlet and an outlet for a liquid that generates a horizontal flow of the liquid containing,
Below and above the horizontal flow, upstream and downstream of the horizontal flow
A first sorting room and a second sorting room provided respectively,
Grains set down below the first sorting room and settled in the first sorting room
A classifying leg for receiving a child, and extending upward from an upper portion of the classifying leg
A flow path merging with the horizontal flow, and a liquid in the second sorting chamber.
Means for blowing upward into the flow path, wherein a mixed slurry of magnesium hydroxide and gypsum is allowed to flow from the reaction crystallization device into the sedimentation classification device via the inlet, and The large-diameter gypsum is settled in the first sorting room,
A system for regenerating and recovering an absorbent in a water-magnesium desulfurization method, wherein magnesium hydroxide having a small particle size is settled in a second sorting chamber.
【請求項2】 上記反応晶析装置において、ドラフトチ
ューブを反応晶析装置の底面近傍まで延長し、ドラフト
チューブ下部に整流板を取り付けて反応晶析装置内に旋
回流を発生させるようにしたことを特徴とする請求項1
に記載の水マグ脱硫法における吸収剤の再生回収システ
ム。
2. The reaction crystallizer according to claim 1, wherein the draft tube is extended to a position near the bottom of the reaction crystallizer, and a rectifying plate is attached to a lower portion of the draft tube to generate a swirling flow in the reaction crystallizer. Claim 1 characterized by the following:
Recovery and recovery system for water mag desulfurization method described in
M
【請求項3】 上記ドラフトチューブの内側底部にコー
ンを配置し、かつ、といの合流部に案内板を設けたこと
を特徴とする請求項1又は2に記載の水マグ脱硫法にお
ける吸収剤の再生回収システム。
3. Place the cone on the inside bottom of the draft tube, and you water mug desulfurization method according to claim 1 or 2, characterized in that a guide plate to confluent portion of the gutter
Absorbent recovery system.
JP29366696A 1996-11-06 1996-11-06 Absorbent regeneration and recovery system in flue gas desulfurization system Expired - Fee Related JP3332760B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP29366696A JP3332760B2 (en) 1996-11-06 1996-11-06 Absorbent regeneration and recovery system in flue gas desulfurization system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29366696A JP3332760B2 (en) 1996-11-06 1996-11-06 Absorbent regeneration and recovery system in flue gas desulfurization system

Publications (2)

Publication Number Publication Date
JPH10128052A JPH10128052A (en) 1998-05-19
JP3332760B2 true JP3332760B2 (en) 2002-10-07

Family

ID=17797685

Family Applications (1)

Application Number Title Priority Date Filing Date
JP29366696A Expired - Fee Related JP3332760B2 (en) 1996-11-06 1996-11-06 Absorbent regeneration and recovery system in flue gas desulfurization system

Country Status (1)

Country Link
JP (1) JP3332760B2 (en)

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Also Published As

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