JP2004195394A - Flue gas desulfurization apparatus - Google Patents

Flue gas desulfurization apparatus Download PDF

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Publication number
JP2004195394A
JP2004195394A JP2002368406A JP2002368406A JP2004195394A JP 2004195394 A JP2004195394 A JP 2004195394A JP 2002368406 A JP2002368406 A JP 2002368406A JP 2002368406 A JP2002368406 A JP 2002368406A JP 2004195394 A JP2004195394 A JP 2004195394A
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Prior art keywords
desulfurization
flue gas
particles
thin film
towers
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JP2002368406A
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Japanese (ja)
Inventor
Kinryu Sho
金龍 鍾
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China Steel Corp
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China Steel Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a flue gas desulfurization apparatus excellent in desulfurization efficiency, in which the operationable time for every desulfurization unit is longer than that of conventional fixed type desulfurization apparatuses. <P>SOLUTION: The desulfurization apparatus recovering particles for desulfurization to recycle it after removing sulfur oxides in the flue gas by bringing a particle group for desulfurization wetted by addition of water into contact with flue gas is provided with a desulfurization device removing sulfur oxides from flue gas by making flue gas pass through in the state of housing the wetted particle group and by reacting sulfur oxides in flue gas with the surfaces of the particle for desulfurization to stick and bond sulfur oxides to the surface so as to form thin films; a separator which is installed at the lower part of the desulfurization device and in which the thin films are broken by friction and collision of the particles each other to separate the thin films from the particles while the particles adhered with the thin films gradually moving downward by vibration; a water supplying device supplying water to the particle group; and a recovering device which is installed at the lower part of the separator and which recovers the particles which has removed of the thin films into the desulfurization device to recycle them. <P>COPYRIGHT: (C)2004,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、排煙脱硫設備に関し、特に加水によって濡らされた脱硫用粒子群にて排煙と接触し、排煙中における硫黄酸化物を除去した後、脱硫用粒子を回収して再利用する排煙脱硫設備に関する。
【0002】
【従来の技術】
従来のボイラーなどの燃焼排煙から硫黄酸化物を除去する排煙脱硫方法の一つとしては、濡らされた脱硫用粒子、例えば炭酸カルシウム(石灰石)粒子群にて排煙中における硫黄酸化物(SO,SOなど)と反応して前記炭酸カルシウム粒子の表面に硫酸カルシウムまたは亜硫酸カルシウム薄膜を形成することにより、前記排煙から前記硫黄酸化物を除去するという方法を採用している。この方法を応用する排煙脱硫設備は、主として固定式と流動式との二種が分けられている。
【0003】
図1に示す排煙脱硫設備1は、固定式の例である。この排煙脱硫設備1により排煙から脱硫をしようとする場合、まず、弁11を開けて粒子蓄積タンク12から未加水の脱硫用粒子、例えば炭酸カルシウム粒子121を脱硫室13内に供給してから、前記脱硫室13内の上方に設けられている給水器14で炭酸カルシウム粒子群121へ給水して前記炭酸カルシウム粒子群121を濡らし、その後、弁15A,15Bを開けて排煙を分岐路151から前記炭酸カルシウム粒子群121、篩16、分岐路152及び煙道17を順次に経由して脱硫した後、外部へ排気させるという脱硫工程をすることができる。そして、所定時間の稼動を経った後、前記弁15A,15Bを閉じて前記篩16の下面に設けられている振動器18を作動させて前記脱硫室13内の粒子群121を振動し、粒子同士間の摩擦や衝突によって前記炭酸カルシウム粒子121の表面に形成した硫酸カルシウム薄膜を砕いて前記炭酸カルシウム粒子121から分離させ、次いで弁15C,15Dを開け、集塵器19にて該薄膜の破砕物を収集して前記脱硫室13から除去する炭酸カルシウム粒子121の再生工程を行う。前記再生工程を終えた後、前記粒子蓄積タンク12から未加水の炭酸カルシウム粒子121を前記脱硫室13内に補足し、引き続いて、前記給水器14で炭酸カルシウム粒子群121へ給水することにより、再び脱硫工程を行うことができる。前記排煙脱硫設備1は、通常、前記脱硫室13を複数備えているため、前記脱硫用粒子の再生工程は前記複数の脱硫室13に逐一に行われることができるので、脱硫用粒子の再生中、脱硫工程を実施し続けることができる。
【0004】
前記排煙脱硫設備1は、脱硫工程を進行する時、前記脱硫用粒子121は動かず、即ち固定的であるので、設備が簡単である上、効果も良いが、一旦脱硫用粒子群121の堆積が厚過ぎると、排煙通過の抵抗が大きくなり、排煙が粒子群121を通過し難くなったり、再生時の振動効果もより上層の粒子に至らなくなって薄膜の分離効果が悪くなったりする種々の問題があるため、堆積する脱硫用粒子の量がかなり制限されるので、脱硫室13の使用時間が短くて前記再生工程も頻繁に行わなければならないという欠点がある。
【0005】
図2に示す排煙脱硫設備2は、流動式の例である。該排煙脱硫設備2は、複数の並列した脱硫塔20を備えている。脱硫工程の進行中において、前記複数の脱硫塔20内には、加水によって濡らされた脱硫用粒子としての炭酸カルシウム粒子群21が各脱硫塔20の上から下へと連続的に流動している。また、前記粒子群21の流動と同時に、排煙が入り口22から入って前記流動の粒子群21に割り込んで通過し、脱硫を行ってから、前記脱硫塔20同士間の隙間23から外部へ排気している。
【0006】
前記流動の粒子で脱硫を行う排煙脱硫設備2は、稼動可能な時間が長いが、粒子が流動する状態で脱硫を行っているので、流動時の前記粒子同士間の摩擦や衝突によって前記脱硫用粒子の表面に形成した薄膜を砕き、前記脱硫用粒子から分離させ、更に前記薄膜の破砕物が脱硫後の排煙と一緒に外部へ排出し、排煙の出口を塞いだり、外気にキャリオーバして、せっかく脱硫した排煙を汚染したりするという欠点がある。
【0007】
【発明が解決しようとする課題】
上記に鑑みて、本発明の目的は、従来の流動式におけるキャリオーバまたは排煙の出口を塞ぐことなどの問題がない上、脱硫ユニット毎の稼動可能な時間も従来の固定式よりかなり長い排煙脱硫設備を提供しようとすることにある。
【0008】
【課題を解決するための手段】
上記目的を達成するために、発明者は、まず、加水によって濡らされた脱硫用粒子群と排煙とを接触させることによって、排煙中における硫黄酸化物を除去した後、脱硫用粒子を回収して再利用する排煙脱硫設備であって、前記濡らされた脱硫用粒子群を収容した状態で前記排煙を通過させ、排煙中における硫黄酸化物を脱硫用粒子の表面と反応させて薄膜となるように付着結合させ、前記排煙から硫黄酸化物を除去する脱硫装置と、前記脱硫装置の下方に設けられていて、振動によって、前記薄膜が付着している脱硫用粒子を下へと徐々に移動させながら、脱硫用粒子同士間の摩擦や衝突によって前記薄膜を砕き、脱硫用粒子から分離させる分離装置と、前記脱硫用粒子群へ給水する給水装置と、前記分離装置の下方に設けられていて、前記薄膜を除去した脱硫用粒子を前記脱硫装置内に回収して再利用する回収装置とを備えてなることを特徴とする排煙脱硫設備を提供する。
【0009】
この構成による排煙脱硫設備は、粒子群を動かさない状態で脱硫工程を行うので、前記キャリオーバまたは排煙の出口を塞ぐことなどの問題がなく、且つ、再生工程において粒子が流動の状態で互いに摩擦したり衝突したりし、前記薄膜を砕いて脱硫用粒子から分離させるので、前記脱硫装置に大量の脱硫用粒子を収容しても薄膜の分離効果が良い。
【0010】
そして、前記脱硫装置は、ハウジングと、前記ハウジング内に左右方向に隙間を空けて並列し、前記ハウジングを前室と後室との二室に仕切っている複数の脱硫塔とからなり、前記ハウジングの前記前室の方に排煙の入り口が設けられ、前記後室の方に排煙の出口が設けられており、また、前記複数の脱硫塔は、いずれも、前記濡らされた脱硫用粒子群を直立壁(または直立する塀)のように積んで保持し、且つ、前記直立壁のような脱硫用粒子群の左右両側の壁面を前記ハウジング内の排煙に開放させる立てフレームからなることが好ましい。それにより、前記排煙は前記入り口から入った後、前記複数の脱硫塔同士間の隙間に入って、前記立てフレームに保持されている脱硫用粒子群の左右両側の壁面の一方から他方へ通過し、前記出口を経由して出ることができるため、前記立てフレーム内に大量の脱硫用粒子が堆積しても、前記立てフレームの保持により前記脱硫用粒子群の厚さがちっとも変らないので、排煙通過の抵抗が従来の固定式のように大きくなることがない。即ち、本発明の排煙脱硫設備は、大量の脱硫用粒子を前記脱硫ユニットとしての脱硫塔内に堆積することができるので、脱硫ユニット毎の稼動可能な時間は従来の固定式よりずっと長い。
【0011】
そして、前記複数の脱硫塔は、いずれも、前後一対の立て板の間に隙間を空けて左右対立している一対の前記立てフレームを立設してなり、且つ、前記後ろの立て板は他の全ての脱硫塔の後ろの立て板と互いに連接して一体になり、その上にまた各脱硫塔の前記一対の立てフレーム間の隙間によって形成されている通路と連通するゲート付き開口が複数設けられることが好ましい。それにより、前記複数の脱硫塔同士間の隙間に入ってから前記一対の立てフレームの一つに保持されている脱硫用粒子群を通過した排煙は、先に前記一対の立てフレーム間の通路に入って前記ゲート付き開口を通過し、初めて前記出口を経由して出ることができる。また、所定時間の稼動を経った後、前記複数の脱硫塔における一部の脱硫塔を再生しようとする場合、当該一部の脱硫塔それぞれの前記一対の立てフレーム間のゲート付き開口を閉じて当該一部の脱硫塔内への排煙をストップし、残りの脱硫塔だけへ排煙を流通させることができるので、一部の脱硫塔の再生中において他の残りの脱硫塔により排煙の脱硫工程を実施し続けることができる。
【0012】
なお、前記立てフレームは、その間の空間が下から上へ徐々に展開した2の対向する平板からなる平板組みを隙間を空けて上下複数配列してなることが好ましい。それにより、排煙は、上下平板組み同士間の隙間を経由して脱硫用粒子群の壁の一方の面から他方の面に浸透することができる。また、前記平板は、その上縁が上へ反り、下縁が下へ反るように構成されていることが好ましい。それにより、前記平板の構成強度が増加される上、脱硫用粒子群も立てフレームに安定に保持され得、脱硫用粒子が上下平板組み同士間の隙間を経由して複数の脱硫塔同士間または立てフレーム間の通路内に崩落するということを避けることもできる。
【0013】
そして、前記排煙脱硫設備は、濡らされた脱硫用粒子を前記複数の脱硫塔それぞれの立てフレーム内に供給する粒子供給装置を更に備え、前記分離装置は、前記複数の脱硫塔の真下にそれぞれ斜めに設けられていて、それらのメッシュが前記脱硫用粒子より小である複数の篩と、前記複数の篩をそれぞれ振動する複数の振動器とからなり、前記給水装置は、前記立てフレーム毎の上方に設けられていて、前記立てフレームに保持されている脱硫用粒子群へ給水する第1の給水器と、前記篩毎の上方に設けられていて、前記篩へ給水する第2の給水器とからなることが好ましい。それにより、各脱硫塔への粒子供給及び濡らし作業並びに再生工程を独立に行うことができるので、一部の脱硫塔の脱硫用粒子の再生中、他の脱硫塔に脱硫工程を実施し続けることができる。
【0014】
そして、前記回収装置は、前記篩の下端側に設けられていて、前記薄膜を除去した脱硫用粒子を回収して前記立てフレーム内へ輸送する粒子回収手段と、前記篩の真下に設けられていて、前記篩から落ちた薄膜の破砕物と給水(または給水した水)とを収集する収集手段とを備えてなることが好ましい。それにより、前記脱硫用粒子を回収して再利用することができる。
【0015】
なお、前記収集手段は、収集タンクからなり、且つ、この収集タンクの近くには、また、前記収集タンクの上層の水層を案内して、薄膜の破砕物と前記給水とからなる混濁液を濾過して前記破砕物を給水から除去する濾過装置と、前記収集タンクの底面に沈殿した薄膜の破砕物を外部に排除する排除装置とを備えていることが好ましい。また、前記濾過した給水は外部へ直接的に廃棄し、または前記給水装置に回収して再利用することができる。
【0016】
【発明の実施の形態】
以下、図面を参照しながら本発明の排煙脱硫設備の好ましい実施形態を詳しく説明する。なお、以下の説明においては、そのサイズに拘わらず、略同一の機能及び構成を有する構成要素については、同一符号を付し、重複説明は必要な場合にのみ行う。
【0017】
本発明の排煙脱硫設備3は、加水によって濡らされた脱硫用粒子群とボイラーなどの燃焼排煙とを接触させることによって、排煙における硫黄酸化物を除去した後、脱硫用粒子を回収して再利用するものである。図3に示すように、該排煙脱硫設備3は、主として粒子供給装置4と、脱硫装置5と、分離装置6と、給水装置7と、回収装置8と、濾過装置9と、排除装置10とからなる。もっと詳しく説明すると、図3及び図4に示すように、前記粒子供給装置4は、加水によって濡らされた例えば炭酸カルシウムなどの脱硫用粒子31を蓄積している蓄積タンク41と、前記蓄積タンク41に蓄積されている脱硫用粒子31を前記蓄積タンク41の下側から前記脱硫装置5の上方まで輸送する水平輸送パイプ42及び垂直輸送パイプ43と、前記水平輸送パイプ42及び垂直輸送パイプ43と連通していて、前記脱硫装置5の上方まで輸送された脱硫用粒子31を前記脱硫装置5内へ供給して充填する粒子供給手段44と、前記脱硫装置5への供給に余った脱硫用粒子31を前記蓄積タンク41に回流させる粒子回流パイプ45とからなる。
【0018】
また、前記粒子供給手段44は、その両端が前記垂直輸送パイプ43及び前記粒子回流パイプ45とそれぞれ連通している粒子供給パイプ441と、前記粒子供給パイプ441の下面に左右方向(軸方向)に隙間を空けて並列している複数の粒子供給器442と、それぞれ前記粒子供給パイプ441と前記複数の粒子供給器442との間に設けられている複数のゲート付き開口443とを備えてなる。
【0019】
そして、前記脱硫装置5は、前記粒子供給装置4の複数の粒子供給器442の下方に設けられているハウジング51と、前記複数の粒子供給器442に対応して前記ハウジング51内に左右方向に隙間を空けて並列し、前記ハウジング51を前室511と後室512との二室に仕切っている複数の脱硫塔52とからなる。
【0020】
そして、前記ハウジング51の前記前室511の方に、排煙の入り口5110が設けられ、前記後室512の方に、排煙の出口5120が設けられている。前記複数の脱硫塔52は、いずれも、図4及び図5に示すように、前後一対の立て板521,522の間に、隙間523を空けて左右対立している一対の立てフレーム524,524を立設してなる。前記一対の立てフレーム524,524は、前記脱硫用粒子31を直立壁のように積んで保持し、且つ前記直立壁のような脱硫用粒子群の左右両側の壁面を前記ハウジング51内の排煙に開放させるものである。また、各脱硫塔52の前記後ろの立て板522はそれぞれ他の全ての脱硫塔52の後ろの立て板522と互いに連接して一体になり、且つその面上に、各脱硫塔52の前記一対の立てフレーム524,524間の隙間523によって形成されている通路とそれぞれ連通する複数のゲート付き開口5220が設けられている。
【0021】
前記一対の立てフレーム524,524は、いずれも、複数の平板組み5240を隙間を空けて上下配列してなる。前記複数の平板組み5240は、いずれも、その間の空間が下から上へ徐々に展開した2の対向する平板5241からなる。本実施形態において、前記平板5241は、図6に示すように、その上縁が水平面と75度になるように上へ反り、下縁が水平面と75度になるように下へ反っている。また、前記前後一対の立て板521,522の間には、前記立て板521,522と平行する複数の仕切板525が前記複数の平板組み5240を前後等距離に分割するように並列してある。図5をもっと詳しくみると、前記複数の平板5241は、いずれも、前記複数の仕切板525同士間にそれぞれ挟まれている小平板5242から前後連続してなる。また、前記仕切板525には、それぞれ前記一対の立てフレーム524,524間の隙間523と前記立てフレーム524の粒子堆積空間と連通している複数の通孔5250が開けてある。
【0022】
そして、前記分離装置6は、図4及び図7に示すように、前記複数の脱硫塔の真下にそれぞれ右上から左下へ斜めに設けられていて、それらのメッシュが前記脱硫用粒子31より小である複数の主篩61と、前記複数の主篩61の上方にそれぞれ左上から右下へ斜めに設けられていて、それらのメッシュが前記脱硫用粒子31より小である複数の副篩62と、前記複数の主篩61及び副篩62の下方に設けられていて、前記複数の篩61,62をそれぞれ振動する複数の振動器63と、前記複数の副篩62の下端側から隣りの他の主篩61の下方に前記複数の主篩61とそれぞれ平行して延伸してなる複数の邪魔板64とからなる。
【0023】
前記給水装置7は、図4及び図7に示すように、前記粒子供給器442毎の前記立てフレーム524の上方に設けられていて、前記立てフレーム524に保持されている脱硫用粒子群へ給水する第1の給水器71と、前記篩61,62毎の上方に設けられていて、前記篩61,62へ給水する第2の給水器72とからなる。
【0024】
前記回収装置8は、図3、図4及び図8に示すように、粒子回収手段81と収集手段82とからなる。注意すべきは、該粒子回収手段81は前記粒子供給装置4中の一部の部材を利用している。即ち、前記粒子回収手段81は、前記主篩61毎の下端側に設けられていて、前記脱硫用粒子31を回収する複数の回収タンク810を備えている。また、前記複数の回収タンク810の下面は、前記粒子供給装置4の前記水平輸送パイプ42と連通している。それにより、前記回収した脱硫用粒子31は、前記水平輸送パイプ42及び垂直輸送パイプ43を経由して前記粒子供給手段44に輸送されることができる。
【0025】
そして、前記収集手段82は、前記複数の主篩61の真下に設けられていて、前記主篩61及び副篩62から落ちた下記薄膜の破砕物と給水とを収集する収集タンク820からなる。
【0026】
以下、図3、図4及び図9を参照しながら本発明の排煙脱硫設備により脱硫工程及び粒子再生工程を行う過程を説明する。まず、排煙の脱硫工程をしようとする場合、前記複数の粒子供給器442と前記粒子供給パイプ441との間の複数のゲート付き開口443を開け、前記蓄積タンク41から前記水平輸送パイプ42及び垂直輸送パイプ43を経由して濡らされた炭酸カルシウムなどの脱硫用粒子31を前記複数の粒子供給器442に輸送してから、三角柱の案内部材444を経由して各脱硫塔52の一対の立てフレーム524内に落ち込ませて直立壁のように堆積し、そして、前記排煙の入り口5110を開け、この時、排煙は、図9に示すように、前記入り口5110から入った後、前記複数の脱硫塔52同士間の隙間に入って、前記立てフレーム524に保持されている脱硫用粒子群の左右両側の壁面の一方から他方へ通過し、脱硫をした後、前記一対の立てフレーム524,524間の通路523に入って前記ゲート付き開口5220を通過し、前記出口5120を経由して出ることができる。また、前記濡らされた脱硫用粒子31は、排煙中における硫黄酸化物(SO,SOなど)と反応した後、その表面に硫酸カルシウムまたは亜硫酸カルシウム薄膜が形成する。
【0027】
そして、所定時間の稼動を経った後、例えば前記複数の脱硫塔中の一部の脱硫塔(脱硫塔Aを例として)を再生しようとする場合、まず、図9に示すように、脱硫塔Aのゲート付き開口5220を閉じて当該脱硫塔A内への排煙をストップし、残りの脱硫塔B、Cなどだけへ排煙を流通させ、そして、前記第1と第2の給水器71,72を開けると共に脱硫塔Aの下方の複数の振動器63を作動させて前記篩61,62を振るって、前記薄膜が付着している脱硫用粒子31を下へと徐々に移動させながら、脱硫用粒子31同士間の摩擦や衝突によって前記薄膜を砕き、脱硫用粒子31から分離させることができる。また、前記脱硫用粒子31を前記主篩61及び前記副篩62上に正確的に落とすため、前記主篩61及び前記副篩62と前記一対の立てフレーム524,524との間に複数の案内板526が設けられている。
【0028】
前記再生した脱硫用粒子31は、前記主篩61の斜面に沿って前記回収タンク810に落ちて前記水平と垂直輸送パイプ42,43を経由して脱硫塔Aの上方の粒子供給器442へ回流することができる。前記主篩61と前記副篩62の篩目から落ちた硫酸カルシウム薄膜の破砕物と給水とは、前記収集タンク820に落ちることができる。この時、密度が水の密度より小である薄膜の破砕物は水面に浮き、水の密度より大である薄膜の破砕物は前記収集タンク820の底面に沈んで沈殿物となる。本実施形態において、前記収集タンク820の上層の水層は、案内板91を介して後述の濾過装置9に輸送されて前記破砕物を給水から除去し、給水を回収する。前記収集タンク820の底面に沈んだ破砕物の沈殿物は、後述の排除装置10を介して外部に排除される。
【0029】
前記濾過装置9は、図3に示すように、前記収集タンク820の傍に設けられている給水回収タンク92と、前記給水回収タンク92の上方に渡っていて、そのメッシュが前記破砕物より小である濾過用布93と、前記収集タンク820の上層の水層を前記濾過用布93上に案内する前記案内板91とからなる。それにより、前記収集タンク820の上層に収集された薄膜の破砕物と前記給水とからなる混濁液を濾過して前記破砕物を給水から除去し、該給水を外部へ直接的に廃棄し、または前記給水装置7に回収して再利用することができるようにさせる。
【0030】
そして、前記排除装置10は、図3及び図8に示すように、前記収集タンク820の底面にある沈殿物を受ける第1のスクリューコンベヤ101と、その一端が前記第1のスクリューコンベヤ101と連接し、他端が前記収集タンク820より高いように直立している第2のスクリューコンベヤ102とからなる。それにより、モータの作動によって、前記収集タンク820の底面に沈んだ薄膜の破砕物の沈殿物を前記第1のスクリューコンベヤ101及び前記第2のスクリューコンベヤ102を介して外部に排除することができる。また、前記第2のスクリューコンベヤ102の他端が前記収集タンク820の高さより高いので、前記薄膜の破砕物の沈殿物が排除されるが、給水が排除されない。
【0031】
【発明の効果】
この構成による排煙脱硫設備は、粒子群を動かさない状態で脱硫工程を行うので、前記流動式のキャリオーバまたは排煙の出口を塞ぐことなどの問題がなく、且つ、再生工程において粒子が流動の状態で互いに摩擦したり衝突したりし、前記薄膜を砕いて脱硫用粒子から分離させるので、前記立てフレーム内に大量の脱硫用粒子を収容しても薄膜の分離効果が良い。また、前記排煙は前記脱硫用粒子群の左右両側の壁面の一方から他方へ通過しているため、前記立てフレーム内に大量の脱硫用粒子が堆積しても、前記立てフレームの保持により前記脱硫用粒子群の厚さがちっとも変らないので、排煙通過の抵抗が従来の固定式のように大きくなることがない。即ち、本発明の排煙脱硫設備は、脱硫効果がよい上、脱硫塔毎の稼動可能な時間は従来の固定式よりずっと長い。その外、複数の単独作業のできる脱硫塔が設けられているので、一部の脱硫塔の脱硫用粒子の再生中、他の脱硫塔に脱硫工程を実施し続けることができる。また、再生工程において、脱硫用粒子へ給水しながら薄膜の分離を行っているので、薄膜の分離効果がよい上、高温の排煙により熱くなった脱硫用粒子を冷却したり濡らしたりし、脱硫用粒子からの灰塵飛散を避けることもできる。
【0032】
以上説明した実施の形態は、あくまでも本発明の技術的内容を明らかにする意図のものにおいてなされたものであり、本発明はそうした具体例に限定して狭義に解釈されるものではなく、本発明の精神とクレームに述べられた範囲で、いろいろと変更して実施できるものである。
【図面の簡単な説明】
【図1】従来の固定式排煙脱硫設備の一部を模式的に示す説明図。
【図2】従来の流動式排煙脱硫設備の一部を模式的に示す説明図。
【図3】本発明の排煙脱硫設備の好ましい実施形態の構造関係斜視図。
【図4】図3のI−I線の一部拡大断面図。
【図5】前記実施形態における脱硫塔の分解斜視図。
【図6】前記脱硫塔を構成する平板の拡大説明図。
【図7】前記実施形態の一部拡大斜視図。
【図8】前記実施形態の他の一部拡大斜視図。
【図9】図3のII−II線の断面図。
【符号の説明】
3…排煙脱硫設備、31…脱硫用粒子、4…粒子供給装置、5…脱硫装置、51…ハウジング、511…前室、5110…入り口、512…後室、5120…出口、52…脱硫塔、521,522…立て板、5220…ゲート付き開口、524…立てフレーム、5240…平板組み、5241…平板、6…分離装置、61,62…篩、63…振動器、7…給水装置、71…第1の給水器、72…第2の給水器、8…回収装置、81…回収手段、82…収集手段、9…濾過装置、10…排除装置。
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a flue gas desulfurization facility, in particular, contacts with flue gas at a desulfurization particle group wetted by water to remove sulfur oxides in the flue gas, and then collects and reuses the desulfurization particles. It relates to flue gas desulfurization equipment.
[0002]
[Prior art]
One of the conventional flue gas desulfurization methods for removing sulfur oxides from combustion flue gas from boilers and the like is a method for removing sulfur oxides in flue gas using wet desulfurization particles, for example, calcium carbonate (limestone) particles. (SO 2 , SO 3, etc.) to form a thin film of calcium sulfate or calcium sulfite on the surface of the calcium carbonate particles, thereby removing the sulfur oxides from the flue gas. The flue gas desulfurization equipment to which this method is applied is mainly divided into two types: fixed type and flow type.
[0003]
The flue gas desulfurization equipment 1 shown in FIG. 1 is a fixed type example. When desulfurization is to be performed from flue gas by the flue gas desulfurization equipment 1, first, the valve 11 is opened and unhydrolyzed desulfurization particles, for example, calcium carbonate particles 121 are supplied from the particle accumulation tank 12 into the desulfurization chamber 13. Then, the water is supplied to the calcium carbonate particle group 121 by the water supply device 14 provided above the desulfurization chamber 13 to wet the calcium carbonate particle group 121, and then the valves 15A and 15B are opened to remove the flue gas. A desulfurization step of performing desulfurization from 151 through the calcium carbonate particle group 121, the sieve 16, the branch passage 152, and the flue 17 in order and then exhausting to the outside can be performed. After the operation for a predetermined time, the valves 15A and 15B are closed, and the vibrator 18 provided on the lower surface of the sieve 16 is operated to vibrate the particle group 121 in the desulfurization chamber 13, and The calcium sulfate thin film formed on the surface of the calcium carbonate particle 121 is crushed and separated from the calcium carbonate particle 121 by friction or collision between the particles, and then the valves 15C and 15D are opened. The process of regenerating the calcium carbonate particles 121 for collecting and removing the substances from the desulfurization chamber 13 is performed. After finishing the regeneration step, the unhydrated calcium carbonate particles 121 are captured from the particle accumulation tank 12 into the desulfurization chamber 13, and subsequently, the water is supplied to the calcium carbonate particle group 121 by the water supply device 14, The desulfurization step can be performed again. Since the flue gas desulfurization equipment 1 usually includes a plurality of the desulfurization chambers 13, the step of regenerating the desulfurization particles can be performed in the plurality of desulfurization chambers 13 one by one. During, the desulfurization step can be continued.
[0004]
In the flue gas desulfurization equipment 1, the desulfurization particles 121 do not move when moving through the desulfurization process, that is, are stationary, so that the equipment is simple and effective, but once the desulfurization particle group 121 If the accumulation is too thick, the resistance of the smoke exhaust passage becomes large, the smoke exhaust becomes difficult to pass through the particle group 121, and the vibration effect at the time of regeneration does not reach the upper layer particles, and the thin film separation effect is deteriorated. Because of the various problems described above, the amount of the particles for desulfurization to be deposited is considerably limited, so that the use time of the desulfurization chamber 13 is short and the regeneration step must be performed frequently.
[0005]
The flue gas desulfurization equipment 2 shown in FIG. 2 is an example of a flow type. The flue gas desulfurization facility 2 includes a plurality of parallel desulfurization towers 20. During the course of the desulfurization step, a group of calcium carbonate particles 21 as desulfurization particles wetted by water flows continuously from the top to the bottom of each of the desulfurization towers 20 in the plurality of desulfurization towers 20. . Simultaneously with the flow of the particle group 21, the flue gas enters through the inlet 22, breaks into the flowing particle group 21 and passes therethrough, performs desulfurization, and then exhausts to the outside through the gap 23 between the desulfurization towers 20. are doing.
[0006]
The flue gas desulfurization equipment 2 that performs desulfurization with the flowing particles has a long operable time, but performs desulfurization in a state where the particles flow, so that the desulfurization occurs due to friction or collision between the particles during the flow. The thin film formed on the surface of the particles for use is crushed and separated from the particles for desulfurization, and the crushed material of the thin film is discharged to the outside together with the exhaust gas after desulfurization to block the outlet of the exhaust gas or carry over to the outside air. Thus, there is a disadvantage that the desulfurized exhaust gas is contaminated.
[0007]
[Problems to be solved by the invention]
In view of the above, it is an object of the present invention to provide a conventional flow type that has no problems such as a carry-over or a blockage of an exhaust gas outlet, and that the operating time of each desulfurization unit is considerably longer than that of the conventional fixed type. It is to provide a desulfurization facility.
[0008]
[Means for Solving the Problems]
In order to achieve the above object, the inventor firstly removes sulfur oxides in flue gas by bringing the desulfurizing particle group wet with water into contact with flue gas, and then recovers the desulfurizing particles. In the flue gas desulfurization equipment to be reused, passing the flue gas in a state containing the wet desulfurization particle group, reacting the sulfur oxide in the flue gas with the surface of the desulfurization particles A desulfurization device that adheres and bonds to form a thin film and removes sulfur oxides from the flue gas, and a desulfurization device that is provided below the desulfurization device and vibrates to lower the desulfurization particles to which the thin film is attached. While gradually moving, the thin film is crushed by friction or collision between the desulfurization particles, a separation device for separating from the desulfurization particles, a water supply device for supplying water to the desulfurization particle group, and below the separation device. Provided and before Providing flue gas desulfurization equipment, characterized in that the desulfurization particles to remove thin films formed by a collecting device to collect and recycle in the desulfurization apparatus.
[0009]
Since the flue gas desulfurization equipment according to this configuration performs the desulfurization step without moving the particle group, there is no problem such as blocking the outlet of the carryover or the flue gas, and the particles are mutually flowing in the regeneration step in the regeneration step. Since the thin film is crushed and crushed and separated from the particles for desulfurization, the separating effect of the thin film is good even if a large amount of the particles for desulfurization are accommodated in the desulfurization device.
[0010]
The desulfurization apparatus includes a housing and a plurality of desulfurization towers arranged in parallel in the housing with a gap in the left-right direction, with the housing partitioned into two chambers, a front chamber and a rear chamber. An inlet for exhaust gas is provided toward the front chamber, an outlet for exhaust gas is provided toward the rear chamber, and the plurality of desulfurization towers each include the wet desulfurization particles. A vertical frame that holds and holds the group as an upright wall (or an upright fence) and that opens the left and right side walls of the desulfurization particle group such as the upright wall to the smoke exhaust in the housing. Is preferred. Thereby, after the flue gas enters from the entrance, it enters the gap between the plurality of desulfurization towers and passes from one of the left and right side walls of the desulfurization particle group held by the vertical frame to the other. However, since it is possible to exit via the outlet, even if a large amount of desulfurization particles are accumulated in the standing frame, the thickness of the desulfurization particle group does not change at all by holding the standing frame, The resistance to smoke exhaust does not increase as in the conventional fixed type. That is, since the flue gas desulfurization equipment of the present invention can deposit a large amount of desulfurization particles in the desulfurization tower as the desulfurization unit, the operable time of each desulfurization unit is much longer than that of the conventional fixed type.
[0011]
Each of the plurality of desulfurization towers has a pair of standing frames that are left and right opposed to each other with a gap between a pair of front and rear standing plates, and the rear standing plate is all other members. A plurality of gated openings communicating with a passage formed by a gap between the pair of standing frames of each of the desulfurization towers. Is preferred. Thereby, the flue gas that has passed through the desulfurization particle group held in one of the pair of standing frames after entering the gap between the plurality of desulfurization towers is first passed through the passage between the pair of standing frames. It can enter, pass through the gated opening and only exit through the exit. Further, after the operation for a predetermined time, when attempting to regenerate some of the desulfurization towers in the plurality of desulfurization towers, close the gated opening between the pair of vertical frames of each of the desulfurization towers. Since the flue gas into some of the desulfurization towers can be stopped and the flue gas can be circulated only to the remaining desulfurization towers, the other remaining desulfurization towers can recycle the flue gas during regeneration of some of the desulfurization towers. The desulfurization step can be continued.
[0012]
In addition, it is preferable that the vertical frame is formed by vertically arranging a plurality of flat plate sets including two opposing flat plates in which a space therebetween is gradually developed from bottom to top with a gap therebetween. Thereby, the smoke exhaust can permeate from one surface of the wall of the desulfurization particle group to the other surface via the gap between the upper and lower flat plate assemblies. Further, it is preferable that the flat plate is configured such that an upper edge thereof is warped upward and a lower edge thereof is warped downward. Thereby, the structural strength of the flat plate is increased, and the desulfurizing particle group can be stably held on the vertical frame, and the desulfurizing particles can be stuck between a plurality of desulfurizing towers via a gap between the upper and lower flat plate assemblies. It is also possible to avoid falling into the passage between the standing frames.
[0013]
The flue gas desulfurization equipment further includes a particle supply device that supplies the wet desulfurization particles into the upright frames of the plurality of desulfurization towers, respectively, and the separation device is provided directly below the plurality of desulfurization towers, respectively. A plurality of sieves that are provided diagonally and whose meshes are smaller than the particles for desulfurization, and include a plurality of vibrators that respectively vibrate the plurality of sieves, wherein the water supply device is provided for each of the standing frames. A first water supply provided above and supplying water to the desulfurization particles held by the vertical frame, and a second water supply provided above each sieve and supplying water to the sieve And preferably As a result, the particle supply to each desulfurization tower, the wetting operation, and the regeneration step can be performed independently, so that the desulfurization step is continuously performed on the other desulfurization towers during the regeneration of the desulfurization particles of some desulfurization towers. Can be.
[0014]
The recovery device is provided at a lower end side of the sieve, and a particle recovery unit that recovers the desulfurization particles from which the thin film has been removed and transports the particles into the vertical frame, and is provided directly below the sieve. Preferably, the apparatus further comprises a collecting means for collecting the crushed thin film dropped from the sieve and water (or supplied water). Thereby, the particles for desulfurization can be collected and reused.
[0015]
In addition, the collecting means comprises a collecting tank, and near the collecting tank, also guides the upper water layer of the collecting tank to remove the turbid liquid consisting of the crushed material of the thin film and the water supply. It is preferable to have a filtration device for removing the crushed material from the feed water by filtration, and an elimination device for removing the crushed material of the thin film settled on the bottom surface of the collection tank to the outside. Further, the filtered water supply can be directly discarded to the outside, or collected in the water supply device and reused.
[0016]
BEST MODE FOR CARRYING OUT THE INVENTION
Hereinafter, preferred embodiments of the flue gas desulfurization equipment of the present invention will be described in detail with reference to the drawings. In the following description, components having substantially the same function and configuration will be denoted by the same reference numerals, regardless of their size, and repeated description will be made only when necessary.
[0017]
The flue gas desulfurization equipment 3 of the present invention removes sulfur oxides in flue gas by bringing the desulfurization particle group wet with water into contact with combustion flue gas from a boiler or the like, and then recovers the desulfurization particles. And reuse it. As shown in FIG. 3, the flue gas desulfurization equipment 3 mainly includes a particle supply device 4, a desulfurization device 5, a separation device 6, a water supply device 7, a recovery device 8, a filtration device 9, a rejection device 10 Consists of More specifically, as shown in FIGS. 3 and 4, the particle supply device 4 includes a storage tank 41 storing desulfurization particles 31 such as calcium carbonate wetted by water, and a storage tank 41. A horizontal transport pipe 42 and a vertical transport pipe 43 for transporting the desulfurization particles 31 stored in the storage tank 41 from below the storage tank 41 to above the desulfurization apparatus 5, and communicates with the horizontal transport pipe 42 and the vertical transport pipe 43. A particle supply means 44 for supplying and filling the desulfurization particles 31 transported to above the desulfurization device 5 into the desulfurization device 5; and a desulfurization particle 31 surplus supplied to the desulfurization device 5. And a particle circulating pipe 45 for circulating the particles into the storage tank 41.
[0018]
The particle supply means 44 includes a particle supply pipe 441 having both ends communicating with the vertical transport pipe 43 and the particle circulating pipe 45, respectively, and a lower surface of the particle supply pipe 441 in a left-right direction (axial direction). The apparatus includes a plurality of particle supply devices 442 arranged in parallel with a gap, and a plurality of gated openings 443 provided between the particle supply pipe 441 and the plurality of particle supply devices 442, respectively.
[0019]
The desulfurization device 5 includes a housing 51 provided below the plurality of particle supply devices 442 of the particle supply device 4 and a horizontal direction inside the housing 51 corresponding to the plurality of particle supply devices 442. A plurality of desulfurization towers 52 are arranged side by side with a gap therebetween and partition the housing 51 into two chambers, a front chamber 511 and a rear chamber 512.
[0020]
A smoke exhaust inlet 5110 is provided in the front chamber 511 of the housing 51, and a smoke exhaust outlet 5120 is provided in the rear chamber 512. As shown in FIGS. 4 and 5, each of the plurality of desulfurization towers 52 has a pair of standing frames 524, 524 that are opposed to each other with a gap 523 between a pair of front and rear standing plates 521, 522. To be erected. The pair of upright frames 524 and 524 hold the desulfurizing particles 31 like an upright wall and hold the same, and the left and right side walls of the desulfurizing particle group such as the upright walls in the housing 51 are provided with smoke exhaust. It is open to the public. The rear standing plates 522 of the respective desulfurization towers 52 are connected to and integrated with the rear standing plates 522 of all the other desulfurization towers 52, respectively. Are provided with a plurality of gated openings 5220 that respectively communicate with a passage formed by a gap 523 between the vertical frames 524 and 524.
[0021]
Each of the pair of standing frames 524 and 524 is configured by vertically arranging a plurality of flat plate sets 5240 with a gap. Each of the plurality of flat plate sets 5240 includes two opposing flat plates 5241 in which a space therebetween is gradually developed from bottom to top. In the present embodiment, as shown in FIG. 6, the flat plate 5241 warps upward so that its upper edge is at 75 degrees with the horizontal plane, and warps downward so that its lower edge is at 75 degrees with the horizontal plane. In addition, between the pair of front and rear standing plates 521 and 522, a plurality of partition plates 525 parallel to the standing plates 521 and 522 are arranged in parallel so as to divide the plurality of flat plate sets 5240 into front and rear equal distances. . Referring to FIG. 5 in more detail, each of the plurality of flat plates 5241 is continuously formed in front of and behind a small flat plate 5242 sandwiched between the plurality of partition plates 525. Further, the partition plate 525 has a plurality of through holes 5250 communicating with the gap 523 between the pair of upright frames 524 and 524 and the particle accumulation space of the upright frame 524, respectively.
[0022]
As shown in FIGS. 4 and 7, the separation device 6 is provided diagonally from the upper right to the lower left just below the plurality of desulfurization towers, and their mesh is smaller than the desulfurization particles 31. A plurality of main sieves 61 and a plurality of sub-sieves 62 which are provided diagonally from the upper left to the lower right above the plurality of main sieves 61 and whose meshes are smaller than the desulfurization particles 31; A plurality of vibrators 63 are provided below the plurality of main sieves 61 and the sub-sieves 62 and vibrate the plurality of sieves 61 and 62, respectively, and another vibrator 63 adjacent to the plurality of sub-sieves 62 from the lower end side. Below the main sieve 61, the main sieve 61 and a plurality of baffles 64 extending in parallel with each other.
[0023]
As shown in FIGS. 4 and 7, the water supply device 7 is provided above the vertical frame 524 for each of the particle feeders 442, and supplies water to the desulfurization particle group held by the vertical frame 524. And a second water supply device 72 provided above each of the sieves 61 and 62 to supply water to the sieves 61 and 62.
[0024]
The collecting device 8 includes a particle collecting means 81 and a collecting means 82 as shown in FIGS. It should be noted that the particle collecting means 81 utilizes some members in the particle supply device 4. That is, the particle collecting means 81 is provided at a lower end side of each of the main sieves 61 and includes a plurality of collecting tanks 810 for collecting the desulfurizing particles 31. The lower surfaces of the plurality of recovery tanks 810 communicate with the horizontal transport pipe 42 of the particle supply device 4. Thereby, the recovered desulfurization particles 31 can be transported to the particle supply means 44 via the horizontal transport pipe 42 and the vertical transport pipe 43.
[0025]
The collecting means 82 is provided immediately below the plurality of main sieves 61 and includes a collecting tank 820 for collecting the crushed material of the following thin film dropped from the main sieve 61 and the sub-sieve 62 and water supply.
[0026]
Hereinafter, the process of performing the desulfurization step and the particle regeneration step by the flue gas desulfurization equipment of the present invention will be described with reference to FIGS. 3, 4, and 9. First, when a desulfurization process of flue gas is to be performed, a plurality of gated openings 443 between the plurality of particle supply devices 442 and the particle supply pipes 441 are opened, and the horizontal transport pipes 42 and After transporting the wet desulfurization particles 31 such as calcium carbonate via the vertical transport pipe 43 to the plurality of particle feeders 442, a pair of desulfurization towers 52 of each desulfurization tower 52 via the triangular prism guide member 444. It falls into the frame 524 and accumulates like an upright wall, and opens the smoke exhaust port 5110. At this time, after the smoke exhaust enters the entrance 5110 as shown in FIG. After passing through the gap between the desulfurization towers 52 and passing from one of the left and right wall surfaces of the desulfurization particle group held by the vertical frame 524 to the other, and performing desulfurization, Stand enters the passage 523 between the frames 524,524 through the gated opening 5220, you can exit via the outlet 5120. The wet desulfurization particles 31 react with sulfur oxides (SO 2 , SO 3, etc.) in the flue gas, and then form a calcium sulfate or calcium sulfite thin film on the surface thereof.
[0027]
Then, after a certain period of operation, for example, when trying to regenerate some of the desulfurization towers (for example, desulfurization tower A) among the plurality of desulfurization towers, first, as shown in FIG. The gated opening 5220 of A is closed to stop the flue gas into the desulfurization tower A, and the flue gas is circulated only to the remaining desulfurization towers B, C, and the like. , 72 are opened and the plurality of vibrators 63 below the desulfurization tower A are operated to shake the sieves 61, 62, while gradually moving the desulfurizing particles 31 to which the thin film adheres downward. The thin film can be broken by friction or collision between the desulfurizing particles 31 and separated from the desulfurizing particles 31. Further, in order to accurately drop the desulfurizing particles 31 onto the main sieve 61 and the sub-sieve 62, a plurality of guides are provided between the main sieve 61 and the sub-sieve 62 and the pair of standing frames 524, 524. A plate 526 is provided.
[0028]
The regenerated desulfurization particles 31 fall along the slope of the main sieve 61 into the recovery tank 810, and are circulated to the particle feeder 442 above the desulfurization tower A via the horizontal and vertical transport pipes 42 and 43. can do. The crushed calcium sulfate thin film and water supplied from the sieves of the main sieve 61 and the sub-sieve 62 can fall into the collecting tank 820. At this time, the crushed material of the thin film whose density is smaller than the density of water floats on the water surface, and the crushed material of the thin film whose density is larger than the water density sinks to the bottom of the collection tank 820 and becomes a sediment. In this embodiment, the upper water layer of the collection tank 820 is transported to a filtration device 9 described below via a guide plate 91 to remove the crushed material from the water supply and recover the water supply. The sediment of the crushed material that has settled on the bottom surface of the collection tank 820 is removed to the outside via a removal device 10 described below.
[0029]
As shown in FIG. 3, the filtration device 9 includes a water supply recovery tank 92 provided near the collection tank 820 and a water supply recovery tank 92, and the mesh is smaller than the crushed material. , And the guide plate 91 for guiding the upper aqueous layer of the collection tank 820 onto the filtration cloth 93. Thereby, the turbid liquid composed of the crushed material of the thin film collected in the upper layer of the collection tank 820 and the water supply is filtered to remove the crushed material from the water supply, and the water supply is directly discarded to the outside, or The water is supplied to the water supply device 7 so that it can be reused.
[0030]
Then, as shown in FIG. 3 and FIG. 8, the rejecting device 10 is connected to a first screw conveyor 101 for receiving the sediment on the bottom surface of the collection tank 820, and one end thereof is connected to the first screw conveyor 101. And the second screw conveyor 102 having the other end standing upright so as to be higher than the collection tank 820. Thereby, by the operation of the motor, the sediment of the crushed thin film that has settled on the bottom surface of the collection tank 820 can be removed to the outside via the first screw conveyor 101 and the second screw conveyor 102. . In addition, since the other end of the second screw conveyor 102 is higher than the height of the collection tank 820, sediment of the crushed material of the thin film is eliminated, but water supply is not eliminated.
[0031]
【The invention's effect】
Since the flue gas desulfurization equipment according to this configuration performs the desulfurization step without moving the particle group, there is no problem such as the above-mentioned flow-type carryover or blocking the exit of the flue gas, and the particles are not allowed to flow in the regeneration step. The thin film is crushed and collides with each other in the state, and the thin film is crushed and separated from the desulfurizing particles. Therefore, even if a large amount of the desulfurizing particles are contained in the vertical frame, the effect of separating the thin film is good. Further, because the smoke exhaust passes from one of the left and right side walls of the desulfurization particle group to the other, even if a large amount of desulfurization particles accumulate in the vertical frame, the holding of the vertical frame causes the aforementioned Since the thickness of the desulfurization particle group does not change at all, the resistance of the exhaust gas passage does not increase as in the conventional fixed type. That is, the flue gas desulfurization equipment of the present invention has a good desulfurization effect, and the operable time for each desulfurization tower is much longer than that of the conventional fixed type. In addition, since a plurality of desulfurization towers which can be operated independently are provided, the desulfurization step can be continuously performed on other desulfurization towers during regeneration of the desulfurization particles of some desulfurization towers. In addition, in the regeneration process, the thin film is separated while supplying water to the desulfurization particles, so the thin film separation effect is good, and the desulfurization particles heated by the high-temperature flue gas are cooled or wet, and the desulfurization is performed. It is also possible to avoid scattering of ash dust from the working particles.
[0032]
The embodiments described above are intended to clarify the technical contents of the present invention, and the present invention is not limited to such specific examples and is not interpreted in a narrow sense. Various modifications can be made within the spirit and scope of the claims.
[Brief description of the drawings]
FIG. 1 is an explanatory view schematically showing a part of a conventional fixed-type flue gas desulfurization facility.
FIG. 2 is an explanatory view schematically showing a part of a conventional fluidized flue gas desulfurization facility.
FIG. 3 is a structural perspective view of a preferred embodiment of a flue gas desulfurization facility of the present invention.
FIG. 4 is a partially enlarged cross-sectional view taken along the line II of FIG. 3;
FIG. 5 is an exploded perspective view of the desulfurization tower in the embodiment.
FIG. 6 is an enlarged explanatory view of a flat plate constituting the desulfurization tower.
FIG. 7 is a partially enlarged perspective view of the embodiment.
FIG. 8 is another partially enlarged perspective view of the embodiment.
FIG. 9 is a sectional view taken along line II-II in FIG. 3;
[Explanation of symbols]
3 flue gas desulfurization equipment, 31 particles for desulfurization, 4 particles supply device, 5 desulfurizer, 51 housing, 511 front chamber, 5110 entrance, 512 rear chamber, 5120 outlet, 52 desulfurization tower , 521, 522: Standing plate, 5220: Opening with gate, 524: Standing frame, 5240: Flat plate assembly, 5241: Flat plate, 6: Separation device, 61, 62: Sieve, 63: Vibrator, 7: Water supply device, 71 1st water supply, 72 2nd water supply, 8 ... collection | recovery apparatus, 81 ... collection | recovery means, 82 ... collection | collection means, 9 ... filtration apparatus, 10 ... rejection apparatus.

Claims (7)

加水によって濡らされた脱硫用粒子群と排煙とを接触させることによって、排煙中における硫黄酸化物を除去した後、脱硫用粒子を回収して再利用する排煙脱硫設備であって、
前記濡らされた脱硫用粒子群を収容した状態で前記排煙を通過させ、排煙中における硫黄酸化物を脱硫用粒子の表面と反応させて薄膜となるように付着結合させ、前記排煙から硫黄酸化物を除去する脱硫装置と、
前記脱硫装置の下方に設けられていて、振動によって、前記薄膜が付着している脱硫用粒子を下へと徐々に移動させながら、脱硫用粒子同士間の摩擦や衝突によって前記薄膜を砕き、脱硫用粒子から分離させる分離装置と、
前記脱硫用粒子群へ給水する給水装置と、
前記分離装置の下方に設けられていて、前記薄膜を除去した脱硫用粒子を前記脱硫装置内に回収して再利用する回収装置とを備えてなることを特徴とする排煙脱硫設備。
A flue gas desulfurization facility that removes sulfur oxides in the flue gas by contacting the desulfurization particles and the flue gas that have been wetted by water to collect and reuse the desulfurizing particles,
The flue gas is passed in a state in which the wet desulfurization particles are accommodated, and the sulfur oxide in the flue gas is reacted with the surface of the desulfurization particles to adhere and bond to form a thin film. A desulfurization device for removing sulfur oxides,
The thin film is provided below the desulfurization device, and crushes the thin film by friction or collision between the desulfurization particles while gradually moving the desulfurization particles to which the thin film adheres downward by vibration. Separation device for separating from the particles for use,
A water supply device for supplying water to the desulfurization particle group,
A flue gas desulfurization facility, comprising: a recovery device provided below the separation device, for recovering the desulfurization particles from which the thin film has been removed into the desulfurization device and reusing the particles.
前記脱硫装置は、ハウジングと、前記ハウジング内に左右方向に隙間を空けて並列し、前記ハウジングを前室と後室との二室に仕切っている複数の脱硫塔とからなり、
前記ハウジングの前記前室の方に排煙の入り口が設けられ、前記後室の方に排煙の出口が設けられており、
また、前記複数の脱硫塔は、
前記濡らされた脱硫用粒子群を直立壁のように積んで保持し、且つ、前記直立壁のような脱硫用粒子群の左右両側の壁面を前記ハウジング内の排煙に開放させる立てフレームからなり、
それにより、前記排煙は前記入り口から入った後、前記複数の脱硫塔同士間の隙間に入って、前記立てフレームに保持されている脱硫用粒子群を通過し、前記出口を経由して出ることができることを特徴とする請求項1に記載の排煙脱硫設備。
The desulfurization device includes a housing and a plurality of desulfurization towers that are arranged side by side in the housing with a gap in the left-right direction, and partition the housing into two chambers, a front chamber and a rear chamber,
An inlet for exhaust gas is provided toward the front room of the housing, and an outlet for exhaust gas is provided toward the rear room,
Further, the plurality of desulfurization towers,
A standing frame for holding the wet desulfurization particle group as an upright wall and holding the same, and opening left and right side walls of the desulfurization particle group such as the upright wall to smoke exhaust in the housing. ,
Thereby, after the flue gas enters from the entrance, it enters the gap between the plurality of desulfurization towers, passes through the desulfurization particle group held in the vertical frame, and exits through the outlet. The flue gas desulfurization equipment according to claim 1, wherein the desulfurization equipment can be used.
前記複数の脱硫塔は、いずれも、前後一対の立て板の間に隙間を空けて左右対立している一対の前記立てフレームを立設してなり、且つ、前記後ろの立て板は他の全ての脱硫塔の後ろの立て板と互いに連接して一体になり、その面上にまた各脱硫塔の前記一対の立てフレーム間の隙間によって形成されている通路と連通するゲート付き開口が複数設けられており、
それにより、前記複数の脱硫塔同士間の隙間に入ってから前記一対の立てフレームの一つに保持されている脱硫用粒子群を通過した排煙は、先に前記一対の立てフレーム間の通路に入って前記ゲート付き開口を通過し、初めて前記出口を経由して出ることができることを特徴とする請求項2に記載の排煙脱硫設備。
In each of the plurality of desulfurization towers, a pair of the upright frames that are opposed to each other with a gap between a pair of front and rear uprights are erected, and the rear uprights are all other desulfurization. A plurality of gated openings communicating with a passage formed by a gap between the pair of standing frames of each desulfurization tower are provided on the surface thereof, and a plurality of openings with gates are provided. ,
Thereby, the flue gas that has passed through the desulfurization particle group held in one of the pair of standing frames after entering the gap between the plurality of desulfurization towers is first passed through the passage between the pair of standing frames. 3. The flue gas desulfurization facility according to claim 2, wherein the apparatus can enter, pass through the gated opening, and exit through the outlet for the first time.
前記立てフレームは、その間の空間が下から上へ徐々に展開した2の対向する平板からなる平板組みを隙間を空けて上下複数配列してなり、
前記平板は、その上縁が上へ反り、下縁が下へ反ったことを特徴とする請求項2または3に記載の排煙脱硫設備。
The vertical frame is formed by arranging a plurality of flat plate sets including two opposing flat plates in which a space therebetween gradually expands from bottom to top with a gap therebetween,
4. The flue gas desulfurization facility according to claim 2, wherein the flat plate has an upper edge warped upward and a lower edge warped downward. 5.
濡らされた脱硫用粒子を前記複数の脱硫塔それぞれの立てフレーム内に供給する粒子供給装置を更に備え、
前記分離装置は、前記複数の脱硫塔の真下にそれぞれ斜めに設けられていて、それらのメッシュが前記脱硫用粒子より小である複数の篩と、前記複数の篩をそれぞれ振動する複数の振動器とからなり、
前記給水装置は、前記立てフレーム毎の上方に設けられていて、前記立てフレームに保持されている脱硫用粒子群へ給水する第1の給水器と、前記篩毎の上方に設けられていて、前記篩へ給水する第2の給水器とからなることを特徴とする請求項2または3に記載の排煙脱硫設備。
Further comprising a particle supply device for supplying the wet desulfurization particles into the standing frame of each of the plurality of desulfurization towers,
The separation device is provided diagonally below each of the plurality of desulfurization towers, a plurality of sieves whose meshes are smaller than the particles for desulfurization, and a plurality of vibrators each vibrating the plurality of sieves. Consisting of
The water supply device is provided above each of the standing frames, a first water supply for supplying water to the desulfurization particles held by the standing frame, and provided above each of the sieves, The flue gas desulfurization facility according to claim 2 or 3, comprising a second water supply device for supplying water to the sieve.
前記回収装置は、前記篩の下端側に設けられていて、前記薄膜を除去した脱硫用粒子を回収して前記立てフレーム内へ輸送する粒子回収手段と、前記篩の真下に設けられていて、前記篩から落ちた薄膜の破砕物と給水とを収集する収集手段とを備えてなることを特徴とする請求項5に記載の排煙脱硫設備。The recovery device is provided at the lower end side of the sieve, a particle recovery means for recovering the desulfurization particles from which the thin film has been removed and transporting the particles into the vertical frame, and provided under the sieve, The flue gas desulfurization equipment according to claim 5, further comprising a collecting means for collecting the crushed material of the thin film dropped from the sieve and the water supply. 前記収集手段は、収集タンクからなり、且つ、この収集タンクの近くには、前記収集タンクの上層の水層を案内して、前記薄膜の破砕物と前記給水とからなる混濁液を濾過して前記破砕物を給水から除去する濾過装置と、前記収集タンクの底面に沈殿した薄膜の破砕物を外部に排除する排除装置とを備えていることを特徴とする請求項6に記載の排煙脱硫設備。The collecting means comprises a collecting tank, and near the collecting tank, guides an upper water layer of the collecting tank, and filters a turbid liquid consisting of the crushed material of the thin film and the water supply. The flue gas desulfurization according to claim 6, further comprising: a filtration device for removing the crushed material from the water supply; Facility.
JP2002368406A 2002-12-19 2002-12-19 Flue gas desulfurization apparatus Pending JP2004195394A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107860237A (en) * 2017-09-30 2018-03-30 四川伊索新型节能材料有限公司 A kind of side column formula kiln body desulfurizer
CN112933910A (en) * 2021-03-08 2021-06-11 上海交通大学 Moving bed coupling absorption desulfurization method based on flue gas semidry method

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107860237A (en) * 2017-09-30 2018-03-30 四川伊索新型节能材料有限公司 A kind of side column formula kiln body desulfurizer
CN107860237B (en) * 2017-09-30 2024-05-10 南京善若网络科技有限公司 Side column type kiln body desulfurizing device
CN112933910A (en) * 2021-03-08 2021-06-11 上海交通大学 Moving bed coupling absorption desulfurization method based on flue gas semidry method
CN112933910B (en) * 2021-03-08 2022-11-08 上海交通大学 Moving bed coupling absorption desulfurization method based on flue gas semidry method

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