JPH0938454A - Method and apparatus for supplying oxidizing air to flue gas desulfurization apparatus - Google Patents
Method and apparatus for supplying oxidizing air to flue gas desulfurization apparatusInfo
- Publication number
- JPH0938454A JPH0938454A JP7194863A JP19486395A JPH0938454A JP H0938454 A JPH0938454 A JP H0938454A JP 7194863 A JP7194863 A JP 7194863A JP 19486395 A JP19486395 A JP 19486395A JP H0938454 A JPH0938454 A JP H0938454A
- Authority
- JP
- Japan
- Prior art keywords
- flow rate
- signal
- air flow
- redox potential
- oxidizing air
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 230000001590 oxidative effect Effects 0.000 title claims abstract description 65
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 16
- 239000003546 flue gas Substances 0.000 title claims abstract description 16
- 238000006477 desulfuration reaction Methods 0.000 title claims description 33
- 230000023556 desulfurization Effects 0.000 title claims description 33
- 238000000034 method Methods 0.000 title claims description 8
- 238000010521 absorption reaction Methods 0.000 claims abstract description 35
- 230000002745 absorbent Effects 0.000 claims abstract description 26
- 239000002250 absorbent Substances 0.000 claims abstract description 26
- 230000033116 oxidation-reduction process Effects 0.000 claims abstract description 19
- 229910052602 gypsum Inorganic materials 0.000 claims abstract description 8
- 239000010440 gypsum Substances 0.000 claims abstract description 8
- 239000007788 liquid Substances 0.000 claims description 63
- 239000007789 gas Substances 0.000 claims description 37
- 238000001514 detection method Methods 0.000 claims description 29
- 229910052815 sulfur oxide Inorganic materials 0.000 claims description 19
- 238000004065 wastewater treatment Methods 0.000 claims description 17
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 9
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 9
- 239000004571 lime Substances 0.000 claims description 9
- 230000002265 prevention Effects 0.000 claims description 9
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 claims description 7
- 229910017464 nitrogen compound Inorganic materials 0.000 claims description 6
- 150000002830 nitrogen compounds Chemical class 0.000 claims description 6
- 238000007664 blowing Methods 0.000 claims description 3
- 239000006096 absorbing agent Substances 0.000 claims 1
- 241000894006 Bacteria Species 0.000 abstract description 11
- 230000001546 nitrifying effect Effects 0.000 abstract description 9
- 239000002351 wastewater Substances 0.000 abstract description 5
- 239000002912 waste gas Substances 0.000 abstract 4
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract 2
- 230000009849 deactivation Effects 0.000 abstract 1
- 230000006866 deterioration Effects 0.000 abstract 1
- 229910052757 nitrogen Inorganic materials 0.000 abstract 1
- 230000003247 decreasing effect Effects 0.000 description 12
- 230000003647 oxidation Effects 0.000 description 8
- 238000007254 oxidation reaction Methods 0.000 description 8
- 239000002002 slurry Substances 0.000 description 8
- 230000000694 effects Effects 0.000 description 7
- 239000002562 thickening agent Substances 0.000 description 7
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 6
- 230000007423 decrease Effects 0.000 description 6
- 239000000460 chlorine Substances 0.000 description 5
- 238000010586 diagram Methods 0.000 description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 5
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 4
- 229910052801 chlorine Inorganic materials 0.000 description 4
- 239000012452 mother liquor Substances 0.000 description 4
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 239000000292 calcium oxide Substances 0.000 description 3
- 235000012255 calcium oxide Nutrition 0.000 description 3
- 238000006386 neutralization reaction Methods 0.000 description 3
- 230000000630 rising effect Effects 0.000 description 3
- 239000007921 spray Substances 0.000 description 3
- 238000003756 stirring Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 2
- 239000000706 filtrate Substances 0.000 description 2
- 230000003472 neutralizing effect Effects 0.000 description 2
- 239000004575 stone Substances 0.000 description 2
- 239000006228 supernatant Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000011505 plaster Substances 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 230000004043 responsiveness Effects 0.000 description 1
- 235000011121 sodium hydroxide Nutrition 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 238000011282 treatment Methods 0.000 description 1
- 241001148471 unidentified anaerobic bacterium Species 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
Abstract
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、排煙脱硫装置の酸
化空気供給方法及び装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for supplying oxidizing air to a flue gas desulfurization apparatus.
【0002】[0002]
【従来の技術】従来、吸収剤として石灰CaO(石灰
石、消石灰又は生石灰)を用いた排煙脱硫装置は、一般
に図4に示されるように、下部に形成された液溜り部1
の吸収液2を、循環ポンプ3の作動により、上部に配設
されたスプレーノズル4から噴霧して循環させると共
に、排ガス導入ダクト5aを介して外部から供給される
排ガスGを、前記スプレーノズル4から噴霧された吸収
液2と接触せしめた後、排ガス導出ダクト5bを介して
排出させる吸収塔5を備えており、該吸収塔5の前記液
溜り部1に、吸収液2の石灰CaOと排ガスG中の硫黄
Sとの反応物CaSO 3を酸化させてCaSO4とする石
膏酸化用の酸化空気Aを供給する圧縮機6を備えた酸化
空気供給流路26を接続している。更に吸収塔5には、
液溜り部1内の吸収液2を撹拌する撹拌機7を設けてい
る。2. Description of the Related Art Conventionally, lime CaO (lime) has been used as an absorbent.
Flue gas desulfurization equipment using stone, slaked lime or quick lime is generally
As shown in FIG. 4, the liquid pool portion 1 formed in the lower portion
The absorption liquid 2 of the above is disposed on the upper part by the operation of the circulation pump 3.
When sprayed from the spray nozzle 4 and circulated,
Is externally supplied via the exhaust gas introduction duct 5a.
Absorption of the exhaust gas G sprayed from the spray nozzle 4
After contact with the liquid 2, through the exhaust gas discharge duct 5b
The absorption tower 5 for discharging is provided, and the liquid in the absorption tower 5
In the reservoir 1, lime CaO of the absorbing liquid 2 and sulfur in the exhaust gas G
Reactant CaSO with S ThreeTo oxidize CaSOFourStone
Oxidation with a compressor 6 supplying oxidizing air A for plaster oxidation
The air supply flow path 26 is connected. Furthermore, in the absorption tower 5,
A stirrer 7 for stirring the absorbing liquid 2 in the liquid reservoir 1 is provided.
You.
【0003】また、後述する母液タンク25から供給さ
れる吸収液23と、サイロ8から供給される石灰9を混
練して吸収剤スラリー10を生成し、且つ該吸収剤スラ
リー10を前記吸収塔5の液溜り部1に供給するための
吸収剤スラリーピット11を設けている。Further, an absorbent 23 supplied from a mother liquor tank 25 described later and lime 9 supplied from a silo 8 are kneaded to produce an absorbent slurry 10, and the absorbent slurry 10 is mixed with the absorbent tower 5. An absorbent slurry pit 11 for supplying the liquid to the liquid reservoir 1 is provided.
【0004】前記吸収塔5の液溜まり部1の吸収液2の
一部が供給され、且つ前記吸収塔5の液溜り部1へ供給
されるカセイソーダ等の中和剤12の一部が供給されて
前記吸収液2と中和剤12との混合撹拌を行う中和タン
ク13を設け、該中和タンク13にて抽出された吸収液
14を濃縮せしめるシックナ15を設け、該シックナ1
5で濃縮された吸収液16が供給され該吸収液16を撹
拌する脱水機供給タンク17を設け、該脱水機供給タン
ク17から抽出される吸収液16を脱水し石膏19を生
成するための脱水機20を設けている。Part of the absorbent 2 in the liquid reservoir 1 of the absorption tower 5 is supplied, and part of the neutralizer 12 such as caustic soda supplied to the liquid reservoir 1 of the absorption tower 5 is supplied. A neutralization tank 13 for mixing and stirring the absorbing liquid 2 and the neutralizing agent 12 is provided, and a thickener 15 for concentrating the absorbing liquid 14 extracted in the neutralizing tank 13 is provided.
A dehydrator supply tank 17 for supplying the absorbent 16 concentrated in 5 and stirring the absorbent 16 is provided, and the absorbent 16 extracted from the dehydrator supply tank 17 is dehydrated to produce gypsum 19. A machine 20 is provided.
【0005】一方、該脱水機20で脱水された水21が
供給され該水21の一部を前記シックナ15へ供給する
ための濾液ピット22を設け、更に、前記シックナ15
の上澄みの吸収液23が前記母液タンク25に供給さ
れ、該母液タンク25の吸収液23の一部を前記吸収塔
5の液溜り部1と、吸収剤スラリーピット11へ供給
し、且つ残りを排水処理装置24へ送るようにした構成
を有している。尚、図4中18は、吸収塔5へ適宜補給
される補給水である。On the other hand, a filtrate pit 22 for supplying the water 21 dehydrated by the dehydrator 20 to supply a part of the water 21 to the thickener 15 is further provided, and the thickener 15 is further provided.
The supernatant absorption liquid 23 is supplied to the mother liquor tank 25, a part of the absorption liquid 23 of the mother liquor tank 25 is supplied to the liquid reservoir 1 of the absorption tower 5 and the absorbent slurry pit 11, and the rest is supplied. It has a configuration in which it is sent to the wastewater treatment device 24. In addition, reference numeral 18 in FIG. 4 denotes makeup water that is appropriately supplemented to the absorption tower 5.
【0006】更に、前記排ガス導入ダクト5aには、硫
黄酸化物濃度を検出する入口SOx検出器27を設置す
ると共に、排ガスGの流量を計測する排ガス流量計28
を設置し、また、前記排ガス導出ダクト5bには出口S
Ox検出器29を設置し、前記入口SOx検出器27と出
口SOx検出器29の各SOx検出値30,31及び前記
排ガス流量計28からの排ガス流量検出値32を入力し
て脱硫負荷信号33を演算して出力する脱硫負荷演算器
34を設置し、該脱硫負荷演算器34からの脱硫負荷信
号33を入力して該脱硫負荷信号33に相応する負荷対
応空気流量指令信号35を出力する関数発生器36を設
置している。関数発生器36は、図5に示すように、脱
硫負荷信号33に対して例えば比例関係の負荷対応空気
流量指令信号35を出力するようになっている。Further, an inlet SOx detector 27 for detecting the concentration of sulfur oxides is installed in the exhaust gas introducing duct 5a, and an exhaust gas flow meter 28 for measuring the flow rate of the exhaust gas G.
And an outlet S is installed in the exhaust gas discharge duct 5b.
An Ox detector 29 is installed, and the SOx detection values 30 and 31 of the inlet SOx detector 27 and the outlet SOx detector 29 and the exhaust gas flow rate detection value 32 from the exhaust gas flow meter 28 are input to output a desulfurization load signal 33. A desulfurization load calculator 34 for calculating and outputting is installed, and a desulfurization load signal 33 from the desulfurization load calculator 34 is input to generate a function corresponding to a load-corresponding air flow rate command signal 35 corresponding to the desulfurization load signal 33. The vessel 36 is installed. As shown in FIG. 5, the function generator 36 outputs a load-corresponding air flow rate command signal 35 that is proportional to the desulfurization load signal 33, for example.
【0007】更に、前記負荷対応空気流量指令信号35
と、酸化空気供給流路26に設置した酸化空気流量検出
器37からの酸化空気流量検出値38とを入力し引算し
て差の信号39を出力する引算器40を設け、該引算器
40からの差の信号39を零にするように、例えば圧縮
機6の入口ベーン41の開度を調節する調節器42の調
節を行って液溜り部1に供給する酸化空気Aの流量が、
前記負荷対応空気流量指令信号35に一致するように制
御するPI調節器43を備えている。Further, the load-corresponding air flow rate command signal 35
And a subtraction unit 40 for inputting and subtracting the oxidation air flow rate detection value 38 from the oxidation air flow rate detector 37 installed in the oxidation air supply flow path 26 and outputting a difference signal 39. The flow rate of the oxidizing air A supplied to the liquid reservoir 1 is adjusted by adjusting the controller 42 that adjusts the opening degree of the inlet vane 41 of the compressor 6 so that the difference signal 39 from the container 40 becomes zero. ,
A PI adjuster 43 is provided to control so as to match the load-corresponding air flow rate command signal 35.
【0008】前述の如き排煙脱硫装置の場合、吸収液2
が循環ポンプ3の作動により循環しており、排ガス導入
ダクト5aから吸収塔5に送り込まれた排ガスGは、ス
プレーノズル4から噴霧される吸収液2と接触すること
により、硫黄酸化物が吸収除去された後、排ガス導出ダ
クト5bにより外部へ排出される。In the case of the flue gas desulfurization apparatus as described above, the absorbing liquid 2
Is circulated by the operation of the circulation pump 3, and the exhaust gas G sent from the exhaust gas introduction duct 5a to the absorption tower 5 comes into contact with the absorbing liquid 2 sprayed from the spray nozzle 4 to absorb and remove sulfur oxides. After being discharged, it is discharged to the outside by the exhaust gas discharge duct 5b.
【0009】一方、前記排ガスGから硫黄酸化物を吸収
した吸収液2の一部は、吸収塔5の液溜り部1の底部か
ら中和タンク13へ供給され、該中和タンク13におい
て中和剤12と混合撹拌され、該混合撹拌された吸収液
14がシックナ15へ送られ、該シックナ15において
濃縮され、該濃縮された吸収液16が脱水機供給タンク
17を経て脱水機20へ送られ、該脱水機20において
水分が除去され石膏19が生成される。On the other hand, a part of the absorption liquid 2 which has absorbed the sulfur oxides from the exhaust gas G is supplied to the neutralization tank 13 from the bottom of the liquid pool portion 1 of the absorption tower 5 and neutralized in the neutralization tank 13. The agent 12 is mixed and stirred, and the mixed and stirred absorption liquid 14 is sent to the thickener 15, concentrated in the thickener 15, and the concentrated absorption liquid 16 is sent to the dehydrator 20 via the dehydrator supply tank 17. The water is removed in the dehydrator 20 to produce the gypsum 19.
【0010】前記脱水機20で脱水された水21は、濾
液ピット22を経て前記シックナ15へ戻され、又、該
シックナ15における前記吸収液14の濃縮時に出る上
澄みの吸収液23は、母液タンク25を経て前記吸収塔
5の液溜り部1と吸収剤スラリーピット11へ供給され
ると共に、排水処理装置24へ送られる。The water 21 dehydrated by the dehydrator 20 is returned to the thickener 15 through the filtrate pit 22, and the supernatant absorbing liquid 23 that appears when the absorbing liquid 14 is concentrated in the thickener 15 is a mother liquor tank. It is supplied to the liquid reservoir 1 and the absorbent slurry pit 11 of the absorption tower 5 via 25 and is sent to the waste water treatment device 24.
【0011】前記吸収剤スラリーピット11へ供給され
た吸収液23は、該吸収剤スラリーピット11において
サイロ8から供給される石灰9と混練され、吸収剤スラ
リー10として前記吸収塔5の液溜り部1に供給され
る。The absorbent 23 supplied to the absorbent slurry pit 11 is kneaded with the lime 9 supplied from the silo 8 in the absorbent slurry pit 11 to form an absorbent slurry 10 in the liquid reservoir of the absorption tower 5. 1 is supplied.
【0012】排水処理装置24へ送られた吸収液23
は、該吸収液23中の窒素化合物の除去、化学的酸素要
求量CODの回復、及びその他の処理が行われるが、前
記窒素化合物の除去は、嫌気性バクテリアによる硝化菌
を用いて分解処理するようにしており、処理された排水
は外部に排出される。Absorbing liquid 23 sent to wastewater treatment device 24
Removes nitrogen compounds in the absorption liquid 23, recovers the chemical oxygen demand COD, and performs other treatments. The nitrogen compounds are removed by decomposing using nitrifying bacteria by anaerobic bacteria. The treated wastewater is discharged to the outside.
【0013】また、前記入口SOx検出器27及び出口
SOx検出器29の各SOx検出値30,31及び前記排
ガス流量計28からの排ガス流量検出値32を入力して
いる脱硫負荷演算器34が脱硫負荷信号33を演算し、
該脱硫負荷信号33が関数発生器36に出力されて負荷
対応空気流量指令信号35に変換される。該負荷対応空
気流量指令信号35は引算器40に入力されると共に、
該引算器40に酸化空気供給流路26に設置した酸化空
気流量検出器37からの酸化空気流量検出値38が入力
されることにより引算され、引算器40からの差の信号
39が零になるようにPI調節器43により調節器42
が調節されて、液溜り部1に供給される酸化空気Aの流
量が、前記負荷対応空気流量指令信号35に一致するよ
うに制御される。Further, the desulfurization load calculator 34 which inputs the respective SOx detection values 30 and 31 of the inlet SOx detector 27 and the outlet SOx detector 29 and the exhaust gas flow rate detected value 32 from the exhaust gas flow meter 28 is desulfurized. Calculate the load signal 33,
The desulfurization load signal 33 is output to the function generator 36 and converted into a load-corresponding air flow rate command signal 35. The load-corresponding air flow rate command signal 35 is input to the subtractor 40, and
The subtraction device 40 is subtracted by inputting the oxidation air flow rate detection value 38 from the oxidation air flow rate detector 37 installed in the oxidation air supply flow path 26, and a subtraction signal 39 from the subtraction device 40 is obtained. The PI controller 43 adjusts the controller 42 so that it becomes zero.
Is adjusted so that the flow rate of the oxidizing air A supplied to the liquid reservoir 1 is controlled to match the load-corresponding air flow rate command signal 35.
【0014】[0014]
【発明が解決しようとする課題】しかしながら、前述の
如き排煙脱硫装置では、圧縮機6から液溜り部1の吸収
液2へ供給される酸化空気Aの流量が、単に脱硫負荷信
号33に基づいた負荷対応空気流量指令信号35にて制
御されているために、SOx検出器27,29の検出誤
差、或いは排ガスGの性状の変化等によって供給される
酸化空気Aの量が多すぎる場合が発生し、このような場
合には、排ガスGと一緒に吸収された塩化物(HCl
等)が塩素(Cl2)のような物質に変化し、吸収液2
中に含まれる残留塩素等の酸化性物質の濃度が上昇し、
吸収液2の酸化還元電位が高まり、排水処理装置24の
硝化菌(バクテリア)の活性低下が引き起こされたり、
或いは硝化菌が死滅してしまい、排水処理装置24の機
能が大幅に低下してしまうという問題を有していた。However, in the flue gas desulfurization apparatus as described above, the flow rate of the oxidizing air A supplied from the compressor 6 to the absorbing liquid 2 of the liquid pool portion 1 is simply based on the desulfurization load signal 33. Since it is controlled by the load-corresponding air flow rate command signal 35, the amount of the oxidizing air A supplied may be too large due to a detection error of the SOx detectors 27 and 29, a change in the property of the exhaust gas G, or the like. However, in such a case, the chloride (HCl
Etc.) is changed to a substance such as chlorine (Cl 2 ) and the absorption liquid 2
The concentration of oxidizing substances such as residual chlorine contained in the
The redox potential of the absorption liquid 2 is increased, and the activity of nitrifying bacteria (bacteria) in the wastewater treatment device 24 is decreased,
Alternatively, there is a problem that the nitrifying bacteria are killed and the function of the wastewater treatment device 24 is significantly reduced.
【0015】本発明は、斯かる実情に鑑み、排水処理装
置の硝化菌の活性低下を防止し、排水処理装置の機能の
低下を防止し得る排煙脱硫装置の酸化空気供給方法及び
装置を提供しようとするものである。In view of the above situation, the present invention provides a method and an apparatus for supplying oxidant air to a flue gas desulfurization device, which can prevent the activity of nitrifying bacteria in the wastewater treatment device from decreasing and the function of the wastewater processing device from decreasing. Is what you are trying to do.
【0016】[0016]
【課題を解決するための手段】本発明の排煙脱硫装置の
酸化空気供給方法は、吸収剤として石灰を用いた吸収液
2と排ガスGとを接触せしめて排ガスG中の硫黄酸化物
を吸収除去する前記排ガスGと接触せしめた吸収液2に
調節器42を介して酸化空気Aを吹き込む酸化空気供給
流路26を備えた吸収塔5を設け、前記排ガスGと接触
せしめた吸収液2から石膏19を回収した後の吸収液2
に含まれる窒素化合物を分解するための排水処理装置2
4を設けた排煙脱硫装置の酸化空気供給方法であって、
吸収液2の酸化還元電位を検出し、酸化還元電位検出値
46が設定値47以上に増加した時に酸化空気Aの供給
量を減少するように前記調節器42を制御することを特
徴としている。The method for supplying oxidizing air to a flue gas desulfurization apparatus according to the present invention absorbs sulfur oxides in the exhaust gas G by bringing the absorbent 2 using lime as an absorbent and the exhaust gas G into contact with each other. The absorption tower 5 provided with the oxidizing air supply flow path 26 for blowing the oxidizing air A through the controller 42 to the absorbent 2 brought into contact with the exhaust gas G to be removed is provided, and from the absorbent 2 brought into contact with the exhaust gas G Absorbing liquid 2 after collecting gypsum 19
Wastewater treatment equipment 2 for decomposing nitrogen compounds contained in
A method for supplying oxidative air to a flue gas desulfurization apparatus provided with 4,
It is characterized in that the redox potential of the absorbing liquid 2 is detected, and the controller 42 is controlled so as to decrease the supply amount of the oxidizing air A when the redox potential detection value 46 increases above a set value 47.
【0017】本発明の排煙脱硫装置の酸化空気供給装置
は、吸収剤として石灰を用いた吸収液2と排ガスGとを
接触せしめて排ガスG中の硫黄酸化物を吸収除去する前
記排ガスGと接触せしめた吸収液2に調節器42を介し
て酸化空気Aを吹き込む酸化空気供給流路26を備えた
吸収塔5と、前記排ガスGと接触せしめた吸収液2から
石膏19を回収した後の吸収液2に含まれる窒素化合物
を分解するための排水処理装置24とを備えた排煙脱硫
装置の酸化空気供給装置であって、脱硫負荷信号33に
基づいて負荷対応空気流量指令信号35を出力する関数
発生器36と、吸収液2の酸化還元電位を検出する酸化
還元電位検出器45と、該酸化還元電位検出器45の酸
化還元電位検出値46と設定値47とを入力し引算によ
り差の信号48を出力する引算器49と、前記差の信号
48に基づいて前記酸化還元電位検出値46が設定値4
7より大きい時に酸化空気Aの流量を減らす酸化還元電
位対応空気流量指令信号50を出力するPI調節器56
と、前記負荷対応空気流量指令信号35と酸化還元電位
対応空気流量指令信号50を入力して小さい側の信号を
選択して出力する低信号選択器53と、該低信号選択器
53からの選択信号52と前記酸化空気供給流路26に
備えた酸化空気流量検出器37からの酸化空気流量検出
値38とを入力し引算して差の信号54を出力する引算
器55と、該引算器55からの差の信号54を零にする
ように前記調節器42の調節を行うPI調節器56とを
備えたことを特徴としている。The oxidizing air supply apparatus for the flue gas desulfurization apparatus of the present invention comprises the exhaust gas G for absorbing and removing the sulfur oxides in the exhaust gas G by bringing the absorbent 2 using lime as an absorbent and the exhaust gas G into contact with each other. After recovering the gypsum 19 from the absorption tower 5 provided with the oxidizing air supply flow path 26 for injecting the oxidizing air A into the contacted absorbent 2 through the controller 42, and the absorbent 2 contacted with the exhaust gas G An oxidizing air supply device for a flue gas desulfurization device, which comprises a wastewater treatment device 24 for decomposing nitrogen compounds contained in the absorbing liquid 2, and outputs a load-corresponding air flow rate command signal 35 based on a desulfurization load signal 33. Function generator 36, redox potential detector 45 for detecting the redox potential of absorbing liquid 2, redox potential detection value 46 and set value 47 of redox potential detector 45, and subtraction The difference signal 48 A subtracter 49 for force, the oxidation-reduction potential detected value 46 based on the signal 48 of the difference is a set value 4
A PI controller 56 that outputs an air flow rate command signal 50 corresponding to a redox potential that reduces the flow rate of the oxidizing air A when it is greater than 7.
A low signal selector 53 for inputting the load-corresponding air flow rate command signal 35 and the oxidation-reduction potential-corresponding air flow rate command signal 50 to select and output the smaller signal, and selection from the low signal selector 53 A subtracter 55 for inputting and subtracting the signal 52 and the oxidizing air flow rate detection value 38 from the oxidizing air flow rate detector 37 provided in the oxidizing air supply flow path 26 and outputting a difference signal 54, and the subtractor 55. And a PI controller 56 that adjusts the controller 42 so that the difference signal 54 from the calculator 55 becomes zero.
【0018】また、PI調節器51に、選択信号52に
所定の加算値57を加算した値によって酸化還元電位対
応空気流量指令信号50の上限を制限する振切り防止回
路58を備えていることを特徴としている。Further, the PI controller 51 is provided with a shake-off prevention circuit 58 for limiting the upper limit of the air flow rate command signal 50 corresponding to the oxidation-reduction potential by a value obtained by adding a predetermined addition value 57 to the selection signal 52. It has a feature.
【0019】ここで、調節器42は、圧縮機6の入口ベ
ーン41の開度を調節するものであっても、或いは酸化
空気供給流路26に備えた弁の開度を調節するものであ
ってもよい。Here, the controller 42 is for adjusting the opening of the inlet vane 41 of the compressor 6 or for adjusting the opening of the valve provided in the oxidizing air supply passage 26. May be.
【0020】上記手段では、吸収液2の酸化還元電位を
検出し、酸化還元電位検出値46が設定値47以上に増
加した時に酸化空気Aの供給量を減少するようにしてい
るので、吸収液2の酸化還元電位が設定値47以上に上
昇するのを防止して、排水処理装置24の硝化菌の活性
低下を防止し、排水処理装置24の機能の低下を防止す
ることができる。In the above means, the redox potential of the absorbing liquid 2 is detected, and when the redox potential detection value 46 increases above the set value 47, the supply amount of the oxidizing air A is decreased. It is possible to prevent the oxidation-reduction potential of No. 2 from rising above the set value 47, to prevent the activity of the nitrifying bacteria of the waste water treatment device 24 from decreasing, and to prevent the function of the waste water processing device 24 from decreasing.
【0021】また、酸化空気供給装置の制御回路44を
構成するPI調節器51に、選択信号52に所定の加算
値57を加算した値によって酸化還元電位対応空気流量
指令信号50の上限を制限する振切り防止回路58を備
えたことにより、酸化空気Aの流量を減少させる酸化還
元電位対応空気流量指令信号50が発せられた時に直ち
にその酸化還元電位対応空気流量指令信号50が低信号
選択器53により選択されるようにして、酸化空気Aの
流量の減少の作用を応答性よく行わせることができる。Further, the PI controller 51 constituting the control circuit 44 of the oxidizing air supply device limits the upper limit of the oxidation reduction potential corresponding air flow rate command signal 50 by a value obtained by adding a predetermined addition value 57 to the selection signal 52. Since the shake-off prevention circuit 58 is provided, when the redox potential corresponding air flow rate command signal 50 for reducing the flow rate of the oxidizing air A is issued, the redox potential corresponding air flow rate command signal 50 immediately outputs the low signal selector 53. As described above, the effect of reducing the flow rate of the oxidizing air A can be responsively performed.
【0022】[0022]
【発明の実施の形態】以下、本発明の実施の形態を、図
示例と共に説明する。BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below with reference to the drawings.
【0023】図1は、前記図4の従来の排煙脱硫装置に
適用した本発明の実施の形態の一例を示したもので、基
本的な構成は図4に示す従来のものと同様であるが、本
実施の形態において特徴とするところは、図1に示す制
御回路44を備えた点にある。FIG. 1 shows an example of an embodiment of the present invention applied to the conventional flue gas desulfurization apparatus shown in FIG. 4, and its basic construction is the same as that of the conventional apparatus shown in FIG. However, a feature of this embodiment is that the control circuit 44 shown in FIG. 1 is provided.
【0024】吸収塔5の液溜り部1に供給している酸化
空気Aの供給量を減少すると、排水処理装置24の硝化
菌に影響を及ぼす残留塩素濃度を低下させ得ることが本
願発明者等の実験により明らかとなり、又、残留塩素濃
度は酸化還元電位の変化要因であることから、吸収液2
の酸化還元電位を検出し、該酸化還元電位に応じて吸収
液2へ供給する酸化空気Aの量を増減させれば、排水処
理装置24の硝化菌の活性低下を防止できることが明ら
かとなった。The inventors of the present application can reduce the residual chlorine concentration affecting the nitrifying bacteria in the waste water treatment device 24 by reducing the supply amount of the oxidizing air A supplied to the liquid pool portion 1 of the absorption tower 5. It became clear by the experiment of 1., and the residual chlorine concentration is a factor of the change of the redox potential.
It was revealed that the activity reduction of the nitrifying bacteria in the wastewater treatment device 24 can be prevented by detecting the redox potential of No. 2 and increasing / decreasing the amount of the oxidizing air A supplied to the absorbing solution 2 according to the redox potential. .
【0025】このため、図1及び図2に示すように、吸
収塔5の液溜り部1の吸収液2或いは循環経路中の吸収
液2の酸化還元電位を検出する酸化還元電位検出器45
を設け、該酸化還元電位検出器45の酸化還元電位検出
値46と設定値47とを入力し引算して差の信号48を
出力する引算器49を設け、該引算器49からの差の信
号48に基づいて前記酸化還元電位検出値46が設定値
47より大きい時に空気流量を減らすように酸化還元電
位対応空気流量指令信号50を出力するPI調節器51
を設ける。Therefore, as shown in FIGS. 1 and 2, a redox potential detector 45 for detecting the redox potential of the absorption liquid 2 in the liquid reservoir 1 of the absorption tower 5 or the absorption liquid 2 in the circulation path.
Is provided, and a subtracter 49 for inputting and subtracting the redox potential detection value 46 and the set value 47 of the redox potential detector 45 to output a difference signal 48 is provided. Based on the difference signal 48, when the redox potential detection value 46 is larger than a set value 47, a PI controller 51 that outputs a redox potential corresponding air flow rate command signal 50 to reduce the air flow rate.
Is provided.
【0026】一方、図4と同様に、入口SOx検出器2
7のSOx検出値30と出口SOx検出器29のSOx検
出値31、及び排ガス流量計28からの排ガス流量検出
値32とを入力して脱硫負荷信号33を演算している脱
硫負荷演算器34からの脱硫負荷信号33が関数発生器
36に入力されて得られた負荷対応空気流量指令信号3
5と、前記酸化還元電位対応空気流量指令信号50とを
入力して小さい側の信号を選択して選択信号52として
出力する低信号選択器53を設ける。On the other hand, as in FIG. 4, the inlet SOx detector 2
From the desulfurization load calculator 34 which inputs the SOx detection value 30 of 7 and the SOx detection value 31 of the outlet SOx detector 29 and the exhaust gas flow rate detection value 32 from the exhaust gas flow meter 28 to calculate the desulfurization load signal 33. Load corresponding air flow rate command signal 3 obtained by inputting desulfurization load signal 33 of
5 and the air flow rate command signal 50 corresponding to the oxidation-reduction potential are input, a low signal selector 53 for selecting the signal on the smaller side and outputting it as the selection signal 52 is provided.
【0027】更に、低信号選択器53からの選択信号5
2と、酸化空気供給流路26に備えた酸化空気流量検出
器37からの酸化空気流量検出値38とを入力し引算し
て差の信号54を出力する引算器55を設けると共に、
該引算器55からの差の信号54を零にするように調節
器42の調節を行うPI調節器56を設ける。Further, the selection signal 5 from the low signal selector 53
2, and a subtractor 55 that inputs and subtracts the oxidizing air flow rate detection value 38 from the oxidizing air flow rate detector 37 provided in the oxidizing air supply flow path 26 and outputs a difference signal 54,
A PI adjuster 56 is provided which adjusts the adjuster 42 to zero the difference signal 54 from the subtractor 55.
【0028】次に、上記実施の形態例の作用について説
明する。Next, the operation of the above embodiment will be described.
【0029】脱硫負荷演算器34からの脱硫負荷信号3
3が関数発生器36に入力されて得られた負荷対応空気
流量指令信号35が低信号選択器53を介して引算器5
5に入力されると共に、酸化空気供給流路26に備えた
酸化空気流量検出器37からの酸化空気流量検出値38
が引算器55に入力されて引算されることにより差の信
号54が求められ、該差の信号54を零になるようにP
I調節器56によって調節器42の調節が行われて、液
溜り部1に供給される酸化空気Aの流量が、前記負荷対
応空気流量指令信号35に一致するよう制御される。Desulfurization load signal 3 from the desulfurization load calculator 34
3 is input to the function generator 36, and the load-corresponding air flow rate command signal 35 obtained through the low signal selector 53 is added to the subtracter 5
5 and the oxidizing air flow rate detection value 38 from the oxidizing air flow rate detector 37 provided in the oxidizing air supply flow path 26.
Is input to a subtractor 55 and subtracted to obtain a difference signal 54, and P is set so that the difference signal 54 becomes zero.
The I adjuster 56 adjusts the adjuster 42 so that the flow rate of the oxidizing air A supplied to the liquid reservoir 1 is controlled to match the load-corresponding air flow rate command signal 35.
【0030】一方、前記液溜り部1の吸収液2の酸化還
元電位が上昇してくると、その酸化還元電位を検出して
いる酸化還元電位検出器45の酸化還元電位検出値46
が上昇し、該酸化還元電位検出値46が設定値47より
大きくなると、該酸化還元電位検出値46が引算器49
のマイナス(−)側に入力されているので、差の信号4
8がマイナスの値となり、従ってPI調節器51はマイ
ナスの差の信号48を無くすように減らす方向の酸化還
元電位対応空気流量指令信号50を低信号選択器53に
出力することになり、前記負荷対応空気流量指令信号3
5に対して酸化還元電位対応空気流量指令信号50の方
が小さいことにより、酸化還元電位対応空気流量指令信
号50が選択されて選択信号52として引算器55に出
力されることにより、以後は酸化空気供給流路26の酸
化空気Aの流量が酸化還元電位対応空気流量指令信号5
0に一致するように低減される。On the other hand, when the redox potential of the absorbing liquid 2 in the liquid reservoir 1 rises, the redox potential detection value 46 of the redox potential detector 45 detecting the redox potential is detected.
Is increased and the redox potential detection value 46 becomes larger than the set value 47, the redox potential detection value 46 is subtracted from the subtracter 49.
Since it is input to the minus (-) side of, the difference signal 4
8 becomes a negative value, so that the PI controller 51 outputs to the low signal selector 53 the air flow rate command signal 50 corresponding to the redox potential in the direction of decreasing so as to eliminate the signal 48 of the negative difference. Corresponding air flow rate command signal 3
Since the air flow rate command signal 50 corresponding to the redox potential is smaller than that of 5, the air flow rate command signal 50 corresponding to the redox potential is selected and output to the subtractor 55 as the selection signal 52. The flow rate of the oxidizing air A in the oxidizing air supply channel 26 is the air flow rate command signal 5 corresponding to the redox potential.
Reduced to match zero.
【0031】また、酸化空気Aの流量が減少されて酸化
還元電位検出値46が設定値47より低くなると、差の
信号48がプラスの値となり、従ってPI調節器51は
プラスの差の信号48を無くすように増加する方向の酸
化還元電位対応空気流量指令信号50を低信号選択器5
3に出力することになり、これにより酸化還元電位対応
空気流量指令信号50が負荷対応空気流量指令信号35
より大きくなると、低信号選択器53は今度は負荷対応
空気流量指令信号35を選択して引算器55に出力する
ようになる。Further, when the flow rate of the oxidizing air A is decreased and the redox potential detection value 46 becomes lower than the set value 47, the difference signal 48 becomes a positive value, so that the PI controller 51 outputs a positive difference signal 48. The air flow rate command signal 50 corresponding to the redox potential in the increasing direction so as to eliminate
3 to output the air flow rate command signal 50 corresponding to the oxidation-reduction potential to the air flow rate command signal 35 corresponding to the load.
When it becomes larger, the low signal selector 53 in turn selects the load-corresponding air flow rate command signal 35 and outputs it to the subtractor 55.
【0032】従って、通常時は負荷対応空気流量指令信
号35によって酸化空気Aの流量を制御し、酸化還元電
位検出値46が設定値47を越えた場合には酸化空気A
の流量を絞る酸化還元電位対応空気流量指令信号50に
より制御し、それによって液溜り部1の吸収液2の酸化
還元電位が所定値以上に上昇することを防止して、排水
処理装置24の硝化菌の活性が低下するのを防止するこ
とができる。Therefore, normally, the flow rate of the oxidizing air A is controlled by the load-corresponding air flow rate command signal 35, and when the oxidation reduction potential detection value 46 exceeds the set value 47, the oxidizing air A is detected.
Is controlled by the air flow rate command signal 50 corresponding to the oxidation-reduction potential, which prevents the oxidation-reduction potential of the absorbing liquid 2 in the liquid reservoir 1 from rising above a predetermined value, and nitrification of the wastewater treatment device 24. It is possible to prevent the activity of the bacterium from decreasing.
【0033】また、前記PI調節器51に、低信号選択
器53からの選択信号52に所定の加算値57(例えば
数パーセント)を加算した値によって酸化還元電位対応
空気流量指令信号50の上限を制限する振切り防止回路
58(リセット−ワインドアップ防止回路)を設けてい
る。In addition, the upper limit of the air flow rate command signal 50 corresponding to the oxidation-reduction potential is set to the PI controller 51 by a value obtained by adding a predetermined addition value 57 (for example, several percent) to the selection signal 52 from the low signal selector 53. A shake-off prevention circuit 58 (reset-windup prevention circuit) for limiting is provided.
【0034】前記PI調節器51は、引算器49からの
差の信号48を無くすように、図3に示すように0%か
ら100%の間で増加したり減少したりする酸化還元電
位対応空気流量指令信号50を低信号選択器53に出力
するものである。即ち、例えば前記関数発生器36から
の負荷対応空気流量指令信号35が例えば50%である
とした時に、酸化還元電位対応空気流量指令信号50が
0%から徐々に増加して行く場合(差の信号48がプラ
スの場合)についてみると、低信号選択器53はこの小
さい酸化還元電位対応空気流量指令信号50を選択して
酸化空気Aの流量を増加し、酸化還元電位対応空気流量
指令信号50が50%を越えると、前記負荷対応空気流
量指令信号35の方が小さくなるので該負荷対応空気流
量指令信号35が選択されるように切り替る。この時、
前記酸化還元電位対応空気流量指令信号50は更に増加
し続け、ついには破線50’で示すように100%に達
してしまう。The PI regulator 51 corresponds to the redox potential which increases or decreases between 0% and 100% as shown in FIG. 3 so as to eliminate the difference signal 48 from the subtractor 49. The air flow rate command signal 50 is output to the low signal selector 53. That is, when the load-corresponding air flow rate command signal 35 from the function generator 36 is, for example, 50%, the redox potential-corresponding air flow rate command signal 50 gradually increases from 0% (the difference (When the signal 48 is positive), the low signal selector 53 selects the small redox potential corresponding air flow rate command signal 50 to increase the flow rate of the oxidizing air A, and the redox potential corresponding air flow rate command signal 50. Exceeds 50%, the load-corresponding air flow rate command signal 35 becomes smaller, so that the load-corresponding air flow rate command signal 35 is switched to be selected. This time,
The air flow rate command signal 50 corresponding to the oxidation-reduction potential continues to increase and finally reaches 100% as shown by the broken line 50 '.
【0035】一方、液溜り部1の酸化還元電位が設定値
47より大きくなって差の信号48がマイナスになる
と、PI調節器51は100%の状態から点Bより減少
方向の酸化還元電位対応空気流量指令信号50を出力す
るようになるが、該酸化還元電位対応空気流量指令信号
50が50%まで減少するまでには時間が掛かり、この
間は負荷対応空気流量指令信号35が低信号選択器53
で選択され続け、そのために酸化還元電位対応空気流量
指令信号50が選択されて実際に液溜り部1に供給され
る酸化空気Aの流量が減少されるまでには大きな時間遅
れHを生じてしまう問題がある。On the other hand, when the redox potential of the liquid reservoir 1 becomes larger than the set value 47 and the difference signal 48 becomes negative, the PI controller 51 responds to the redox potential in the decreasing direction from the point B at 100%. Although the air flow rate command signal 50 is output, it takes time for the air flow rate command signal 50 corresponding to the oxidation-reduction potential to decrease to 50%, and during this period, the load-corresponding air flow rate command signal 35 is the low signal selector. 53
Therefore, a large time delay H occurs until the air flow rate command signal 50 corresponding to the redox potential is selected and the flow rate of the oxidizing air A actually supplied to the liquid reservoir 1 is reduced. There's a problem.
【0036】このために、前記PI調節器51に振切り
防止回路58を備えて、選択信号52の出力に所定の加
算値57(数パーセント)を加算するようにし、例え
ば、50%+数パーセント(例えば3%)=53%を上
限として設定するようになっているので、例えば図3に
示すようにPI調節器の酸化還元電位対応空気流量指令
信号50が増加して53%に達すると、それ以上に上昇
することなくその値を保持するようになり、従ってPI
調節器51の酸化還元電位対応空気流量指令信号50が
減少する信号が出力された場合には、前記53%の値か
ら直ちに減少するようになって時間の遅れをH’のよう
に極力小さくすることができる。For this purpose, the PI adjuster 51 is provided with a swing-out prevention circuit 58 so that a predetermined addition value 57 (several percent) is added to the output of the selection signal 52, for example, 50% + several percent. Since the upper limit is set to (for example, 3%) = 53%, for example, as shown in FIG. 3, when the air flow rate command signal 50 corresponding to the redox potential of the PI controller increases and reaches 53%, It will keep its value without going up further, so PI
When a signal for reducing the air flow rate command signal 50 corresponding to the redox potential of the controller 51 is output, the air flow rate command signal 50 decreases immediately from the value of 53%, and the time delay is minimized to H '. be able to.
【0037】[0037]
【発明の効果】以上説明したように、本発明の排煙脱硫
装置の酸化空気供給方法及び装置によれば、吸収液2の
酸化還元電位を検出し、酸化還元電位検出値46が設定
値47以上に増加した時に酸化空気Aの供給量を減少す
るようにしているので、吸収液2の酸化還元電位が設定
値47以上に上昇するのを防止して、排水処理装置24
の硝化菌の活性低下を防止し、排水処理装置24の機能
の低下を防止することができる。As described above, according to the oxidizing air supply method and device of the flue gas desulfurization apparatus of the present invention, the redox potential of the absorbing liquid 2 is detected, and the redox potential detection value 46 is the set value 47. Since the supply amount of the oxidizing air A is decreased when the amount is increased above, the oxidation-reduction potential of the absorbing liquid 2 is prevented from rising above the set value 47, and the wastewater treatment device 24
It is possible to prevent a decrease in the activity of the nitrifying bacteria and prevent a decrease in the function of the wastewater treatment device 24.
【0038】また、酸化空気供給装置の制御回路44を
構成するPI調節器51に、選択信号52に所定の加算
値57を加算した値によって酸化還元電位対応空気流量
指令信号50の上限を制限する振切り防止回路58を備
えたことにより、酸化空気Aの流量を減少させる酸化還
元電位対応空気流量指令信号50が発せられた時に直ち
にその酸化還元電位対応空気流量指令信号50が低信号
選択器53により選択されるようにして、酸化空気Aの
流量を減少させる作用を応答性よく行わせることができ
る。Further, the PI controller 51 constituting the control circuit 44 of the oxidizing air supply device limits the upper limit of the air flow rate command signal 50 corresponding to the oxidation reduction potential by the value obtained by adding the predetermined addition value 57 to the selection signal 52. Since the shake-off prevention circuit 58 is provided, when the redox potential corresponding air flow rate command signal 50 for reducing the flow rate of the oxidizing air A is issued, the redox potential corresponding air flow rate command signal 50 immediately outputs the low signal selector 53. Thus, the action of reducing the flow rate of the oxidizing air A can be performed with good responsiveness.
【図1】本発明の実施の形態例を示す概要図である。FIG. 1 is a schematic diagram showing an embodiment of the present invention.
【図2】制御回路の構成を示すブロック図である。FIG. 2 is a block diagram showing a configuration of a control circuit.
【図3】振切り防止回路による酸化還元電位対応空気流
量指令信号の変化を表わす線図である。FIG. 3 is a diagram showing a change in an air flow rate command signal corresponding to a redox potential by a shake-off prevention circuit.
【図4】従来例の概要図である。FIG. 4 is a schematic diagram of a conventional example.
【図5】関数発生器の脱硫負荷信号と負荷対応空気流量
指令信号との関係を示す線図である。FIG. 5 is a diagram showing a relationship between a desulfurization load signal of a function generator and a load-corresponding air flow rate command signal.
2 吸収液 5 吸収塔 19 石膏 24 排水処理装置 26 酸化空気供給流路 33 脱硫負荷信号 35 負荷対応空気流量指令信号 36 関数発生器 37 酸化空気流量検出器 38 酸化空気流量検出値 42 調節器 45 酸化還元電位検出器 46 酸化還元電位検出値 47 設定値 48 差の信号 49 引算器 50 酸化還元電位対応空気流量指令信号 51 PI調節器 52 選択信号 53 低信号選択器 54 差の信号 55 引算器 56 PI調節器 57 加算値 58 振切り防止回路 A 酸化空気 G 排ガス 2 Absorbing liquid 5 Absorption tower 19 Gypsum 24 Waste water treatment device 26 Oxidizing air supply flow path 33 Desulfurization load signal 35 Load corresponding air flow rate command signal 36 Function generator 37 Oxidizing air flow rate detector 38 Oxidizing air flow rate detection value 42 Regulator 45 Oxidation Reduction potential detector 46 Oxidation reduction potential detection value 47 Set value 48 Difference signal 49 Subtractor 50 Redox potential corresponding air flow rate command signal 51 PI controller 52 Selection signal 53 Low signal selector 54 Difference signal 55 Subtraction device 56 PI controller 57 Addition value 58 Shake-off prevention circuit A Oxidizing air G Exhaust gas
Claims (3)
と排ガス(G)とを接触せしめて排ガス(G)中の硫黄
酸化物を吸収除去する前記排ガス(G)と接触せしめた
吸収液(2)に調節器(42)を介して酸化空気(A)
を吹き込む酸化空気供給流路(26)を備えた吸収塔
(5)を設け、前記排ガス(G)と接触せしめた吸収液
(2)から石膏(19)を回収した後の吸収液(2)に
含まれる窒素化合物を分解するための排水処理装置(2
4)を設けた排煙脱硫装置の酸化空気供給方法であっ
て、吸収液(2)の酸化還元電位を検出し、酸化還元電
位検出値(46)が設定値(47)以上に増加した時に
酸化空気(A)の供給量を減少するように前記調節器
(42)を制御することを特徴とする排煙脱硫装置の酸
化空気供給方法。1. An absorbing liquid using lime as an absorbent (2)
And the exhaust gas (G) are brought into contact with each other to absorb and remove the sulfur oxides in the exhaust gas (G). The absorbing liquid (2) brought into contact with the exhaust gas (G) is oxidized with air (A) through the controller (42). )
The absorption liquid (2) after recovering the gypsum (19) from the absorption liquid (2) brought into contact with the exhaust gas (G) by providing the absorption tower (5) provided with the oxidizing air supply flow path (26) for blowing in Wastewater treatment equipment for decomposing nitrogen compounds contained in
4) A method for supplying oxidizing air to a flue gas desulfurization apparatus, wherein when the redox potential of the absorbing liquid (2) is detected and the redox potential detection value (46) increases above a set value (47). A method for supplying oxidizing air to a flue gas desulfurization device, characterized in that the controller (42) is controlled so as to reduce the supply amount of oxidizing air (A).
と排ガス(G)とを接触せしめて排ガス(G)中の硫黄
酸化物を吸収除去する前記排ガス(G)と接触せしめた
吸収液(2)に調節器(42)を介して酸化空気(A)
を吹き込む酸化空気供給流路(26)を備えた吸収塔
(5)と、前記排ガス(G)と接触せしめた吸収液
(2)から石膏(19)を回収した後の吸収液(2)に
含まれる窒素化合物を分解するための排水処理装置(2
4)とを備えた排煙脱硫装置の酸化空気供給装置であっ
て、脱硫負荷信号(33)に基づいて負荷対応空気流量
指令信号(35)を出力する関数発生器(36)と、吸
収液(2)の酸化還元電位を検出する酸化還元電位検出
器(45)と、該酸化還元電位検出器(45)の酸化還
元電位検出値(46)と設定値(47)とを入力し引算
により差の信号(48)を出力する引算器(49)と、
前記差の信号(48)に基づいて前記酸化還元電位検出
値(46)が設定値(47)より大きい時に酸化空気
(A)の流量を減らす酸化還元電位対応空気流量指令信
号(50)を出力するPI調節器(56)と、前記負荷
対応空気流量指令信号(35)と酸化還元電位対応空気
流量指令信号(50)を入力して小さい側の信号を選択
して出力する低信号選択器(53)と、該低信号選択器
(53)からの選択信号(52)と前記酸化空気供給流
路(26)に備えた酸化空気流量検出器(37)からの
酸化空気流量検出値(38)とを入力し引算して差の信
号(54)を出力する引算器(55)と、該引算器(5
5)からの差の信号(54)を零にするように前記調節
器(42)の調節を行うPI調節器(56)とを備えた
ことを特徴とする排煙脱硫装置の酸化空気供給装置。2. An absorbing liquid using lime as an absorbing agent (2)
And the exhaust gas (G) are brought into contact with each other to absorb and remove the sulfur oxides in the exhaust gas (G). The absorbing liquid (2) brought into contact with the exhaust gas (G) is oxidized with air (A) through the controller (42). )
The absorption tower (5) provided with an oxidizing air supply flow path (26) for blowing the gas into the absorption liquid (2) after recovering the gypsum (19) from the absorption liquid (2) brought into contact with the exhaust gas (G). Wastewater treatment equipment for decomposing nitrogen compounds contained (2
And a function generator (36) for outputting a load-corresponding air flow rate command signal (35) based on a desulfurization load signal (33), and an absorbing liquid. The redox potential detector (45) for detecting the redox potential of (2), the redox potential detection value (46) and the set value (47) of the redox potential detector (45) are input and subtracted. A subtractor (49) that outputs a difference signal (48) by
An air flow rate corresponding air flow rate command signal (50) for reducing the flow rate of oxidizing air (A) is output when the redox potential detection value (46) is larger than a set value (47) based on the difference signal (48). And a low signal selector (56) that inputs the load-corresponding air flow rate command signal (35) and the oxidation-reduction potential-corresponding air flow rate command signal (50) and selects and outputs the smaller signal ( 53), the selection signal (52) from the low signal selector (53), and the oxidizing air flow rate detection value (38) from the oxidizing air flow rate detector (37) provided in the oxidizing air supply flow path (26). And a subtracter (55) that subtracts and outputs a difference signal (54), and the subtractor (5)
And a PI controller (56) for adjusting the controller (42) so that the signal (54) of the difference from (5) becomes zero. .
2)に所定の加算値(57)を加算した値によって酸化
還元電位対応空気流量指令信号(50)の上限を制限す
る振切り防止回路(58)を備えていることを特徴とす
る排煙脱硫装置の酸化空気供給装置。3. A PI controller (51) is provided with a selection signal (5).
2) A flue gas desulfurization characterized by comprising a shake-off prevention circuit (58) for limiting the upper limit of the redox potential corresponding air flow rate command signal (50) by a value obtained by adding a predetermined addition value (57) Oxidizing air supply device of equipment.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7194863A JPH0938454A (en) | 1995-07-31 | 1995-07-31 | Method and apparatus for supplying oxidizing air to flue gas desulfurization apparatus |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7194863A JPH0938454A (en) | 1995-07-31 | 1995-07-31 | Method and apparatus for supplying oxidizing air to flue gas desulfurization apparatus |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0938454A true JPH0938454A (en) | 1997-02-10 |
Family
ID=16331556
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP7194863A Pending JPH0938454A (en) | 1995-07-31 | 1995-07-31 | Method and apparatus for supplying oxidizing air to flue gas desulfurization apparatus |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0938454A (en) |
-
1995
- 1995-07-31 JP JP7194863A patent/JPH0938454A/en active Pending
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