JP3190938B2 - Flue gas desulfurization equipment - Google Patents
Flue gas desulfurization equipmentInfo
- Publication number
- JP3190938B2 JP3190938B2 JP09387791A JP9387791A JP3190938B2 JP 3190938 B2 JP3190938 B2 JP 3190938B2 JP 09387791 A JP09387791 A JP 09387791A JP 9387791 A JP9387791 A JP 9387791A JP 3190938 B2 JP3190938 B2 JP 3190938B2
- Authority
- JP
- Japan
- Prior art keywords
- power plant
- desulfurization
- load
- concentration
- flue gas
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 238000006477 desulfuration reaction Methods 0.000 title claims description 39
- 230000023556 desulfurization Effects 0.000 title claims description 39
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims description 12
- 239000003546 flue gas Substances 0.000 title claims description 12
- 238000010521 absorption reaction Methods 0.000 claims description 34
- 239000007789 gas Substances 0.000 claims description 18
- 230000002159 abnormal effect Effects 0.000 claims description 13
- 235000019738 Limestone Nutrition 0.000 claims description 12
- 230000007613 environmental effect Effects 0.000 claims description 12
- 239000006028 limestone Substances 0.000 claims description 12
- 239000002002 slurry Substances 0.000 claims description 12
- 239000000446 fuel Substances 0.000 claims description 11
- 239000007788 liquid Substances 0.000 claims description 11
- 238000000034 method Methods 0.000 claims description 8
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 claims description 3
- 229910052815 sulfur oxide Inorganic materials 0.000 claims description 3
- 238000002485 combustion reaction Methods 0.000 claims description 2
- 230000001590 oxidative effect Effects 0.000 claims description 2
- 230000005856 abnormality Effects 0.000 description 7
- 238000004364 calculation method Methods 0.000 description 6
- 239000010440 gypsum Substances 0.000 description 5
- 229910052602 gypsum Inorganic materials 0.000 description 5
- 238000010248 power generation Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 238000003915 air pollution Methods 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000000779 smoke Substances 0.000 description 2
- 230000002745 absorbent Effects 0.000 description 1
- 239000002250 absorbent Substances 0.000 description 1
- LVGQIQHJMRUCRM-UHFFFAOYSA-L calcium bisulfite Chemical compound [Ca+2].OS([O-])=O.OS([O-])=O LVGQIQHJMRUCRM-UHFFFAOYSA-L 0.000 description 1
- 235000010260 calcium hydrogen sulphite Nutrition 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 238000013500 data storage Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000002803 fossil fuel Substances 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 239000003595 mist Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は排煙脱硫装置に係わり、
特に装置の異常時においても環境規制値を満足する運転
条件を与えるのに好適な計算機システムを備えた排煙脱
硫装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a flue gas desulfurization device,
In particular, the present invention relates to a flue gas desulfurization apparatus provided with a computer system suitable for providing operating conditions satisfying environmental regulation values even when the apparatus is abnormal.
【0002】[0002]
【従来の技術】近年、発電所が増大するのにつれて化石
燃料を主燃料とするボイラも大型化し、発電用ボイラが
大気汚染に与える影響も増加しつつある。この大気汚染
を拡大する公害物質の内、多大な影響を占める硫黄酸化
物(以下SOxまたはSO2と略す。)の排出規制は年々
厳しくなる傾向にある。特に近年、火力発電プラントの
中での設置比率が上昇している石炭火力プラントにおい
ては、排煙脱硫装置が全ての新設プラントに設置されて
いる。従ってその運用面においても脱硫装置の運転は発
電プラントの運転に不可欠であり、脱硫装置の異常によ
り、排出SOX濃度、煤塵濃度が規制値を超える場合に
は、発電プラントの運転もできなくなる。2. Description of the Related Art In recent years, as power plants have increased, the size of boilers using fossil fuel as a main fuel has also increased, and the effect of power generation boilers on air pollution has been increasing. Among pollutants to expand this air pollution, sulfur oxides occupying a great influence (hereinafter abbreviated as SO x or SO 2.) Emissions regulations are in strict tends year by year. In particular, in a coal-fired power plant in which the installation ratio among thermal power plants has been increasing in recent years, flue gas desulfurization apparatuses are installed in all new plants. Therefore, the operation of the desulfurization device is indispensable for the operation of the power plant also in terms of its operation, and if the exhausted SO X concentration or the dust concentration exceeds the regulation values due to the abnormality of the desulfurization device, the operation of the power plant cannot be performed.
【0003】しかしながら、一方において最近の急速な
国内電力需要量の伸びにより、供給量の余裕が減少し、
特に夏期の電力ピーク時においては供給の余裕がほとん
どなく、大型発電プラント一基の停止は、停電と言う最
悪事態を招くことになる場合もある。このため、排煙脱
硫装置の運用において、その運転状態の異常時において
も発電プラントの最適運転を目指す必要が生じてきた。However, on the other hand, the recent rapid growth of domestic power demand has reduced the margin of supply,
In particular, there is almost no margin for supply during the peak power season in the summer season, and shutting down one large power plant may lead to the worst case of blackout. For this reason, in the operation of the flue gas desulfurization device, it has become necessary to aim at the optimal operation of the power plant even when the operation state is abnormal.
【0004】以下図面を用いて従来技術の問題点を説明
する。火力発電所に設置される排煙脱硫装置は石灰石
(CaCO3)を吸収剤とした吸収スラリを用い、排ガ
スとの気液接触によりSOxを吸収し、さらに吸収反応
生成物を空気により酸化し、石膏として回収する湿式石
灰石−石膏法が主流である。この方式の系統図を図2に
示す。ボイラからの排ガスは脱硫ファン1より排ガス煙
道2を介して吸収塔3内に導入され、吸収液スラリと吸
収塔3内で気液接触により排ガス中に含まれるSOx、
煤塵が除去される。清浄化された処理ガスはデミスタ5
で同伴ミストが除去された後、煙道4により大気へ排出
される。[0004] Problems of the prior art will be described below with reference to the drawings. The flue gas desulfurization unit installed in the thermal power plant uses an absorption slurry containing limestone (CaCO 3 ) as an absorbent, absorbs SO x by gas-liquid contact with exhaust gas, and oxidizes the absorption reaction product with air. The wet limestone-gypsum method recovered as gypsum is the mainstream. FIG. 2 shows a system diagram of this system. The exhaust gas from the boiler is introduced into the absorption tower 3 from the desulfurization fan 1 via the exhaust gas flue 2, and SO x contained in the exhaust gas by gas-liquid contact in the absorption liquid slurry and the absorption tower 3.
Dust is removed. Cleaned processing gas is demister 5
After the accompanying mist is removed in the above, the air is discharged to the atmosphere by the flue 4.
【0005】一方、吸収塔循環タンク6内の石灰石を含
んだ吸収スラリは吸収塔循環ポンプ7により循環され、
吸収塔3の上部から吸収塔3内にスプレされる。吸収に
必要な石灰石は石灰石スラリとして石灰石スラリ槽8に
貯えられ、石灰石スラリポンプ9により昇圧され石灰石
スラリ配管10を経て吸収塔循環タンク6に供給され
る。一方、吸収塔3内で吸収されたSO2は石灰石と反
応し、重亜硫酸カルシウムとなり、吸収塔循環タンク6
内で該タンク6に吹き込まれる空気11により酸化され
石膏となる。この石膏スラリは吸収塔3から導管12に
より抜き出された後、脱水され最終的に粉末の石膏とし
て回収される。On the other hand, the absorption slurry containing limestone in the absorption tower circulation tank 6 is circulated by the absorption tower circulation pump 7,
It is sprayed into the absorption tower 3 from the upper part of the absorption tower 3. Limestone required for absorption is stored as a limestone slurry in a limestone slurry tank 8, pressurized by a limestone slurry pump 9, and supplied to an absorption tower circulation tank 6 via a limestone slurry pipe 10. On the other hand, SO 2 absorbed in the absorption tower 3 reacts with limestone to form calcium bisulfite, and the absorption tower circulation tank 6
Inside, it is oxidized by the air 11 blown into the tank 6 to form gypsum. This gypsum slurry is extracted from the absorption tower 3 by the conduit 12, then dehydrated and finally recovered as powdered gypsum.
【0006】以上のような系統において脱硫装置に流入
する排ガス量およびSO2濃度がそれぞれ流量計13と
入口SO2濃度計14で計測される。また出口SO2濃度
が出口SO2濃度計15により計測される。この脱硫装
置出口(煙突入口)のSO2濃度が環境規制値を超えな
いように脱硫装置を運転する必要がある。In the above system, the amount of exhaust gas flowing into the desulfurizer and the SO 2 concentration are measured by the flow meter 13 and the inlet SO 2 concentration meter 14, respectively. The outlet SO 2 concentration is measured by the outlet SO 2 concentration meter 15. The SO 2 concentration in the desulfurization apparatus outlet (chimney inlet) needs to operate the desulfurizer so as not to exceed the environmental regulation value.
【0007】[0007]
【発明が解決しようとする課題】前記したシステムにお
いて、従来技術では脱硫装置の補機の異常等により性能
が低下した場合の発電プラントの運転制御に対する考慮
がなされておらず、装置の異常時にも発電プラントの運
転を継続した場合、出口SO2濃度が環境規制値を超え
ることになる。また、発電プラントを停止する場合、上
述したように電力安定供給の面から社会的にも大きな影
響を及ぼすことになる。In the above-mentioned system, no consideration is given in the prior art to the operation control of the power plant when the performance is deteriorated due to an abnormality in the auxiliary equipment of the desulfurization apparatus. When the operation of the power plant is continued, the outlet SO 2 concentration exceeds the environmental regulation value. In addition, when the power plant is stopped, there is a great social impact from the viewpoint of stable power supply as described above.
【0008】そこで、本発明の目的は脱硫装置の補機の
異常等により性能が低下した場合の発電プラントの運転
制御を可能にした脱硫装置を提供することである。SUMMARY OF THE INVENTION It is an object of the present invention to provide a desulfurization apparatus capable of controlling the operation of a power plant when the performance of the desulfurization apparatus deteriorates due to an abnormality in an auxiliary machine or the like.
【0009】[0009]
【課題を解決するための手段】本発明の上記目的は次の
構成により達成される。すなわち、ボイラなどの燃焼装
置から排出される排ガス中の硫黄酸化物を除去する排煙
脱硫装置において、脱硫装置の性能に関連する排ガス
量、入口SO2濃度、出口SO2濃度、吸収液pH、石灰
石スラリ量、吸収塔循環液量、酸化空気量等のプロセス
量から発電機出力、燃料切り替え等の発電プラント負荷
に応じた脱硫性能を予測する脱硫性能予測手段と、該脱
硫性能予測手段の予測値と予め設定されている環境規制
値と比較して環境規制値に基づき許容される発電プラン
トの最適負荷を設定する発電プラント最適負荷設定手段
と、該発電プラント最適負荷設定手段の設定値に基づき
発電プラントの負荷出力制御を行う発電プラント負荷出
力制御手段とを設けた排煙脱硫装置である。The above object of the present invention is achieved by the following constitution. That is, in the flue gas desulfurization apparatus for removing sulfur oxides in an exhaust gas discharged from the combustion device such as a boiler, the exhaust gas quantity relating to the performance of the desulfurization apparatus, inlet SO 2 concentration, the outlet SO 2 concentration, the absorption solution pH, A desulfurization performance prediction means for predicting a desulfurization performance according to a power generation plant load such as a generator output and a fuel switch from a process amount such as a limestone slurry amount, an absorption tower circulating liquid amount and an oxidizing air amount, and a prediction by the desulfurization performance prediction means Power plant optimum load setting means for setting an optimum load of the power plant that is allowed based on the environmental regulation value by comparing the value with a preset environmental regulation value, based on the set value of the power plant optimum load setting means. This is a flue gas desulfurization device provided with a power plant load output control means for controlling the load output of the power plant.
【0010】ここで脱硫装置出口SO2濃度を支配する
要因としては、排ガス量、入口SO2濃度、吸収塔循環
液量、吸収塔pHがあり、排ガス量が少ない程、入口S
O2濃度が少ない程、吸収塔循環液量が多い程、また吸
収塔pHが高い程、吸収塔3での性能が向上し、出口S
O2濃度を低くできる。The factors controlling the SO 2 concentration at the outlet of the desulfurizer are the exhaust gas amount, the SO 2 concentration at the inlet, the amount of the circulating liquid in the absorption tower, and the pH of the absorption tower.
The lower the O 2 concentration, the larger the amount of circulating liquid in the absorption tower, and the higher the pH of the absorption tower, the more the performance in the absorption tower 3 is improved.
O 2 concentration can be reduced.
【0011】[0011]
【作用】脱硫装置の性能に関連する排ガス量、入口SO
2濃度、出口SO2濃度、吸収液pH、石灰石スラリ量、
吸収塔循環液量、酸化空気量等のプロセス量から発電機
出力、燃料切り替え等の発電プラント負荷に応じた脱硫
性能を予測し、この予測値と予め設定されている環境規
制値と比較して環境規制値に基づき許容される発電プラ
ントの最適負荷を設定する。このプラント最適負荷設定
値に基づき発電プラントの負荷出力制御を行う。[Action] Exhaust gas volume related to desulfurization unit performance, inlet SO
2 concentration, outlet SO 2 concentration, absorbing solution pH, limestone slurry amount,
The desulfurization performance according to the power plant load such as generator output and fuel switching is predicted from the process amount such as the amount of circulating liquid in the absorption tower and the amount of oxidized air, and this predicted value is compared with a preset environmental regulation value. Set the optimum load of the power plant that is allowed based on the environmental regulation value. The load output of the power plant is controlled based on the plant optimum load set value.
【0012】そして、前記プロセス量の異常時にも前記
制御システムが作動するため、その異常条件下での各負
荷の脱硫性能を予測し、それによって各負荷での出口S
O2濃度を予測することができる。この出口SO2濃度の
予測値が環境規制値を満足できる発電プラント負荷を設
定、制御できることになるので、環境規制値を超えた運
転や、発電プラントの全停止をすることがない。Since the control system operates even when the process amount is abnormal, the desulfurization performance of each load under the abnormal condition is predicted, whereby the outlet S at each load is estimated.
O 2 can be predicted concentrations. Since the power generation plant load at which the predicted value of the outlet SO 2 concentration satisfies the environmental regulation value can be set and controlled, the operation exceeding the environmental regulation value and the power plant not being stopped completely are not performed.
【0013】[0013]
【実施例】本発明になる演算装置の構成を図1に示す。
本実施例では4つの演算部と予測計算に必要なデータ部
から構成される。FIG. 1 shows the configuration of an arithmetic unit according to the present invention.
In this embodiment, it is composed of four operation units and a data unit necessary for prediction calculation.
【0014】まず、第1の演算部(現状性能チェック手
段)21では連続的に計測される各プラント量から脱硫
性能計算を行い、次のような手順で係数kを求める。 η=100×{(SO2)1−(SO2)2}/(SO2)1 (1) η:脱硫率 (SO2)1:SO2濃度計14で測定される入口SO2濃度(ppm) (SO2)2:SO2濃度計15で測定される出口SO2濃度(ppm) η=k×f1{(SO2)1}・f2(L)・f3(G)・f4(pH) (2) L:吸収塔循環液量(m3/h) G:ガス量(m3/h) pH:吸収塔pH k=η/[f1{(SO2)1}・f2(L)・f3(G)・f4(pH)] (3) 係数kは設計数値として設定されているが(3)式によ
り各運転時におけるkを逆算し、各運転状態におけるk
を用いて、次の性能予測計算を行うことにより精度の高
い計算が可能となる。First, the first computing section (current performance checking means) 21 calculates the desulfurization performance from the continuously measured plant quantities, and obtains the coefficient k in the following procedure. η = 100 × {(SO 2 ) 1 − (SO 2 ) 2 } / (SO 2 ) 1 (1) η: Desulfurization rate (SO 2 ) 1 : Inlet SO 2 concentration measured by the SO 2 concentration meter 14 ( ppm) (SO 2 ) 2 : Outlet SO 2 concentration (ppm) measured by the SO 2 concentration meter 15 η = k × f 1 {(SO 2 ) 1 } · f 2 (L) · f 3 (G) · f 4 (pH) (2) L: the absorption tower circulating fluid volume (m 3 / h) G: gas volume (m 3 / h) pH: absorption tower pH k = η / [f 1 {(SO 2) 1}・ F 2 (L) ・ f 3 (G) ・ f 4 (pH)] (3) The coefficient k is set as a design value. K at
The following performance prediction calculation is performed by using, so that highly accurate calculation can be performed.
【0015】演算部(脱硫性能予測手段)22は各負荷
における性能を(2)式を用いて予測計算するものでデ
ータとしては現状のプロセス量である循環液量L、吸収
塔pHを用い、排ガス性状としては内部データ貯蔵部2
5に貯えられた各燃料種毎の各負荷排ガス性状(ガス量
G、SO2濃度(SO2)1)である。これらのデータを
用い各負荷時の脱硫性能を予測計算し、煙突出口SO2
濃度を求める。The calculating section (desulfurization performance predicting means) 22 predicts and calculates the performance at each load by using the equation (2), and uses the circulating liquid amount L and the absorption tower pH which are the current process amounts as data. Internal data storage 2 as exhaust gas properties
5 shows the properties (gas amount G, SO 2 concentration (SO 2 ) 1 ) of each load exhaust gas for each fuel type stored in No. 5 . Using these data, the desulfurization performance at each load was predicted and calculated, and the smoke outlet SO 2
Find the concentration.
【0016】脱硫装置の異常の一例として、例えば、吸
収塔循環ポンプ7の4台の内1台が故障した場合は、吸
収塔循環液量Lは定格値の3/4に低下し、脱硫性能が
低下することになる。As an example of the abnormality of the desulfurization apparatus, for example, when one of the four absorption tower circulating pumps 7 fails, the circulating liquid amount L of the absorption tower is reduced to / of the rated value, and the desulfurization performance is reduced. Will decrease.
【0017】次に演算部(発電プラント最適負荷設定手
段)23で環境規制値データ27と上述の演算部22で
計算した各負荷での煙突出口SO2濃度から、規制値を
満足するに最適な発電プラントの負荷を演算し、設定す
る。最後に演算部(発電プラント負荷出力制御手段)2
4で最適負荷を制御装置に出力指令する。Next, based on the environmental regulation value data 27 and the smoke outlet SO 2 concentration at each load calculated by the computing unit 22 in the computing unit (optimum load setting means for power plant) 23, an optimal regulation value is satisfied. Calculate and set the load of the power plant. Finally, a calculation unit (power plant load output control means) 2
In step 4, the optimum load is output to the control device.
【0018】本実施例の具体的な作用について以下例を
用いて説明する。まず、次の異常現象についてのケース
を考える。 異常現象(1) 吸収塔循環ポンプ1台故障 異常現象(2) 〃 2台故障 ボイラ使用燃料および性状について下記発電プラントの
100%、75%、50%、25%の各負荷時における
SO2条件を考慮する。The specific operation of the present embodiment will be described below using an example. First, consider the case of the following abnormal phenomenon. Abnormal phenomenon (1) Absorption tower circulation pump 1 failure Abnormal phenomenon (2) 〃 2 failures Regarding fuel and properties of boiler SO 2 condition at each load of 100%, 75%, 50%, 25% of the following power plant Consider.
【0019】[0019]
【表1】 [Table 1]
【0020】上記の異常現象(1)、(2)とボイラ運
転条件(a)、(b)の組み合わせから四ケースの条件
について、前記(2)式により出口SO2濃度を計算す
る。From the combination of the above abnormal phenomena (1) and (2) and the boiler operating conditions (a) and (b), the outlet SO 2 concentration is calculated by the above equation (2) under four conditions.
【0021】[0021]
【表2】 [Table 2]
【0022】ここで規制値を100ppmとすると演算
部23により規制値を満足する負荷が次のように設定さ
れる。 ケース1{異常(1)、燃料(a)} 25% ケース2{異常(1)、燃料(b)} 100% ケース3{異常(2)、燃料(a)} 0%(停
止) ケース4{異常(2)、燃料(b)} 50%Here, assuming that the regulation value is 100 ppm, the load which satisfies the regulation value is set by the arithmetic unit 23 as follows. Case 1 (abnormal (1), fuel (a)) 25% Case 2 (abnormal (1), fuel (b)) 100% Case 3 (abnormal (2), fuel (a)) 0% (stop) Case 4 {Abnormal (2), fuel (b)} 50%
【0023】本発明の上記実施例では、脱硫装置の異常
時の対応として発電プラント負荷制限を考えたが、特に
燃料切り替えが迅速に行える重油焚き火力発電プラント
においては、異常時に低硫黄分の重油への切り替えで対
応することも可能である。In the above-described embodiment of the present invention, the load of the power plant is considered as a measure in response to an abnormality of the desulfurization apparatus. It is also possible to respond by switching to.
【0024】[0024]
【発明の効果】本発明によれば脱硫装置の異常発生時に
その異常の程度およびその時の運転状態(ボイラ、使用
燃料)から 性能予測計算を行うことにより、規制値を
越えることなく最適な発電プラント負荷を設定できる効
果がある。According to the present invention, when an abnormality occurs in a desulfurization unit, a performance prediction calculation is performed based on the degree of the abnormality and the operating state (boiler, fuel used) at that time, so that the optimum power generation plant without exceeding the regulation value is obtained. There is an effect that the load can be set.
【図1】本発明の実施例の計算システムの構成図であ
る。FIG. 1 is a configuration diagram of a calculation system according to an embodiment of the present invention.
【図2】排煙脱硫装置の系統図である。FIG. 2 is a system diagram of a flue gas desulfurization device.
2 排ガス煙道 3 吸収塔 6 吸収塔循環タンク 7 吸収塔循環ポンプ 8 石灰石スラリ槽 13 排ガス流量計 14 入口SO2濃度計 15 出口SO2濃度計2 Exhaust gas flue 3 Absorption tower 6 Absorption tower circulation tank 7 Absorption tower circulation pump 8 Limestone slurry tank 13 Exhaust gas flow meter 14 Inlet SO 2 concentration meter 15 Outlet SO 2 concentration meter
Claims (2)
ガス中の硫黄酸化物を除去する排煙脱硫装置において、
脱硫装置の性能に関連する排ガス量、入口SO2濃度、
出口SO2濃度、吸収液pH、石灰石スラリ量、吸収塔
循環液量、酸化空気量等のプロセス量から発電機出力、
燃料切り替え等の発電プラント負荷に応じた脱硫性能を
予測する脱硫性能予測手段と、該脱硫性能予測手段の予
測値と予め設定されている環境規制値と比較して環境規
制値に基づき許容される発電プラントの最適負荷を設定
する発電プラント最適負荷設定手段と、該発電プラント
最適負荷設定手段の設定値に基づき発電プラントの負荷
出力制御を行う発電プラント負荷出力制御手段と、を設
けたことを特徴とする排煙脱硫装置。1. A flue gas desulfurization device for removing sulfur oxides in exhaust gas discharged from a combustion device such as a boiler,
Exhaust gas quantity related to the performance of the desulfurization apparatus, inlet SO 2 concentration,
The output of the generator from the process amount such as outlet SO 2 concentration, absorption liquid pH, limestone slurry amount, absorption tower circulation liquid amount, oxidizing air amount, etc.
Desulfurization performance prediction means for predicting the desulfurization performance according to the power plant load such as fuel switching, and comparing the predicted value of the desulfurization performance prediction means with a preset environmental regulation value to allow based on the environmental regulation value. A power plant optimum load setting means for setting an optimum load of the power plant, and a power plant load output control means for controlling a load output of the power plant based on a set value of the power plant optimum load setting means are provided. And flue gas desulfurization equipment.
荷設定手段と発電プラント負荷出力制御手段とは、前記
プロセス量の異常時にも作動することを特徴とする請求
項1記載の排煙脱硫装置。2. The flue gas desulfurization apparatus according to claim 1, wherein the desulfurization performance prediction means, the power plant optimum load setting means, and the power plant load output control means operate even when the process amount is abnormal.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP09387791A JP3190938B2 (en) | 1991-04-24 | 1991-04-24 | Flue gas desulfurization equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP09387791A JP3190938B2 (en) | 1991-04-24 | 1991-04-24 | Flue gas desulfurization equipment |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH04322721A JPH04322721A (en) | 1992-11-12 |
| JP3190938B2 true JP3190938B2 (en) | 2001-07-23 |
Family
ID=14094707
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP09387791A Expired - Fee Related JP3190938B2 (en) | 1991-04-24 | 1991-04-24 | Flue gas desulfurization equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3190938B2 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113082990B (en) * | 2021-04-09 | 2023-05-30 | 浙江菲达环保科技股份有限公司 | One-key start-stop method and system for full-load section of desulfurization system |
| CN115155269B (en) * | 2022-09-09 | 2023-01-24 | 启东凯顺机械制造有限公司 | Automatic control method of gas fine desulfurization system |
| CN115738622B (en) * | 2023-01-09 | 2023-05-12 | 常州嘉瑞特环保能源科技有限公司 | Tail gas emission detection system of desulfurization equipment |
-
1991
- 1991-04-24 JP JP09387791A patent/JP3190938B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH04322721A (en) | 1992-11-12 |
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