JPS60227845A - Treating apparatus of exhaust gas - Google Patents

Treating apparatus of exhaust gas

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Publication number
JPS60227845A
JPS60227845A JP59085985A JP8598584A JPS60227845A JP S60227845 A JPS60227845 A JP S60227845A JP 59085985 A JP59085985 A JP 59085985A JP 8598584 A JP8598584 A JP 8598584A JP S60227845 A JPS60227845 A JP S60227845A
Authority
JP
Japan
Prior art keywords
gas
exhaust gas
temp
coal
inlet
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
Application number
JP59085985A
Other languages
Japanese (ja)
Inventor
Masatoshi Kudome
正敏 久留
Takeshi Kunimoto
国本 武志
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP59085985A priority Critical patent/JPS60227845A/en
Publication of JPS60227845A publication Critical patent/JPS60227845A/en
Pending legal-status Critical Current

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Abstract

PURPOSE:To improve the collectivity by providing a temp. control means of exhaust gas on the upstream side of an electrical dust collector, and regulating the heat absorption of the heat retained by boiler exhaust gas in the treating apparatus of exhaust gas. CONSTITUTION:The combustion gas discharged from a boiler 1 is heat-exchanged with combustion air at an air preheater 4. The gas temp. at the inlet to an electrical dust collector 6 or the contained ash content is detected by a detector 20, and the amt. of a medium for controlling the gas temp. at the inlet to the electrical dust collector which is supplied into a gas temp. controller 17 is controlled through a control valve 18 so that the inlet gas temp. or the electric resistance may be regulated to a specified value to prevent a decrease in the dust collecting performance due to the variation in the kind of coals, etc. A low-pressure feed-water heater, and air- or seawater-cooled exhaust gas cooler, a cold-water spray, etc. are used as the gas temp. controller. The gas freed of dust at the electrical dust collector is pressurized by an induced draft blower 8, SO2, etc. is removed at a stack gas desulfurizer 9, and the gas is discharged into the atmosphere from a stack 11.

Description

【発明の詳細な説明】 本発明は排ガス処理装置に係り、特に石炭焚きボイラ等
に適用し得る排ガス処理装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an exhaust gas treatment device, and more particularly to an exhaust gas treatment device that can be applied to a coal-fired boiler or the like.

従来の排ガス処理装置は、例えば第1図に示す如く、ボ
イラ1における燃焼部2から排出される燃焼ガスは、ボ
イラ出口煙道3を経て空気予熱器4にて燃焼用空気と熱
交換を行なった後、空気予熱器出口煙道5ケ経て電気集
塵器6に流入する。石炭燃焼ガス中には、通常多量(瀝
青炭で20〜50 rr/N7y?)の灰(石炭に含ま
れている灰分)が含有されているが、電気集塵器6はこ
の燃焼ガス中に含有されている灰を除去するものである
。電気集塵器6で除塵された燃焼ガスは、集塵器出口煙
道7を経て誘引通風機8にて昇圧後、排煙脱硫装置9で
SO2および残留煤塵除去後煙道10を経て煙突11よ
り大気に廃棄されるようになされている。
In a conventional exhaust gas treatment device, for example, as shown in FIG. 1, combustion gas discharged from a combustion section 2 in a boiler 1 passes through a boiler outlet flue 3 and exchanges heat with combustion air in an air preheater 4. After that, the air flows into the electrostatic precipitator 6 through five air preheater outlet flues. Coal combustion gas usually contains a large amount of ash (ash contained in coal) (20 to 50 rr/N7y for bituminous coal), but the electrostatic precipitator 6 can remove the ash contained in this combustion gas. This is to remove the ash that has been removed. The combustion gas from which dust has been removed by the electrostatic precipitator 6 passes through the dust collector outlet flue 7, increases its pressure in the induced draft fan 8, removes SO2 and residual soot in the flue gas desulfurization device 9, and passes through the flue 10 to the chimney 11. more waste is being disposed of into the atmosphere.

上記の如〈従来の排ガス処理装置は、入口ガス温度調整
機能がないので、特に石炭焚きボイラ用排ガス処理装置
においては、下記の如き問題を生ずる。
As described above, the conventional exhaust gas treatment apparatuses do not have an inlet gas temperature adjustment function, and therefore, the following problems occur, especially in exhaust gas treatment apparatuses for coal-fired boilers.

石炭焚きボイラ用電気集塵器入口ガス性状の特徴として
は、 (1)石炭性状特に水分量により、石炭乾燥用空気(−
次空気)の必要量が変る。このため空気予熱器通過空気
量が変り、空気予熱器出口(電気集塵器入口)ガス温度
が変る。
Characteristics of the gas properties at the inlet of an electrostatic precipitator for coal-fired boilers include: (1) Depending on the coal properties, especially the moisture content, the coal drying air (-
The required amount of air) changes. Therefore, the amount of air passing through the air preheater changes, and the gas temperature at the air preheater outlet (electrostatic precipitator inlet) changes.

(11)石炭燃焼ガス中には、多量の石炭灰が含有され
ており、その量は石炭中に含まれる灰分量による。一般
的な瀝青炭で燃焼ガス中濃度は10〜50 ?r/N−
である。これらを除去しないと大気中に廃棄され大気を
汚染する。
(11) Coal combustion gas contains a large amount of coal ash, and the amount depends on the amount of ash contained in the coal. Is the concentration in the combustion gas of common bituminous coal 10 to 50? r/N-
It is. If these are not removed, they will be discarded into the atmosphere and pollute the air.

011)石炭灰は多種類の鉱物質より構成されていて、
その捕集性は灰性状により変るとともに温度によっても
変る。これは灰の電気抵抗が温度に大きく影響されるか
らである。
011) Coal ash is composed of many types of minerals,
Its collection ability changes depending on the ash properties and also changes depending on the temperature. This is because the electrical resistance of ash is greatly affected by temperature.

上記の如く石炭灰の捕集性はガス温度により影響され、
その性状により適正温度域が存在するが、従来の排ガス
処理装置は、前記の如くガス温度調整機能がないため、
石炭性状変動に際し排ガス温度が適正温度に力らないの
で、その捕集効率が著しく低下する場合がある等の欠点
があった。
As mentioned above, the collection performance of coal ash is affected by the gas temperature.
There is an appropriate temperature range depending on its properties, but conventional exhaust gas treatment equipment does not have a gas temperature adjustment function as mentioned above.
When the coal properties change, the temperature of the exhaust gas is not maintained at an appropriate temperature, so there are drawbacks such as a significant drop in the collection efficiency.

本発明は上記の事情に鑑みて提案されたもので、その目
的とするところは、電気集塵装置の入口ガス温度を適正
温度に制御して電気集塵装置の集塵性能を向上し得る排
ガス処理装置を提供することにある。
The present invention has been proposed in view of the above circumstances, and its purpose is to improve the dust collection performance of the electrostatic precipitator by controlling the inlet gas temperature of the electrostatic precipitator to an appropriate temperature. The purpose of this invention is to provide a processing device.

本発明による排ガス処理装置は、排ガスを電気集塵装置
に導いて、排ガス中のダストを集塵するようにした排ガ
ス処理装置において、上記電気集塵装置の上流に排ガス
の温度制御手段を設けたことを特徴とt/%電気集塵装
置の上流に、例えば低圧給水加熱器、空気又は海水冷却
式排ガスクーラ、冷空気導入装置および冷水スプレィ装
置等を設置して、ボイラ排ガス保有熱の熱吸収量を調整
して適正排ガス温度を維持することにより捕集性を向上
させるようにして、前記従来の欠点を解消し得るように
したものである。
An exhaust gas treatment device according to the present invention is an exhaust gas treatment device that guides exhaust gas to an electrostatic precipitator to collect dust in the exhaust gas, and includes temperature control means for the exhaust gas provided upstream of the electrostatic precipitator. The feature is that, upstream of the t/% electrostatic precipitator, for example, a low-pressure feed water heater, an air or seawater cooling type exhaust gas cooler, a cold air introduction device, a cold water spray device, etc. are installed to absorb the heat held in the boiler exhaust gas. The above-mentioned drawbacks of the conventional methods can be overcome by adjusting the amount and maintaining a proper exhaust gas temperature to improve collection performance.

本発明の実施例を添付図面を参照して詳細に説明する。Embodiments of the present invention will be described in detail with reference to the accompanying drawings.

第2図は本発明の一実施例の構成を示す図、第3図は燃
焼ガス温度と灰の電気抵抗との関係を示す図、第4図は
燃焼ガス温度による電気抵抗の低下を示す図、第5図〜
第8図はそれぞれ本発明の一実施例におけるガス温度制
御装置の例を示す図、第9図は本発明の一実施例におけ
る燃焼ガス中のSO,濃度と酸露点との関係を示す図で
ある。
Fig. 2 is a diagram showing the configuration of an embodiment of the present invention, Fig. 3 is a diagram showing the relationship between combustion gas temperature and electrical resistance of ash, and Fig. 4 is a diagram showing the decrease in electrical resistance depending on combustion gas temperature. , Figure 5~
FIG. 8 is a diagram showing an example of a gas temperature control device according to an embodiment of the present invention, and FIG. 9 is a diagram showing the relationship between SO, concentration, and acid dew point in combustion gas in an embodiment of the present invention. be.

第2図に示されたものは、本発明をボイラから排出され
るガスを処理する装置に適用した場合の一実施例であり
、この場合のボイラから排出される灰の性状と集塵性能
との関係について第3図および第4図について説明する
What is shown in Fig. 2 is an example in which the present invention is applied to a device for treating gas discharged from a boiler, and the properties and dust collection performance of the ash discharged from the boiler in this case are The relationship will be explained with reference to FIGS. 3 and 4.

一般に石炭は炭素、水素、酸素、窒素、硫黄を主成分と
17た有機化合物を主体に灰分および水分を含有してお
り、火炉で燃焼し燃焼ガスとなる。その組成および灰組
成は石炭により大巾に変化するが、灰の捕集性はその電
気抵抗に支配され電気抵抗が小さい程捕集性が優れる。
Coal generally contains carbon, hydrogen, oxygen, nitrogen, and sulfur as its main components, as well as organic compounds, 17 ash, and moisture, and is burned in a furnace to become combustion gas. Although its composition and ash composition vary widely depending on the coal, the collection performance of ash is controlled by its electrical resistance, and the lower the electrical resistance, the better the collection performance.

灰の電気抵抗を支配する成分は燃焼ガス中のSOsと灰
中のNa2OmKto等のアルカリ金属である。
The components that control the electrical resistance of the ash are SOs in the combustion gas and alkali metals such as Na2OmKto in the ash.

前者は低温域において灰の表面に吸着し電気抵抗を下げ
る(表面伝導支配)又、後着は体積伝導率を高め電気抵
抗を下げる。従って高温域では体積伝導が支配的となり
、低温域では表面伝導が支配的となる。低温集塵器はガ
ス温度が低い(通常180℃以下)域で使用するもので
、その集血性はSO3の灰付着量(表面伝導)に影響さ
れろ。第3図に燃焼ガス温度と灰の電気抵抗の関係を示
す。第3図中の(A) 、 (B) 、 (C) 、 
(D)は石炭の特徴を示す。(5)は硫黄分およびアル
カリ成分共少ない石炭、(B)は硫黄分は少ないがアル
カリ成分は多い石炭、(C)は硫黄分は多くアルカリ成
分の少ない石炭、(至)は硫黄分、アルカリ成分共多い
石炭の燃焼ガス中灰分の電気抵抗を示す。
The former adsorbs to the surface of the ash at low temperatures and lowers the electrical resistance (dominated by surface conduction), while the latter increases the volume conductivity and lowers the electrical resistance. Therefore, volume conduction becomes dominant in the high temperature region, and surface conduction becomes dominant in the low temperature region. Low-temperature dust collectors are used in areas where the gas temperature is low (usually below 180°C), and their ability to collect blood is affected by the amount of SO3 ash attached (surface conduction). Figure 3 shows the relationship between combustion gas temperature and electrical resistance of ash. (A), (B), (C) in Figure 3,
(D) shows the characteristics of coal. (5) is coal with low sulfur and alkali content, (B) is coal with low sulfur content but high alkali content, (C) is coal with high sulfur content and low alkali content, and (to) is coal with low sulfur content and alkali content. It shows the electrical resistance of ash in the combustion gas of coal, which has many components.

第3図が示す様に電気抵抗はガス温度によりかわり、そ
の極大値となる温度が低温電気集塵器適用温度域に存在
する。ここで石炭焚きボイラの燃焼ガス温度はボイラ負
荷により変るのみならず、石炭性状により変るし又、石
炭性状により電気抵抗特性が異なるので、成る条件(成
る石炭、成るガス温度条件)に対し設計した電気集塵器
は他の条件(石炭が設計炭と相違する場合)下では集塵
性能が著しく低下することがある(第4図で設計点A点
に対し、石炭が変ることにより使用点が3点となり電気
抵抗が増加し集塵性能が低下する)この様に従来方式で
は使用炭が設計炭と相違する場合、集塵性能が大きく低
下し、煙突より飛散する煤塵量が許容限界以上となり大
気汚染上重大な問題と々る〇本発明は上記の問題を解消
するために冷されたもので、第2図および第5図〜M7
図において第1図に示されたものと同一部分には同一符
号を伺して説明する。
As shown in FIG. 3, the electrical resistance changes depending on the gas temperature, and the temperature at which it reaches its maximum value exists in the temperature range where the low-temperature electrostatic precipitator is applicable. Here, the combustion gas temperature of a coal-fired boiler changes not only depending on the boiler load, but also on the coal properties, and the electrical resistance characteristics differ depending on the coal properties, so the temperature of the combustion gas in a coal-fired boiler is designed for the following conditions (coal, gas temperature conditions). The dust collection performance of an electrostatic precipitator may deteriorate significantly under other conditions (when the coal is different from the designed coal) (in Figure 4, the usage point is different from the design point A due to a change in the coal). 3 points, the electrical resistance increases and the dust collection performance decreases) In this way, in the conventional method, if the charcoal used is different from the designed charcoal, the dust collection performance decreases significantly, and the amount of soot and dust scattered from the chimney exceeds the allowable limit. This is a serious problem in terms of air pollution. The present invention is cooled to solve the above problems, and the problems shown in Figs. 2 and 5 to M7
In the figures, the same parts as those shown in FIG. 1 will be described using the same reference numerals.

第2図において、17はガス温度制御装置、18は制御
弁、19は制御弁作動リレー、2゜はガス温度又は含有
灰分の電気抵抗の検出器であり、これらの各要素が第1
図に示す従来例に伺加されている。
In FIG. 2, 17 is a gas temperature control device, 18 is a control valve, 19 is a control valve activation relay, and 2° is a gas temperature or electric resistance detector for contained ash.
This is an addition to the conventional example shown in the figure.

上記本発明の一実施例の作用について説明するO 第2図に示された↓うに、電気集塵器6の入口ガス温度
又は含有灰分の電気抵抗を検出器20で検出し5、ガス
温度制御装置17に供給される電気集塵器6の入口ガス
温度制御媒体量を制御弁作動リレー19および制御弁1
8を介して、上記入口ガス温度又は電気抵抗が所定値に
力るように制御することにより、炭種変動等による電気
集塵器6の集塵性能の低下を防止することができる。
The operation of the above-mentioned embodiment of the present invention will be explained below. As shown in FIG. The amount of inlet gas temperature control medium of the electrostatic precipitator 6 supplied to the device 17 is controlled by the control valve activation relay 19 and the control valve 1.
By controlling the inlet gas temperature or electrical resistance to a predetermined value through the precipitator 8, it is possible to prevent the dust collection performance of the electrostatic precipitator 6 from deteriorating due to variations in coal type or the like.

第5図に示すものは、第2図におけるガス温度制御装置
17として低圧給水加熱方式のガス温度制御装置17を
使用する場合、の実施例を示すもので、この実施例によ
れば燃焼ガス温度の調整と同時に、燃焼ガス保有熱を回
収してプラントの熱効率の向上をも図ることができるも
のである。第5図において復水器21より得られる復水
は、後水ポンプ22により昇圧後、第1低圧給水ヒータ
23および第2低圧給水ヒータ24を経て第3低圧給水
ヒータ(図示せず)又は脱気器(図示せず)に至るが、
この低圧給水の一部を低圧給水加熱方式のガス温度制御
装置(燃焼ガス/低圧給水ヒータ)77に導き燃焼排ガ
ス保有熱を回収するようになされている。
What is shown in FIG. 5 is an embodiment in which a low-pressure feed water heating type gas temperature control device 17 is used as the gas temperature control device 17 in FIG. 2. According to this embodiment, the combustion gas temperature At the same time, it is possible to improve the thermal efficiency of the plant by recovering the heat retained in the combustion gas. In FIG. 5, the condensate obtained from the condenser 21 is pressurized by the rear water pump 22, passes through the first low-pressure water heater 23 and the second low-pressure water heater 24, and then is sent to the third low-pressure water heater (not shown) or desorbed. This leads to the respiratory organs (not shown),
A part of this low-pressure feed water is guided to a gas temperature control device (combustion gas/low-pressure feed water heater) 77 of a low-pressure feed water heating type, and the heat retained in the combustion exhaust gas is recovered.

この場合電気集塵器6の入口ガス温度は、給水ヒータ給
水量の制御、給水ヒータの伝熱面積の調整又は通過燃焼
ガス量の調整により制御される。
In this case, the inlet gas temperature of the electrostatic precipitator 6 is controlled by controlling the amount of water supplied to the feed water heater, adjusting the heat transfer area of the feed water heater, or adjusting the amount of passing combustion gas.

第6図に示すものは第2図におけるガス温度制御装置ノ
アとして冷水スプレィ方式のガス温度制御装[77を使
用する場合の例であり、この例では水の蒸発潜熱を利用
して小Uの水@霧にて燃焼ガス温度を制御(低下)する
ものである。この場合@霧水により燃焼ガス中の水蒸気
分圧が上昇するが、例えば第9図に示すように、酸露点
が上昇し灰のSO,吸着量が増加するため灰の電気抵抗
は更に改善される効果がある。因に燃焼ガス温度を10
℃低下させるに必要なスプレィ水量はガス量の約0.4
%程度である。第6図における制御弁18はスプレィ制
御弁となり、ガス温度制御装置17はヌブし/イノズル
となる。
What is shown in Fig. 6 is an example in which a cold water spray type gas temperature control device [77] is used as the gas temperature control device Noah in Fig. 2. In this example, the latent heat of vaporization of water is used to The combustion gas temperature is controlled (lowered) using water @ fog. In this case, the partial pressure of water vapor in the combustion gas increases due to fog water, but as shown in Figure 9, for example, the acid dew point increases and the amount of SO adsorbed by the ash increases, so the electrical resistance of the ash is further improved. It has the effect of Incidentally, the combustion gas temperature is 10
The amount of spray water required to lower the temperature is approximately 0.4 of the amount of gas.
It is about %. The control valve 18 in FIG. 6 is a spray control valve, and the gas temperature control device 17 is a nozzle.

第7図に示すものは、第2図におけるガス温度制御装置
I7として冷空気導入方式を使用する場合の例で、この
方式では、押込通風機出口空気又は大気を電気集塵器6
の入口煙道部に設けた混合器に導入し、燃焼ガスと混合
させてガス温度の低下を図るものである。この場合燃焼
ガスを10℃低下させるのに必要な空気量はガス量の約
9チ程度となる。第7図における制御弁18は冷空気制
御ダンパとなり、13は押込通風機である。
What is shown in FIG. 7 is an example in which a cold air introduction method is used as the gas temperature control device I7 in FIG.
The gas is introduced into a mixer installed at the inlet flue of the engine, and is mixed with combustion gas to lower the gas temperature. In this case, the amount of air required to lower the combustion gas by 10° C. is approximately 9 inches of the gas amount. The control valve 18 in FIG. 7 is a cold air control damper, and 13 is a forced draft fan.

第8図に示すものは第2図におけるガス温度制御装置1
7として空気又は海水冷却方式を使用する場合の例で、
この方式では電気集塵器6の入口煙道に空冷式又は水冷
式冷却器を設置してガス温度を制御する方式である。こ
の場合には処理ガス量が増加しないという利点がある。
What is shown in Fig. 8 is the gas temperature control device 1 in Fig. 2.
7 is an example of using air or seawater cooling method,
In this method, an air-cooled or water-cooled cooler is installed in the inlet flue of the electrostatic precipitator 6 to control the gas temperature. In this case, there is an advantage that the amount of processing gas does not increase.

第8図における制御弁18は空気又は海水量制御弁とな
り、ガス温度制御装置17は熱交換器となる。
The control valve 18 in FIG. 8 is an air or seawater amount control valve, and the gas temperature control device 17 is a heat exchanger.

以上により本発明によれば、排ガス処理装置の電気集塵
装置の入口煙道(上流)に設備された燃焼ガス温度制御
装置により、燃焼ガス温度を適正温度に制御することに
より、例えば第4図に示すように、設計炭と相違する石
炭を使用する場合、従来は灰の電気抵抗がAからBに増
加し、集塵性が著しく低下することになるが、本発明に
よれば燃焼ガス温度を適正温度に下げることにより、例
えば第4図の(5)と同一レベルの電気抵抗Cに低下さ
せることができるので、電気集塵装置の集塵性能を向上
させることができる。
As described above, according to the present invention, the combustion gas temperature is controlled to an appropriate temperature by the combustion gas temperature control device installed at the inlet flue (upstream) of the electrostatic precipitator of the exhaust gas treatment device, for example, as shown in FIG. As shown in Figure 2, when using coal different from the designed coal, conventionally the electrical resistance of the ash increases from A to B, resulting in a significant drop in dust collection, but according to the present invention, the combustion gas temperature By lowering the temperature to an appropriate temperature, the electrical resistance C can be lowered to, for example, the same level as (5) in FIG. 4, so the dust collection performance of the electrostatic precipitator can be improved.

さらに例えばガス温度制御装置として低圧給水加熱方式
を使用すると、燃焼ガス温度を調整して集塵性を向上さ
せると同時に、燃焼ガス保有熱を回収してプラントの熱
効率を向上させることができ、またガス温度制御装置と
して冷水スプレィ方式を使用すると、燃焼ガス中の湿分
増加により、その電気抵抗をさらに低下させ、集塵性能
を一層向上させることができる等の優れた効果が奏せら
れるものである。
Furthermore, for example, if a low-pressure feed water heating system is used as a gas temperature control device, it is possible to adjust the combustion gas temperature to improve dust collection, and at the same time recover the heat retained in the combustion gas to improve the thermal efficiency of the plant. When a cold water spray method is used as a gas temperature control device, the increased moisture in the combustion gas can further reduce its electrical resistance, further improving dust collection performance, and other excellent effects can be achieved. be.

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

第1図は従来例の構成を示す図、第2図は本発明の一実
施例の構成を示す図、第3図は燃焼ガス温度と灰の電気
抵抗との関係を示す図、第4図は燃焼ガス温度による電
気抵抗の低下を示す図、第5図〜第8図はそれぞれ本発
明の一実施例におけるガス温度制御装置の例を示す図、
第9図は本発明の一実施例における燃焼ガス中のSO8
濃度と酸露点との関係を示す図である。 17・・・ガス温度制御装置、18・・・制御弁、19
・・・制御弁作動リレー、20・・・検出器。 出願人復代理人 弁理士 鈴 江 武 彦第 1 図 5 第3図 たり6力・・入扁度 □ 第4図 産児か・ス遷凰 □
Fig. 1 is a diagram showing the configuration of a conventional example, Fig. 2 is a diagram showing the configuration of an embodiment of the present invention, Fig. 3 is a diagram showing the relationship between combustion gas temperature and electrical resistance of ash, and Fig. 4 is a diagram showing a decrease in electrical resistance due to combustion gas temperature, and FIGS. 5 to 8 are diagrams each showing an example of a gas temperature control device in an embodiment of the present invention.
Figure 9 shows SO8 in the combustion gas in one embodiment of the present invention.
FIG. 3 is a diagram showing the relationship between concentration and acid dew point. 17... Gas temperature control device, 18... Control valve, 19
...Control valve operation relay, 20...Detector. Applicant's Sub-Attorney Patent Attorney Takehiko Suzue No. 1 Figure 5 Figure 3: 6-force degree of entry □ Figure 4: Birth of child/su transition □

Claims (1)

【特許請求の範囲】[Claims] 排ガスを電気集塵装置に導いて、排ガス中ノダストを集
塵するようにした排ガス処理装置において、上記電気集
塵装置の上流に排ガスの温度制御手段を設けたことを特
徴とする排ガス処理装置。
What is claimed is: 1. An exhaust gas treatment device for guiding exhaust gas to an electrostatic precipitator to collect dust in the exhaust gas, characterized in that an exhaust gas temperature control means is provided upstream of the electrostatic precipitator.
JP59085985A 1984-04-27 1984-04-27 Treating apparatus of exhaust gas Pending JPS60227845A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59085985A JPS60227845A (en) 1984-04-27 1984-04-27 Treating apparatus of exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59085985A JPS60227845A (en) 1984-04-27 1984-04-27 Treating apparatus of exhaust gas

Publications (1)

Publication Number Publication Date
JPS60227845A true JPS60227845A (en) 1985-11-13

Family

ID=13873980

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59085985A Pending JPS60227845A (en) 1984-04-27 1984-04-27 Treating apparatus of exhaust gas

Country Status (1)

Country Link
JP (1) JPS60227845A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63171622A (en) * 1987-01-09 1988-07-15 Babcock Hitachi Kk Exhaust gas treating device
JP2001239129A (en) * 2000-03-03 2001-09-04 Babcock Hitachi Kk Exhaust gas treatment apparatus and operation method therefor
JP2009008365A (en) * 2007-06-29 2009-01-15 Hitachi Ltd Steam power plant
EP2568130A2 (en) 2011-09-12 2013-03-13 Hitachi, Ltd. Heat recovery system of the boiler with CO2 capture system
EP2620707A1 (en) * 2010-09-21 2013-07-31 Shanghai Fubo EP Equipment Co., Ltd. Energy-saving dust collector
JP2016000377A (en) * 2014-06-11 2016-01-07 中国電力株式会社 Power station operation system

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS51119569A (en) * 1975-04-11 1976-10-20 Hitachi Plant Eng & Constr Co Ltd Electric dust collecting method
JPS5250076A (en) * 1975-10-21 1977-04-21 Hitachi Plant Eng & Constr Co Ltd Electric precipitator

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS51119569A (en) * 1975-04-11 1976-10-20 Hitachi Plant Eng & Constr Co Ltd Electric dust collecting method
JPS5250076A (en) * 1975-10-21 1977-04-21 Hitachi Plant Eng & Constr Co Ltd Electric precipitator

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63171622A (en) * 1987-01-09 1988-07-15 Babcock Hitachi Kk Exhaust gas treating device
JP2001239129A (en) * 2000-03-03 2001-09-04 Babcock Hitachi Kk Exhaust gas treatment apparatus and operation method therefor
JP4725985B2 (en) * 2000-03-03 2011-07-13 バブコック日立株式会社 Operation method of flue gas treatment equipment
JP2009008365A (en) * 2007-06-29 2009-01-15 Hitachi Ltd Steam power plant
EP2620707A1 (en) * 2010-09-21 2013-07-31 Shanghai Fubo EP Equipment Co., Ltd. Energy-saving dust collector
EP2620707A4 (en) * 2010-09-21 2015-01-28 Shanghai Fubo Ep Equipment Co Ltd Energy-saving dust collector
EP2568130A2 (en) 2011-09-12 2013-03-13 Hitachi, Ltd. Heat recovery system of the boiler with CO2 capture system
US8752385B2 (en) 2011-09-12 2014-06-17 Hitachi, Ltd. Heat recovery system of the boiler with CO2 capture system
JP2016000377A (en) * 2014-06-11 2016-01-07 中国電力株式会社 Power station operation system

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