JPH11128659A - Device for treating waste gas in starting coal gasification plant - Google Patents

Device for treating waste gas in starting coal gasification plant

Info

Publication number
JPH11128659A
JPH11128659A JP9299932A JP29993297A JPH11128659A JP H11128659 A JPH11128659 A JP H11128659A JP 9299932 A JP9299932 A JP 9299932A JP 29993297 A JP29993297 A JP 29993297A JP H11128659 A JPH11128659 A JP H11128659A
Authority
JP
Japan
Prior art keywords
gas
circulating water
coal gasification
gasification plant
exhaust 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.)
Granted
Application number
JP9299932A
Other languages
Japanese (ja)
Other versions
JP3665919B2 (en
Inventor
Fumihiko Hanayama
文彦 花山
Naoki Kamata
直紀 鎌田
Yoshiki Watabe
芳樹 渡部
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 Power Ltd
Original Assignee
Babcock Hitachi KK
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 Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP29993297A priority Critical patent/JP3665919B2/en
Publication of JPH11128659A publication Critical patent/JPH11128659A/en
Application granted granted Critical
Publication of JP3665919B2 publication Critical patent/JP3665919B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Landscapes

  • Industrial Gases (AREA)
  • Engine Equipment That Uses Special Cycles (AREA)
  • Exhaust Gas After Treatment (AREA)
  • Treating Waste Gases (AREA)

Abstract

PROBLEM TO BE SOLVED: To inhibit the corrosion of an equipment constituting material at the time of starting, in a gas treating device for bringing the gas generated in starting a pressurized coal gasification plant into contact with water to cool and purify the gas. SOLUTION: The gas generated in starting a pressurized coal gasification plant is brought into contact with water, purified and cooled in this gas treating device. In this case, the hydrogen ion concn. (pH) of the circulating water to be brought into contact with the generated gas is kept at 6 to 9 to prevent the corrosion of the equipment constituting material. As the means, a pH meter 33 for measuring the pH of the circulating water in a decanter 26 attached to a gas purifier 3, a pH controller 34 for controlling the supply of a pH regulator (sodium hydroxide, etc.), to the circulating water based on the output of the pH meter 33, a pressure reducing valve 28 for reducing the pressure of the circulating water in the decanter 26 and a pressure reducer 7 for liberating the acidic gas from the pressure-reduced cooling water are provided. Further, a cooler 24 for cooling the cooling water to 50 deg.C or a heater for heating it to 130 deg.C is provided.

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、石炭等の原料を酸
素を含むガス化剤により高温・高圧下でガス化して生成
ガスを得るガス化プラントの起動装置のうち、起動時に
軽油などの燃料を燃焼する際に発生する排ガスを水と接
触させることにより、ガス中に含まれる一酸化窒素、二
酸化窒素等の窒素酸化物あるいは亜硫酸ガス等の微量含
まれる酸性ガス成分を洗浄・除去するガス処理工程の水
循環系統において、起動時の排ガス中に含まれる炭酸ガ
ス等により機器構成材料の腐食を防止する装置に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a starting apparatus for a gasification plant in which a raw material such as coal is gasified at high temperature and high pressure with a gasifying agent containing oxygen to obtain a product gas. Gas treatment for cleaning and removing small amounts of acidic gas components such as nitrogen oxides such as nitric oxide and nitrogen dioxide and sulfur dioxide gas contained in the gas by contacting the exhaust gas generated when combusting gas with water TECHNICAL FIELD The present invention relates to an apparatus for preventing corrosion of equipment constituent materials by carbon dioxide or the like contained in exhaust gas at the time of startup in a water circulation system of a process.

【0002】[0002]

【従来の技術】石炭は豊富な埋蔵量を持つ有用なエネル
ギー源であるが、十数%の灰分(アルミナ、シリカ、カ
ルシウム等)や有害金属(Cr,Hg等)を含むため、
その処理法が難しく適用範囲を狭めていた。しかし噴流
層石炭ガス化装置等では、石炭を酸素等のガス化剤によ
り高温下で部分燃焼して有用なガスを生成すると共に、
灰分を溶融させ有害成分が溶出しにくいスラグとして系
外に取り出すことができる。このため、利用分野が広が
り、特に発電用の燃料として、あるいは産業用の原料と
して有望視されている。
2. Description of the Related Art Coal is a useful energy source with abundant reserves. However, coal contains more than 10% of ash (alumina, silica, calcium, etc.) and harmful metals (Cr, Hg, etc.).
The processing method was difficult and narrowed the applicable range. In spouted bed coal gasifiers, however, coal is partially burned at high temperatures with a gasifying agent such as oxygen to produce useful gas,
It can be taken out of the system as a slag that melts ash and hardly elutes harmful components. For this reason, the field of application is expanding, and it is expected to be particularly useful as a fuel for power generation or a raw material for industrial use.

【0003】図2に、従来の加圧型噴流層ガス化プラン
トにおける、ガス化炉から湿式のガス処理装置廻りの系
統図を示す。この装置では、まず油バーナ13に燃料油
14及び空気15を供給して燃焼することにより、ガス
化炉1から熱回収ボイラ2及びフィルタ6に至る系統の
温度及び圧力を上昇させ、所定の温度及び圧力に到達さ
せて起動準備を行う。このシステムでは、発生ガス11
を湿式のガス処理装置である洗浄器3に通して洗浄しな
がら、出口に設けた圧力調整弁16により、除々に系の
圧力を所定値まで昇圧する。昇温及び昇圧が完了したの
ち、燃料である微粉炭17と酸化剤18をガス化炉1に
投入し、徐々にガス化運転に切り替えていく。洗浄器3
では弁42を開けて循環水20をポンプ9により循環さ
せ、発生ガス11と気液接触させることにより、発生ガ
ス11中に微量含まれるガス成分や未燃分が湿式除去さ
れる。
FIG. 2 is a system diagram of a conventional pressurized spouted bed gasification plant from a gasifier to a wet gas processing apparatus. In this apparatus, first, the fuel oil 14 and the air 15 are supplied to the oil burner 13 and burned, so that the temperature and pressure of the system from the gasifier 1 to the heat recovery boiler 2 and the filter 6 are increased, and the predetermined temperature is increased. And the pressure is reached to prepare for startup. In this system, the generated gas 11
Is passed through the cleaning device 3 which is a wet type gas processing device, and the pressure of the system is gradually increased to a predetermined value by the pressure regulating valve 16 provided at the outlet. After the temperature increase and the pressure increase are completed, the pulverized coal 17 and the oxidizer 18 as the fuel are charged into the gasification furnace 1, and the operation is gradually switched to the gasification operation. Washer 3
Then, the valve 42 is opened, the circulating water 20 is circulated by the pump 9, and brought into gas-liquid contact with the generated gas 11, whereby the gas components and unburned components contained in the generated gas 11 in trace amounts are wet-removed.

【0004】すなわち、洗浄器3は、起動時及びガス化
運転への切替時には、後続の脱硫設備の性能を低下させ
る酸性ガス成分を除去し、石炭ガス化運転中には未捕集
の微細なダスト等やアンモニア、ハロゲン化合物等の微
量ガス成分を除去したり、ガス温度を調節したりする等
の処理を主な目的としている。ガス化運転中は、発生ガ
ス11中に多く含まれているダスト等の固形分をガス洗
浄器で捕集し、デカンタ26により固形分を沈降させ、
排水弁22を調節しながら沈降した固形分を水とともに
抜き出し、適宣補給水が給水される。
That is, the scrubber 3 removes an acidic gas component that degrades the performance of the subsequent desulfurization equipment at the time of start-up and at the time of switching to the gasification operation, and removes uncollected fine particles during the coal gasification operation. The main purpose is to remove dust and other trace gas components such as ammonia and halogen compounds, and to adjust the gas temperature. During the gasification operation, a solid content such as dust contained in the generated gas 11 is collected by a gas scrubber, and the solid content is settled by the decanter 26.
The settled solids are extracted together with the water while adjusting the drain valve 22, and the appropriate replenishment water is supplied.

【0005】ここでは、ガス化炉1に接続された熱回収
ボイラ2、熱回収ボイラ2に接続されたサイクロン1
2、サイクロン12に接続されたフィルタ6、フィルタ
6に接続されたガスガス熱交換器19、ガスガス熱交換
器19に接続されたガス洗浄器3、その下方に配置され
ガス洗浄器3底部に管路38で接続されたデカンタ2
6、デカンタ26の下方に配置されその底部に排水弁2
2を介装した管路37で接続された排水処理設備23、
デカンタ26の底部に弁42を介装した管路27で吸込
側を接続された循環水ポンプ9、循環水ポンプ9の吐出
側とガス洗浄器3の上部を連通する管路36に介装され
た冷却器24、デカンタ26の上部に接続された補給水
供給手段21、ガス洗浄器3の上部に接続された脱硫塔
4、これらの機器を接続する管路及び弁を含んでなる一
連の装置を起動排ガス処理装置という。デカンタ26の
内部は底面から所定の高さまで延びる仕切壁で二つに区
画され、排水弁22を介装した管路37と弁42を介装
した管路27は互いに異なる区画に接続され、前記管路
38は管路37が接続された区画の上部になる位置に接
続され、補給水供給手段21は管路27が接続された区
画の上部になる位置に接続されている。つまり、管路3
8からデカンタ26に流入した循環水は管路37が接続
された区画に溜り(排水弁22は通常閉じられてい
る)、当該区画から溢れた循環水が前記仕切壁を超えて
管路27が接続された区画に流入するようになってい
る。
Here, a heat recovery boiler 2 connected to a gasification furnace 1 and a cyclone 1 connected to the heat recovery boiler 2
2, the filter 6 connected to the cyclone 12, the gas-gas heat exchanger 19 connected to the filter 6, the gas scrubber 3 connected to the gas-gas heat exchanger 19, and a pipe disposed under the gas scrubber 3 at the bottom. Decanter 2 connected by 38
6. A drain valve 2 is disposed below the decanter 26 and is provided at the bottom thereof.
Wastewater treatment equipment 23 connected by a pipeline 37 interposed
The circulating water pump 9, the suction side of which is connected to the bottom of the decanter 26 via a pipe 42 via a valve 42, and a pipe 36 that communicates the discharge side of the circulating water pump 9 with the upper part of the gas scrubber 3. A series of devices including a cooler 24, a make-up water supply means 21 connected to an upper part of a decanter 26, a desulfurization tower 4 connected to an upper part of the gas scrubber 3, and a pipe and a valve connecting these devices. Is referred to as a starting exhaust gas treatment device. The interior of the decanter 26 is divided into two by a partition wall extending from the bottom surface to a predetermined height, and a pipe 37 provided with the drain valve 22 and a pipe 27 provided with the valve 42 are connected to different sections from each other. The pipe 38 is connected to a position above the section to which the pipe 37 is connected, and the makeup water supply means 21 is connected to a position above the section to which the pipe 27 is connected. That is, pipeline 3
The circulating water flowing from 8 into the decanter 26 accumulates in the section to which the line 37 is connected (the drain valve 22 is normally closed), and the circulating water overflowing from the section exceeds the partition wall and the line 27 It flows into the connected compartment.

【0006】[0006]

【発明が解決しようとする課題】ところが、ガス化プラ
ントの起動時においては、油バーナ13の燃焼排ガスで
ある発生ガス11を洗浄器3に通して洗浄・冷却する際
に、当該発生ガス11中に含まれる窒素酸化物(NO2
及びNO3)や亜硫酸ガス(SO2及びSO3)及び炭酸
ガス(CO2)などが、圧力が高くなるにしたがって循
環水20に吸収され易くなり、循環水20が酸性水とな
り、ガス処理設備を構成する機器材料が著しく腐食する
問題があった。
However, when the gasification plant is started, when the generated gas 11 which is the combustion exhaust gas from the oil burner 13 is passed through the cleaning device 3 to be washed and cooled, the generated gas 11 Oxides (NO 2
And NO 3 ), sulfur dioxide (SO 2 and SO 3 ), carbon dioxide (CO 2 ), etc., are more likely to be absorbed by the circulating water 20 as the pressure increases, and the circulating water 20 becomes acidic water, and the gas treatment equipment However, there is a problem that the equipment material constituting the material significantly corrodes.

【0007】石炭ガスプラント起動時の発生ガス11
は、油バーナ13の高温燃焼排ガスであることから、一
般的に油中に含まれる硫黄分や高温燃焼によって生ずる
窒素酸化物(NO2、NO及びN2O)や亜硫酸ガス(S
2及びSO3)が炭酸ガス(CO2)とともに含まれて
いる。これらのガスは水に吸収されると、次式に従って
アニオンとプロトン(水素イオン)に解離することが知
られており、水が酸性を呈することから酸性ガスと呼ば
れている。
Emission gas 11 when starting coal gas plant
Is a high-temperature combustion exhaust gas from the oil burner 13, and is generally sulfur contained in oil or nitrogen oxides (NO 2 , NO and N 2 O) and sulfur dioxide (S 2 ) generated by high-temperature combustion.
O 2 and SO 3 ) are included together with carbon dioxide (CO 2 ). It is known that these gases dissociate into anions and protons (hydrogen ions) when absorbed by water according to the following formula, and are called acid gases because water exhibits acidity.

【0008】[0008]

【化1】 Embedded image

【0009】通常、常温・常圧のもとでは、これらの酸
性ガスは水にあまり多くは吸収されず、NO2では20
%程度、SO2では50%程度、CO2では0.1%以下
の吸収率である。しかしながら本システムのように、加
圧型の石炭ガスプラントを起動する際に発生する排ガス
では、圧力の上昇に伴い各酸性ガス成分の分圧が上昇
し、全圧力が1Mpa程度においては、NO2及びSO2
ではほぼ100%近く、CO2では1%程度が吸収され
るようになる。そのため上記に示した(式2,5,6,
7)に従って、水素イオン濃度が圧力の増加に従って増
加し、繰り返して洗浄に使用している循環水20のpH
は急激に低下する。
[0009] Normally, under the normal temperature and pressure, these acidic gases are not too many absorbed in water, the NO 2 20
%, About 50% for SO 2 and about 0.1% or less for CO 2 . However, as in this system, in the exhaust gas generated when starting a pressurized coal gas plant, the partial pressure of each acid gas component increases with the increase in pressure, and when the total pressure is about 1 MPa, NO 2 and SO 2
In this case, almost 100% is absorbed, and about 1% is absorbed by CO 2 . Therefore, as shown above (Equations 2, 5, 6,
According to 7), the hydrogen ion concentration increases as the pressure increases, and the pH of the circulating water 20 repeatedly used for washing is increased.
Drops sharply.

【0010】ガス処理装置を構成する鉄材料には、石炭
ガス化運転中の発生ガス11中に炭酸ガス、硫化水素
(H2S)及び塩化水素(HCl)等が含まれるため、
ある程度の腐食代を見込んで炭素鋼や低合金鋼等が用い
られる。図3に炭酸ガスを含む水溶液中での鉄の腐食速
度に及ぼす温度の影響を示す。常温〜50℃程度までは
弱酸性ないし弱アルカリ水溶液中でも硫化鉄(FeS
x)や酸化鉄(Fe23)が保護皮膜となり腐食速度は
比較的低い。ところが温度が高くなると、炭酸ガスによ
り100℃付近をピークとして腐食量は増大し、さらに
130℃以上の高温水中では炭酸鉄(FeCO3)等の
2価金属の炭酸塩の生成による保護皮膜により腐食が抑
制されることが知られている(参考文献例:材料と環
境、Vol.44(39),p.142−150,19
95)。しかしながら、例えば全圧力が3MPaで、1
00ppmのNO2及び5%のCO2を含む500m3
/hのガスを5m3の循環水で洗浄すると、循環水のp
Hは洗浄とともに低下し始めて、やがてpHが3以下の
強酸性を示すようになり、機器構成材料であるこれら鉄
材料は激しい腐食を起こし継続して運転することができ
なくなる。
The iron material constituting the gas treatment apparatus contains carbon dioxide, hydrogen sulfide (H 2 S), hydrogen chloride (HCl) and the like in the generated gas 11 during the coal gasification operation.
Carbon steel, low alloy steel, etc. are used in anticipation of a certain amount of corrosion. FIG. 3 shows the effect of temperature on the corrosion rate of iron in an aqueous solution containing carbon dioxide. From room temperature to about 50 ° C, iron sulfide (FeS
x) and iron oxide (Fe 2 O 3 ) serve as a protective film, and the corrosion rate is relatively low. However, as the temperature increases, the amount of corrosion increases due to carbon dioxide gas, peaking at around 100 ° C., and furthermore, in high-temperature water of 130 ° C. or more, corrosion occurs due to the formation of a bivalent metal carbonate such as iron carbonate (FeCO 3 ) due to a protective film. (Reference literature examples: Materials and Environment, Vol. 44 (39), p. 142-150, 19).
95). However, for example, if the total pressure is 3 MPa and 1
500 m 3 N with 00 ppm NO 2 and 5% CO 2
/ H gas is washed with 5 m 3 of circulating water.
H begins to decrease with washing, and eventually shows a strong acidity with a pH of 3 or less, and these iron materials, which are component materials of the device, are severely corroded and cannot be operated continuously.

【0011】本発明の目的は、石炭ガス化プラント起動
時の湿式ガス処理装置において、当該装置の構成材料で
ある鉄材料等の腐食を抑制することにある。
An object of the present invention is to suppress corrosion of a ferrous material or the like which is a constituent material of a wet gas processing apparatus at the time of starting a coal gasification plant.

【0012】[0012]

【課題を解決するための手段】上記目的は、発生ガスと
循環水を接触させるガス処理装置において、ガス洗浄器
で窒素酸化物、亜硫酸ガス、炭酸ガス等の酸性ガスを吸
収した循環水を減圧する減圧手段を設け、一旦循環水に
吸収された酸性ガス(炭酸ガス等)を再び気体として放
散させることにより達成される。減圧された循環水を再
度加圧する循環水加圧ポンプを設け、加圧された循環水
を循環水ポンプの吸込側に送りこむようにしてもよい。
SUMMARY OF THE INVENTION It is an object of the present invention to provide a gas treatment apparatus for bringing generated gas into contact with circulating water, in which a circulating water which has absorbed an acidic gas such as nitrogen oxide, sulfurous acid gas, carbon dioxide gas by a gas scrubber is depressurized. This is achieved by providing a decompression means for dispersing acid gas (carbon dioxide gas or the like) once absorbed in the circulating water as a gas. A circulating water pressurizing pump for pressurizing the depressurized circulating water again may be provided, and the pressurized circulating water may be sent to the suction side of the circulating water pump.

【0013】上記減圧手段に加え、酸性ガスを吸収した
循環水の水素イオン濃度(pH)を調整するpH調整手
段を設け、循環水の水素イオン濃度(pH)を6ないし
9の弱酸性ないし弱アルカリ性とするようにしてもよ
い。
In addition to the above-mentioned depressurizing means, a pH adjusting means for adjusting the hydrogen ion concentration (pH) of the circulating water having absorbed the acidic gas is provided, and the hydrogen ion concentration (pH) of the circulating water is adjusted to be 6 to 9 slightly acidic or weak. You may make it alkaline.

【0014】特にガス洗浄器3に導入される発生ガス1
1中の窒素酸化物及び亜硫酸ガス等の炭酸ガスを除く酸
性ガスの合計濃度が数10ppm以下で低い場合には、
減圧手段及び循環水ポンプのみを設けて、循環水20に
一旦吸収した炭酸ガス等を放散することで腐食を防止で
き、水素イオン濃度(pH)の調整手段は不要である。
また、ガス洗浄器3に導入される発生ガス11のガス温
度が約100℃以上で高い場合には、ガス洗浄器3の循
環水を冷却器により50℃以下に冷却するか、または加
熱器で130℃以上に加熱することで腐食を防止でき
る。一般にこの冷却器または加熱器には、図2の従来例
で示したガス化運転時に使用される冷却器24を兼用す
ることができる(加熱器として使用する場合は、蒸気等
の熱源が必要となる)。また、減圧手段としては、減圧
弁並びに減圧器を設けるか、あるいはガス化運転に用い
られるデカンタ等のドラムを減圧器として兼用し、その
前流に減圧弁を設けることで対処することができる。
In particular, the generated gas 1 introduced into the gas cleaning device 3
When the total concentration of the acid gas except for the carbon dioxide gas such as nitrogen oxide and sulfur dioxide gas in 1 is low at several tens ppm or less,
By providing only the pressure reducing means and the circulating water pump and dispersing the carbon dioxide gas once absorbed in the circulating water 20, corrosion can be prevented, and a means for adjusting the hydrogen ion concentration (pH) is unnecessary.
When the gas temperature of the generated gas 11 introduced into the gas cleaning device 3 is high at about 100 ° C. or higher, the circulating water of the gas cleaning device 3 is cooled to 50 ° C. or lower by a cooler, or Heating to 130 ° C. or higher can prevent corrosion. In general, this cooler or heater can also serve as the cooler 24 used during the gasification operation shown in the conventional example of FIG. 2 (when used as a heater, a heat source such as steam is required. Become). The pressure reducing means can be dealt with by providing a pressure reducing valve and a pressure reducing device, or by using a drum such as a decanter used for gasification operation as a pressure reducing device and providing a pressure reducing valve in front of the device.

【0015】本発明からなるガス処理装置を用いること
により、洗浄によって一旦吸収した酸性ガスを含む循環
水20を減圧して減圧器に抜き出す際に、おもに物理的
に吸収されている炭酸ガスを主成分とする酸性ガスの一
部が放散され、循環水のpHが上昇し、減圧による水分
蒸発により循環水温度が低下する。発生ガス11の温度
が約100℃以下で、且つNOx及びSOx濃度が数1
0ppmで低い場合には、減圧することで循環水のpH
は6程度の弱酸性で温度が50℃以下となり、ガス処理
装置を構成する安価な鉄材料等の腐食を抑制でき、加圧
循環ポンプにより循環水20を加圧して洗浄に用いるこ
とができるようになる。
By using the gas treatment apparatus according to the present invention, when the circulating water 20 containing the acidic gas once absorbed by the washing is reduced in pressure and extracted to the decompressor, mainly the carbon dioxide gas which is physically absorbed is mainly removed. A part of the acidic gas as a component is diffused, the pH of the circulating water rises, and the temperature of the circulating water decreases due to the evaporation of water under reduced pressure. The temperature of the generated gas 11 is about 100 ° C. or less, and the NOx and SOx concentrations are
If it is low at 0 ppm, reduce the pressure to reduce the pH of circulating water.
Has a weak acidity of about 6 and a temperature of 50 ° C. or lower, so that corrosion of inexpensive iron materials and the like constituting the gas treatment apparatus can be suppressed, and the circulating water 20 can be pressurized by the pressurized circulation pump and used for cleaning. become.

【0016】一方、発生ガス11中のNOx及びSOx
濃度が100ppm以上となる微量酸性ガス濃度の高い
場合には、循環水20に吸収されるNOx及びSOxガ
スが増加してNO3~及びSO3 2~濃度が高くなるが、p
H調整器を用いて上式の(2)、(5)により生じる水
素イオン(H+)を中和することで、pHを6ないし9
の弱酸性ないし弱アルカリ性とすることにより、ガス処
理装置の腐食が抑制される。また、発生ガス11の温度
が高く、約100℃以上である場合には、洗浄に伴い循
環水20の温度が50℃以上に上昇するため、冷却器に
より循環水温度を50℃以下にするか、または加熱器に
より130℃以上に加熱して酸化鉄(Fe23)あるい
は炭酸鉄(FeCO3)等の保護皮膜を形成させること
により材料の腐食が抑制できる。
On the other hand, NOx and SOx in the generated gas 11
When the concentration of the trace acid gas is higher than 100 ppm, the NOx and SOx gases absorbed in the circulating water 20 increase, and the NO 3 ~ and SO 3 2 ~ concentrations increase.
The pH is adjusted to 6 to 9 by neutralizing the hydrogen ions (H +) generated by the above formulas (2) and (5) using an H regulator.
By making it weakly acidic or weakly alkaline, corrosion of the gas treatment device is suppressed. Further, when the temperature of the generated gas 11 is high and is about 100 ° C. or more, the temperature of the circulating water 20 rises to 50 ° C. or more due to washing. Alternatively, corrosion of the material can be suppressed by forming a protective film such as iron oxide (Fe 2 O 3 ) or iron carbonate (FeCO 3 ) by heating to 130 ° C. or more by a heater.

【0017】なお、pH調整に用いるアルカリにはNa
OH、KOH等の水酸化アルカリ、不揮発性アミンまた
はアンモニア(NH3、NH4OH)を用いることが望ま
しい。Ca化合物等のアルカリ土類金属塩は、炭酸ガス
と反応し溶解度の低い炭酸塩を折出し易く、機器内部を
閉塞する原因となるため使用しないほうが望ましい。さ
らに、循環水20のpHを9以上のアルカリ性にする
と、ガス化運転に移行する際に発生ガス11中に含まれ
る炭酸ガス(CO2)を吸収し易くなり、燃料であるガ
ス流量が減少してGTを用いる発電システムには不適当
となるため、上記のpH範囲にあるいことが望ましい。
また、本発明によれば、一旦吸収された炭酸ガスを放散
させているため、起動後ガス化運転に切り替える際に、
石炭ガスにダストとして含まれるカルシウム化合物が、
循環水中に溶解している炭酸ガスと反応してスケールを
発生するという問題も軽減される効果が期待できる。
The alkali used for pH adjustment is Na.
It is desirable to use an alkali hydroxide such as OH or KOH, a nonvolatile amine or ammonia (NH 3 , NH 4 OH). It is desirable that alkaline earth metal salts such as Ca compounds are not used because they easily react with carbon dioxide gas to form carbonates having low solubility and cause clogging of equipment. Further, when the pH of the circulating water 20 is made alkaline at 9 or more, the carbon dioxide (CO 2 ) contained in the generated gas 11 is easily absorbed at the time of shifting to the gasification operation, and the flow rate of the gas as fuel decreases. Therefore, it is not suitable for a power generation system using GT, so that it is desirable to be in the above pH range.
According to the present invention, since the carbon dioxide gas once absorbed is diffused, when switching to the gasification operation after startup,
Calcium compounds contained as dust in coal gas,
The effect of reducing the problem of generating scale by reacting with carbon dioxide dissolved in circulating water can be expected.

【0018】[0018]

【発明の実施の形態】BEST MODE FOR CARRYING OUT THE INVENTION

〈実施例1〉石炭ガス化プラントにおける湿式のガス処
理装置に本発明を適用した第1の実施例を図1に示す。
本実施例が図2に示した従来例の構成と異なるのは、炭
酸ガス等を含む発生ガス11と接触させるガス洗浄器3
とデカンタ26と循環水ポンプ9及び冷却器24を含ん
でなる循環水系統において、デカンタ26と循環水ポン
プ9の吸込側を接続する管路27に介装された弁42の
上流側に減圧弁28を介して減圧器7が接続され、減圧
器7の底部に吸込側を接続した循環水加圧ポンプ41が
配置され、循環水加圧ポンプ41の吐出側と前記弁42
の下流側の管路27が管路35により連通され、管路3
5にアルカリ供給調整弁30を介装したアルカリ供給管
路29が接続され、デカンタ26の内部に水素イオン濃
度(pH)を測定するpH測定器33が配置され、pH
測定器33の出力を入力としてアルカリ供給調整弁30
の開度を制御するpH調整器34が設けられている点で
ある。減圧器7の上部(気相部)には、気体を放出する
手段が設けられている。アルカリ供給管路29、アルカ
リ供給調整弁30、及びpH調整器34をpH調整手段
とする。全圧力が3MPaまで加圧し、約100ppm
のNOx、約50ppmのSOx及び5%のCO2を含
む150〜300℃、1000m3N/hのガスを10
3の循環水で洗浄する場合を示した。
Embodiment 1 FIG. 1 shows a first embodiment in which the present invention is applied to a wet gas processing apparatus in a coal gasification plant.
This embodiment is different from the configuration of the conventional example shown in FIG. 2 in that the gas cleaning device 3 is brought into contact with the generated gas 11 containing carbon dioxide gas or the like.
And a decanter 26, a circulating water pump 9 and a cooler 24, a pressure reducing valve is provided upstream of a valve 42 interposed in a pipe line 27 connecting the decanter 26 and the suction side of the circulating water pump 9. The circulating water pressurizing pump 41 having a suction side connected to the bottom of the depressurizing device 7 is disposed at the bottom of the depressurizing device 7.
The pipe 27 on the downstream side of the pipe is communicated by the pipe 35 and the pipe 3
5 is connected to an alkali supply pipe line 29 interposed with an alkali supply adjustment valve 30, and a pH measuring device 33 for measuring a hydrogen ion concentration (pH) is disposed inside the decanter 26.
Using the output of the measuring device 33 as an input, the alkali supply regulating valve 30
The point is that a pH adjuster 34 for controlling the opening degree is provided. Above the decompressor 7 (gas phase part), means for releasing gas is provided. The alkali supply pipe line 29, the alkali supply adjustment valve 30, and the pH adjuster 34 serve as pH adjustment means. Total pressure is increased to 3MPa, about 100ppm
Of NOx, a 150~300 ℃, 1000m 3 N / h of gas containing SOx and 5% CO 2 for about 50 ppm 10
The case of washing with m 3 circulating water was shown.

【0019】本実施例による作用と効果について以下に
説明する。まず、起動時には油バーナ13の燃焼排ガス
をガス洗浄器3を通して循環水20により洗浄及び冷却
する。この操作により発生ガス11中に含まれる酸性ガ
スが循環水20に吸収され、pH測定器33は酸性を示
すようになる。そこで、弁42を閉じ減圧弁28を開い
て減圧器7に循環水20を導きながら、洗浄によって吸
収した酸性ガスを含む循環水を減圧すると、おもに物理
的に吸収されている炭酸ガスを主成分とする酸性ガスの
一部が減圧器7の中で循環水から放散される。
The operation and effect of this embodiment will be described below. First, at startup, the combustion exhaust gas of the oil burner 13 is washed and cooled by the circulating water 20 through the gas washer 3. By this operation, the acidic gas contained in the generated gas 11 is absorbed by the circulating water 20, and the pH meter 33 becomes acidic. Therefore, by closing the valve 42 and opening the pressure reducing valve 28 to guide the circulating water 20 to the pressure reducing device 7 and reducing the pressure of the circulating water containing the acidic gas absorbed by the washing, mainly the carbon dioxide gas physically absorbed is mainly contained. A part of the acid gas is released from the circulating water in the pressure reducer 7.

【0020】さらに、pH測定器33の出力信号を入力
とするpH調整器34の信号に従ってアルカリをアルカ
リ供給調整弁30で制御して管路35に供給し、循環水
加圧ポンプ41により減圧器7の循環水20を管路35
を経て循環水ポンプ9の吸込側に送りこんで再循環させ
ることで、NOx及びSOx等を吸収して生じる循環水
20中の水素イオン(H+)を減少させ、ガス洗浄器3
における循環水20のpHを6ないし9の弱酸性ないし
弱アルカリ性に維持することができる。また、発生ガス
11の顕熱により循環水の温度が50℃以上に上昇する
ため、冷却器24に冷却水25を供給することにより、
循環水20の温度を50℃以下に維持することができ
る。これによって、ガス処理装置を構成する鉄材料の腐
食が抑制される。
Further, alkali is controlled by an alkali supply adjusting valve 30 according to a signal from a pH adjuster 34 to which an output signal of the pH measuring device 33 is input, and is supplied to a pipeline 35. 7 circulating water 20
The hydrogen ions (H +) in the circulating water 20 generated by absorbing NOx and SOx and the like are reduced by being sent to the suction side of the circulating water pump 9 through the
The pH of the circulating water 20 can be maintained at a weakly acidic or weakly alkaline pH of 6 to 9. In addition, since the temperature of the circulating water rises to 50 ° C. or more due to the sensible heat of the generated gas 11, by supplying the cooling water 25 to the cooler 24,
The temperature of the circulating water 20 can be maintained at 50 ° C. or lower. This suppresses corrosion of the iron material constituting the gas processing device.

【0021】〈実施例2〉石炭ガス化プラントにおける
湿式のガス処理装置に本発明を適用した第2の実施例を
図4に示す。本実施例が前記図1に示す第1の実施例と
異なるのは、管路36に介装されていた冷却器24を省
き、管路35のアルカリ供給管路29の接続点より下流
側に加熱器32を介装した点である。本実施例は、循環
水ポンプ9及び循環水加圧ポンプ41を用いて循環水2
0をガス洗浄器3と減圧器7の間で循環し、約300℃
の高温の発生ガス11をガス洗浄器3に通して循環水2
0と接触させることにより、発生ガス11中に含まれる
微量酸性ガス等の不純物を除去する装置である。
Embodiment 2 FIG. 4 shows a second embodiment in which the present invention is applied to a wet gas processing apparatus in a coal gasification plant. This embodiment differs from the first embodiment shown in FIG. 1 in that the cooler 24 provided in the pipe 36 is omitted and the pipe 35 is located downstream of the connection point of the alkali supply pipe 29 in the pipe 35. The point is that the heater 32 is interposed. In the present embodiment, the circulating water pump 9 and the circulating water
0 is circulated between the gas scrubber 3 and the decompressor 7 at about 300 ° C.
High-temperature evolved gas 11 is passed through a gas scrubber 3 to circulate water 2
This is an apparatus for removing impurities such as a trace amount of acidic gas contained in the generated gas 11 by bringing the generated gas 11 into contact with zero.

【0022】本構成によれば、発生ガス11を洗浄、冷
却する際に、ガスの顕熱により循環水20の一部を蒸発
させるとともに、加熱器32に供給するスチーム31の
供給量を調節することにより、循環水20の温度を13
0℃以上に維持することができる。この例のように発生
ガス11の入口温度が300℃程度と高い場合には、そ
の顕熱により循環水20の温度を容易に120℃以上に
維持できるため、循環水20の加熱に補助的に要するス
チーム量は少量で良いことになる。なお、循環水20の
うち蒸発により失われる不足分は、補給水を供給する必
要がある。また、循環水20に吸収される酸性ガスによ
るpH低下を補うために、水素イオン濃度(pH)の測
定器33の値に応じてpH制御器34からアルカリ供給
調整弁30の開度(あるいは開閉)を指示し、循環水の
pHを6ないし9の弱酸性ないし弱アルカリ性に維持す
ることができる。この場合、循環水20の温度が約13
0℃以上と高いために、酸性ガスのうち、特に炭酸ガス
の吸収量が減少し、中和に要するアルカリの供給量は循
環水温度の低い実施例1に比べて極めて少なくなる。
According to this configuration, when the generated gas 11 is washed and cooled, a part of the circulating water 20 is evaporated by the sensible heat of the gas, and the supply amount of the steam 31 supplied to the heater 32 is adjusted. As a result, the temperature of the circulating water 20 becomes 13
It can be maintained at 0 ° C. or higher. When the inlet temperature of the generated gas 11 is as high as about 300 ° C. as in this example, the temperature of the circulating water 20 can be easily maintained at 120 ° C. or more by the sensible heat. A small amount of steam is required. The shortage of the circulating water 20 that is lost due to evaporation needs to be supplied with makeup water. Further, in order to compensate for a decrease in pH due to the acidic gas absorbed in the circulating water 20, the opening degree (or opening and closing) of the alkali supply adjusting valve 30 is controlled by the pH controller 34 in accordance with the value of the hydrogen ion concentration (pH) measuring instrument 33. ) To maintain the pH of the circulating water at a weakly acidic or slightly alkaline pH of 6 to 9. In this case, the temperature of the circulating water 20 is about 13
Since the temperature is as high as 0 ° C. or higher, the amount of absorption of the carbon dioxide gas among the acidic gases is particularly reduced, and the supply amount of the alkali required for neutralization is extremely small as compared with Example 1 in which the circulating water temperature is low.

【0023】〈実施例3〉石炭ガス化プラントにおける
湿式のガス処理装置に本発明を適用した第3の実施例を
図5に示す。本実施例が前記図2に示す従来技術と異な
るのは、ガス洗浄器3とデカンタ26を接続する管路3
8に減圧弁28が介装されていること、デカンタ26の
気相部に弁44を介装した管路39が接続されているこ
と、管路36の冷却器24の上流側にアルカリ供給調整
弁30を介装したアルカリ供給管路29が接続されてい
ること、デカンタ26の内部に水素イオン濃度(pH)
を測定するpH測定器33が配置されていること、pH
測定器33の出力を入力としてアルカリ供給調整弁30
の開度(あるいは開閉)を制御するpH調整器34が設
けられていることである。
Embodiment 3 FIG. 5 shows a third embodiment in which the present invention is applied to a wet gas processing apparatus in a coal gasification plant. This embodiment is different from the prior art shown in FIG. 2 in that a line 3 connecting the gas scrubber 3 and the decanter 26 is connected.
8, a pressure reducing valve 28 is interposed, a gas line portion of the decanter 26 is connected to a pipe 39 interposed with a valve 44, and an alkali supply adjustment is performed on the pipe 36 at an upstream side of the cooler 24. The alkali supply pipe line 29 interposed with the valve 30 is connected, and the hydrogen ion concentration (pH) is set inside the decanter 26.
That the pH measuring device 33 for measuring
Using the output of the measuring device 33 as an input, the alkali supply regulating valve 30
Is provided with a pH adjuster 34 for controlling the opening degree (or opening and closing).

【0024】本実施例では、第1の実施例における減圧
器7の代わりに、従来よりガス化運転に用いるデカンタ
26等のドラムを減圧器として兼用し、デカンタ26と
ガス洗浄器3からデカンタ26に循環水を導く管路38
に減圧弁28を設けてある。ガス化炉起動時には、減圧
弁28により循環水20を減圧し、減圧された循環水を
デカンタ26に導くことで、循環水20中に溶解してい
る酸性ガス8をデカンタ26内で放散させ、放散された
酸性ガス8を弁44を介して管路39から系外に放出す
る。また、pH調整器34はpH測定器33の出力を入
力としてアルカリ供給調整弁30の開度(あるいは開
閉)を制御してアルカリ供給管路29からアルカリを管
路36に供給し、循環水20のpHをアルカリで中和し
て調節することができる。
In this embodiment, instead of the decompressor 7 in the first embodiment, a drum such as a decanter 26 conventionally used for gasification operation is also used as a depressurizer, and the decanter 26 and the gas cleaning device 3 38 that leads circulating water to
Is provided with a pressure reducing valve 28. At the time of starting the gasification furnace, the circulating water 20 is depressurized by the pressure reducing valve 28, and the depressurized circulating water is guided to the decanter 26, so that the acidic gas 8 dissolved in the circulating water 20 is diffused in the decanter 26, The diffused acid gas 8 is discharged from the pipe 39 through the valve 44 to the outside of the system. The pH adjuster 34 receives the output of the pH meter 33 as an input, controls the opening (or opening and closing) of the alkali supply adjusting valve 30, supplies alkali from the alkali supply line 29 to the line 36, and supplies the circulating water 20. Can be adjusted by neutralizing with an alkali.

【0025】ガス化運転中には、従来通り減圧すること
なく循環水20をデカンタ26に導入しながら、循環水
ポンプ9により循環させてガスを洗浄すことができる。
本実施例によれば、減圧器を新たに設置する必要がな
く、低コストで経済的である。
During the gasification operation, the gas can be washed by circulating with the circulating water pump 9 while introducing the circulating water 20 into the decanter 26 without reducing the pressure as in the conventional case.
According to the present embodiment, there is no need to newly install a decompressor, and it is economical at low cost.

【0026】[0026]

【発明の効果】本発明によれば石炭ガス化プラント起動
時の湿式ガス処理装置における鉄材料等の腐食を抑制す
ることができるので、高価な材料を用いることなく、安
価で安定した起動運転のできるガス処理装置を提供でき
る。
According to the present invention, corrosion of iron materials and the like in a wet gas treatment apparatus at the time of starting a coal gasification plant can be suppressed, so that an inexpensive and stable start-up operation can be performed without using expensive materials. And a gas processing device capable of providing the same.

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

【図1】本発明に係る石炭ガス化プラントの起動排ガス
処理装置の第1の実施例を示す系統図である。
FIG. 1 is a system diagram showing a first embodiment of a starting exhaust gas treatment apparatus for a coal gasification plant according to the present invention.

【図2】石炭ガス化プラントの湿式ガス処理装置の従来
例を示す系統図である。
FIG. 2 is a system diagram showing a conventional example of a wet gas processing apparatus of a coal gasification plant.

【図3】炭酸ガス含有水溶液中の鉄の腐食量と温度の関
係を示すグラフである。
FIG. 3 is a graph showing the relationship between the amount of iron corrosion in an aqueous solution containing carbon dioxide and temperature.

【図4】本発明に係る石炭ガス化プラントの起動排ガス
処理装置の第2の実施例を示す系統図である。
FIG. 4 is a system diagram showing a second embodiment of a starting exhaust gas treatment apparatus for a coal gasification plant according to the present invention.

【図5】本発明に係る石炭ガス化プラントの起動排ガス
処理装置の第3の実施例を示す系統図である。
FIG. 5 is a system diagram showing a third embodiment of a starting exhaust gas treatment apparatus for a coal gasification plant according to the present invention.

【符号の説明】[Explanation of symbols]

1 ガス化炉 2 熱回収ボイラ 3 ガス洗浄器 4 脱硫塔 5 スラグ 6 フィルタ 7 減圧器 8 酸性ガス 9 循環水ポンプ 10 スラグホッパ 11 発生ガス 12 サイクロン 13 油バーナ 14 燃料油 15 空気 16 圧力調整弁 17 微粉炭 18 酸化剤 19 ガスガス熱交換器 20 循環水 21 補給水供給手段 22 排水弁 23 排水処理設備 24 冷却器 25 冷却水 26 デカンタ 29 アルカリ供給管路 30 アルカリ供給調整弁 31 スチーム 32 加熱器 33 pH測定器 34 pH制御器 35,36,37,38,39 管路 40 加熱器 41 循環水加圧ポンプ 42,43,44 弁 DESCRIPTION OF SYMBOLS 1 Gasification furnace 2 Heat recovery boiler 3 Gas scrubber 4 Desulfurization tower 5 Slag 6 Filter 7 Pressure reducer 8 Acid gas 9 Circulating water pump 10 Slag hopper 11 Generated gas 12 Cyclone 13 Oil burner 14 Fuel oil 15 Air 16 Pressure control valve 17 Fine powder Charcoal 18 Oxidant 19 Gas-gas heat exchanger 20 Circulating water 21 Make-up water supply means 22 Drain valve 23 Drainage treatment equipment 24 Cooler 25 Cooling water 26 Decanter 29 Alkaline supply line 30 Alkaline supply regulating valve 31 Steam 32 Heater 33 pH measurement Apparatus 34 pH controller 35, 36, 37, 38, 39 Pipe line 40 Heater 41 Circulating water pressurizing pump 42, 43, 44 Valve

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI F01K 23/10 F01N 3/08 Z F01N 3/08 F02C 3/28 F02C 3/28 7/00 Z 7/00 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification code FI F01K 23/10 F01N 3/08 Z F01N 3/08 F02C 3/28 F02C 3/28 7/00 Z 7/00

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 石炭ガス化プラント起動時の排ガスを水
と接触させることにより、ガスを洗浄して排ガス中に含
まれる一酸化炭素あるいは亜硫酸ガスなどの微量ガス成
分を除去するガス洗浄器及び該ガス洗浄器に供給される
水を循環させる循環水ポンプを含んでなるガス処理装置
において、前記ガス洗浄器でガス成分を吸収した循環水
を減圧する減圧手段と、該減圧された循環水を加圧して
前記循環水ポンプに送りこむ循環水加圧手段と、を設け
たことを特徴とする石炭ガス化プラントの起動排ガス処
理装置。
1. A gas washer for removing a trace gas component such as carbon monoxide or sulfur dioxide contained in an exhaust gas by contacting the exhaust gas at the time of starting a coal gasification plant with water to clean the gas. In a gas processing apparatus including a circulating water pump for circulating water supplied to a gas scrubber, a decompression means for decompressing circulating water having absorbed a gas component in the gas scrubber, and applying the depressurized circulating water to the gas processing apparatus. Circulating water pressurizing means for pressurizing and sending the circulating water to the circulating water pump.
【請求項2】 請求項1記載の石炭ガス化プラントの起
動排ガス処理装置において、前記ガス洗浄器でガス成分
を吸収した循環水のpHを6ないし9の弱酸性ないし弱
アルカリ性とすることのできるpH調整手段を設けたこ
とを特徴とする石炭ガス化プラントの起動排ガス処理装
置。
2. The starting exhaust gas treatment apparatus for a coal gasification plant according to claim 1, wherein the circulating water having absorbed the gas component in the gas scrubber can have a pH of 6 to 9 weakly acidic or weakly alkaline. A start-up exhaust gas treatment device for a coal gasification plant, comprising a pH adjusting means.
【請求項3】 請求項1または2に記載の石炭ガス化プ
ラントの起動排ガス処理装置において、循環水の温度を
50℃以下に冷却することのできる冷却器を付設したこ
とを特徴とする石炭ガス化プラントの起動排ガス処理装
置。
3. The coal gasification plant according to claim 1, further comprising a cooler capable of cooling the temperature of the circulating water to 50 ° C. or less. Start-up exhaust gas treatment equipment for chemical plants.
【請求項4】 請求項1または2に記載の石炭ガス化プ
ラントの起動排ガス処理装置において、循環水の温度を
少なくとも130℃に加熱することのできる加熱器を付
設したことを特徴とする石炭ガス化プラントの起動排ガ
ス処理装置。
4. A coal gasification plant starting exhaust gas treatment apparatus according to claim 1, further comprising a heater capable of heating the temperature of the circulating water to at least 130 ° C. Start-up exhaust gas treatment equipment for chemical plants.
【請求項5】 石炭ガス化プラント起動時の排ガスを水
と接触させることにより、ガスを洗浄して排ガス中に含
まれる一酸化炭素あるいは亜硫酸ガスなどの微量ガス成
分を除去するガス洗浄器及び該ガス洗浄器に供給される
水を循環させる循環水ポンプを含んでなるガス処理装置
において、前記ガス洗浄器でガス成分を吸収した循環水
を減圧する減圧手段と、前記ガス洗浄器でガス成分を吸
収した循環水のpHを6ないし9の弱酸性ないし弱アル
カリ性とすることのできるpH調整手段を設けたことを
特徴とする石炭ガス化プラントの起動排ガス処理装置。
5. A gas scrubber and a gas scrubber for removing a trace gas component such as carbon monoxide or sulfur dioxide contained in an exhaust gas by contacting the exhaust gas at the start of a coal gasification plant with water to clean the gas. In a gas treatment apparatus including a circulating water pump that circulates water supplied to a gas scrubber, a decompression unit that decompresses circulating water having absorbed a gas component in the gas scrubber, and a gas component in the gas scrubber. A start-up exhaust gas treatment apparatus for a coal gasification plant, comprising a pH adjusting means capable of adjusting the pH of absorbed circulating water to a weakly acidic or weakly alkaline of 6 to 9.
【請求項6】 請求項2乃至5のいずれかに記載の石炭
ガス化プラントの起動排ガス処理装置において、前記ガ
ス洗浄器でガス成分を吸収した循環水のpHを検出する
pH測定器を有してなり、前記pH調整手段は前記pH
測定器の出力を入力として動作するように構成されてい
ることを特徴とする石炭ガス化プラントの起動排ガス処
理装置。
6. The starting exhaust gas treatment apparatus for a coal gasification plant according to any one of claims 2 to 5, further comprising a pH measuring device for detecting a pH of circulating water having absorbed a gas component in the gas cleaning device. Wherein the pH adjusting means
A starting exhaust gas treatment device for a coal gasification plant, which is configured to operate using an output of a measuring device as an input.
JP29993297A 1997-10-31 1997-10-31 Pressurized coal gasification plant Expired - Lifetime JP3665919B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP29993297A JP3665919B2 (en) 1997-10-31 1997-10-31 Pressurized coal gasification plant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29993297A JP3665919B2 (en) 1997-10-31 1997-10-31 Pressurized coal gasification plant

Publications (2)

Publication Number Publication Date
JPH11128659A true JPH11128659A (en) 1999-05-18
JP3665919B2 JP3665919B2 (en) 2005-06-29

Family

ID=17878684

Family Applications (1)

Application Number Title Priority Date Filing Date
JP29993297A Expired - Lifetime JP3665919B2 (en) 1997-10-31 1997-10-31 Pressurized coal gasification plant

Country Status (1)

Country Link
JP (1) JP3665919B2 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100470658B1 (en) * 2000-12-21 2005-03-07 주식회사 포스코 A facilities for refining waste acid and its refining method
JP2010163621A (en) * 2010-03-05 2010-07-29 Mitsubishi Heavy Ind Ltd Gas treatment method in gasification facility and gasification facility
JP2010215812A (en) * 2009-03-17 2010-09-30 Yanmar Co Ltd Gasification apparatus
CN104023818A (en) * 2011-10-05 2014-09-03 C·A·赫尔南德兹·奥尔韦拉 System for trapping polluting emissions
CN111978993A (en) * 2020-07-17 2020-11-24 新奥科技发展有限公司 Pressure reducing device and coke discharging system

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100470658B1 (en) * 2000-12-21 2005-03-07 주식회사 포스코 A facilities for refining waste acid and its refining method
JP2010215812A (en) * 2009-03-17 2010-09-30 Yanmar Co Ltd Gasification apparatus
JP2010163621A (en) * 2010-03-05 2010-07-29 Mitsubishi Heavy Ind Ltd Gas treatment method in gasification facility and gasification facility
CN104023818A (en) * 2011-10-05 2014-09-03 C·A·赫尔南德兹·奥尔韦拉 System for trapping polluting emissions
CN111978993A (en) * 2020-07-17 2020-11-24 新奥科技发展有限公司 Pressure reducing device and coke discharging system

Also Published As

Publication number Publication date
JP3665919B2 (en) 2005-06-29

Similar Documents

Publication Publication Date Title
TWI276460B (en) Exhaust smoke-processing system
JP5350996B2 (en) Oxygen combustion system exhaust gas treatment equipment
TWI488682B (en) Seawater desulfurization system and power generation system
WO2014103682A1 (en) Exhaust gas processing equipment and gas turbine power generation system using same
JP2012179521A (en) Seawater flue-gas desulfurization system, and power generating system
JPH1157397A (en) Gas purifying method
JP2019076809A (en) Reclaiming apparatus and reclaiming method
JP3665919B2 (en) Pressurized coal gasification plant
JP3831435B2 (en) Gas purification equipment
JP5161906B2 (en) Gas treatment method and gasification equipment in gasification equipment
JP3813835B2 (en) Water recovery system from combustion exhaust gas
JPS5990617A (en) Treatment of waste gas
JPH0459022A (en) Desulfurizing method by spraying fine powder desulfurizing agent to waste combustion gas
JPH11104451A (en) Purification of gas and apparatus for purifying gas
JPH1119468A (en) Gas purification
JP4658350B2 (en) Method and apparatus for reducing sulfur compounds
JP4508307B2 (en) Gas treatment method and gasification equipment in gasification equipment
JP2000053980A (en) Purification of gas
WO2000043658A1 (en) Gas turbine generating method and generator
JPH0693274A (en) Treatment of waste liquor from desulfurization and decynization of coke oven gas
WO2000048711A1 (en) Gas cooling device, gas treatment device, and boiler equipment
JP2001123184A (en) Method for gas purification
JP5979672B2 (en) Thermal power plant operation method
EP3300790A1 (en) Method and device for treating wastewater from gas-cooler cleaning
JP4644912B2 (en) Control method of sintering machine exhaust gas desulfurization equipment

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20040319

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20041105

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20041109

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20050111

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20050308

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20050323

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090415

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100415

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110415

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110415

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120415

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130415

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130415

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140415

Year of fee payment: 9

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313111

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

EXPY Cancellation because of completion of term