JPH0781152B2 - Operation method of coal gasification combined plant - Google Patents
Operation method of coal gasification combined plantInfo
- Publication number
- JPH0781152B2 JPH0781152B2 JP62231145A JP23114587A JPH0781152B2 JP H0781152 B2 JPH0781152 B2 JP H0781152B2 JP 62231145 A JP62231145 A JP 62231145A JP 23114587 A JP23114587 A JP 23114587A JP H0781152 B2 JPH0781152 B2 JP H0781152B2
- Authority
- JP
- Japan
- Prior art keywords
- gas
- coal gasification
- gas turbine
- exhaust gas
- combined plant
- 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
- 239000003245 coal Substances 0.000 title claims description 24
- 238000002309 gasification Methods 0.000 title claims description 23
- 238000000034 method Methods 0.000 title claims description 5
- 239000007789 gas Substances 0.000 claims description 65
- 238000010521 absorption reaction Methods 0.000 claims description 22
- 238000006477 desulfuration reaction Methods 0.000 claims description 14
- 230000023556 desulfurization Effects 0.000 claims description 14
- 229910052717 sulfur Inorganic materials 0.000 claims description 10
- 239000007788 liquid Substances 0.000 claims description 9
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 8
- 238000002485 combustion reaction Methods 0.000 claims description 7
- 229910052757 nitrogen Inorganic materials 0.000 claims description 5
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 4
- 239000011593 sulfur Substances 0.000 claims description 4
- 238000011084 recovery Methods 0.000 description 6
- 230000000694 effects Effects 0.000 description 4
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 239000000809 air pollutant Substances 0.000 description 2
- 231100001243 air pollutant Toxicity 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000006866 deterioration Effects 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- XTHFKEDIFFGKHM-UHFFFAOYSA-N Dimethoxyethane Chemical compound COCCOC XTHFKEDIFFGKHM-UHFFFAOYSA-N 0.000 description 1
- 230000002745 absorbent Effects 0.000 description 1
- 239000002250 absorbent Substances 0.000 description 1
- 239000006096 absorbing agent Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- MTHSVFCYNBDYFN-UHFFFAOYSA-N diethylene glycol Chemical compound OCCOCCO MTHSVFCYNBDYFN-UHFFFAOYSA-N 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 238000011017 operating method Methods 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は石炭ガス化コンバインドプラントにおいて排ガ
ス中のNOX及びSOXを低減させる運転方法に関する。TECHNICAL FIELD The present invention relates to an operating method for reducing NO X and SO X in exhaust gas in a coal gasification combined plant.
第2図は、従来の石炭ガス化コンバインドプラントの系
統図でバンカに貯えられた石炭1はミル2に供給され微
粉に粉砕される。微粉炭は空気等のガス化剤と共にガス
化炉3内に供給され、ガス化反応を行なう。ガス化反応
により生成したガス中には、主成分であるCO,H2の他微
量のS分(H2S,COS)、N分(NH3,HCN)が含まれてい
る。未反応チャー及び生成ガスは顕熱回収熱交換器4に
導入されて、こゝでその温度が1000℃→400℃まで冷却
され熱回収が行われる。次に粗脱塵装置5により生成ガ
ス中の未反応チャーを除去する。除去された未反応チャ
ーはチャー回収ライン6を通り補助燃料としてガス化炉
3へ供給される。一方脱塵された生成ガスは、乾式脱硫
装置7に入り、S分は燃焼してSOXとなり、その約90%
が脱硫された後、精密脱塵装置8で完全に除塵され、ガ
スタービン9へ供給される。ガスタービン9内で燃焼さ
れた排ガスは外部から供給されたNH3とともに脱硝装置1
0において、燃焼排ガス中のNOXを脱硝した後排ガスボイ
ラ11、煙突12を経て大気中へ排出される。FIG. 2 is a system diagram of a conventional coal gasification combined plant, in which a coal 1 stored in a bunker is supplied to a mill 2 and pulverized into fine powder. The pulverized coal is supplied into the gasification furnace 3 together with a gasifying agent such as air to carry out a gasification reaction. The gas produced by the gasification reaction contains a small amount of S content (H 2 S, COS) and N content (NH 3 , HCN) in addition to the main components CO and H 2 . The unreacted char and the produced gas are introduced into the sensible heat recovery heat exchanger 4, where the temperature is cooled from 1000 ° C to 400 ° C and heat is recovered. Next, the unreacted char in the produced gas is removed by the coarse dedusting device 5. The removed unreacted char passes through the char recovery line 6 and is supplied to the gasification furnace 3 as auxiliary fuel. On the other hand, the degassed product gas enters the dry desulfurization unit 7, and the S content is burned to SO X , about 90% of which
After being desulfurized, the dust is completely removed by the precision dust removing device 8 and supplied to the gas turbine 9. Exhaust gas burned in the gas turbine 9 together with NH 3 supplied from the outside denitration device 1
At 0, NO x in the combustion exhaust gas is denitrated and then discharged to the atmosphere through the exhaust gas boiler 11 and the chimney 12.
上記従来の石炭ガス化コンバインドプラントにおいて
は、燃焼排ガス中の大気汚染物質であるSOX及びNOXの低
減効果はS分については90%、N分については脱硝装置
として乾式脱硫装置を用いて80%の効率であり完全では
ない。また上記プラントにおいて乾式脱硫装置7に代え
て湿式の脱硫装置を用いた場合には、脱硫効果を98%程
度迄向上させることができるが、熱効率の低下及び吸収
液の劣化が早い等問題点が多い。In the above conventional coal gasification combined plant, the effect of reducing SO X and NO X which are air pollutants in combustion exhaust gas is 90% for S content and 80% for N content by using a dry desulfurization device as a denitration device. % Efficiency, not perfect. When a wet desulfurization device is used instead of the dry desulfurization device 7 in the above plant, the desulfurization effect can be improved up to about 98%, but there are problems such as reduction in thermal efficiency and rapid deterioration of absorption liquid. Many.
従って、従来の石炭ガス化コンバインドプランにおい
て、含有硫黄分、含有窒素分の多い石炭をガス化した場
合、排ガス中のSOX,NOXが多量に大気中に排出される可
能性があり、また脱硫効果を上げるために湿式脱硫装置
を用いる場合には熱効率の低下等の問題があった。Therefore, in the conventional coal gasification combined plan, when coal containing a large amount of sulfur content and nitrogen content is gasified, a large amount of SO X , NO X in the exhaust gas may be emitted into the atmosphere, and When a wet desulfurization device is used to improve the desulfurization effect, there are problems such as a decrease in thermal efficiency.
本発明はこれらの問題点を解決しようとするものであ
る。The present invention seeks to solve these problems.
本発明は石炭ガス化炉、乾式脱硫装置及びガスタービン
を備えた石炭ガス化コンバインドプラントにおいて、上
記石炭ガス化炉で生成されたガスの一部を石炭ガス化炉
とガスタービンの間から抜き取って湿式吸収装置に導入
してH2S,NH3等のガス中の硫黄分と窒素分を除去した後
上記ガスタービンに供給し、上記湿式吸収装置で吸収液
中のNH3を補集して上記ガスタービンからの燃焼排ガス
と共に脱硝装置に導入して処理することにより、排ガス
中のSOX、及びNOXを低減するようにした。The present invention is a coal gasification combined plant equipped with a coal gasification furnace, a dry desulfurization apparatus and a gas turbine, in which a part of the gas generated in the coal gasification furnace is extracted from between the coal gasification furnace and the gas turbine. After being introduced into the wet absorption device to remove the sulfur and nitrogen components in the gas such as H 2 S and NH 3 , it is supplied to the above gas turbine, and the above wet absorption device collects NH 3 in the absorption liquid. The SO x and NO x in the exhaust gas were reduced by introducing them into the denitration device together with the combustion exhaust gas from the gas turbine and treating them.
本発明では、石炭ガス化炉で生成したガスタービンに供
給されるガスの一部を抜き取り、湿式吸収装置により処
理を行ない、大気汚染物質となるH2S,NH3等を除去した
後ガスタービンに供給する。このため、ガスタービンの
燃焼排ガス中のSOX及びNOXが低減する。また、吸収液中
のNH3を湿式吸収装置においてストリッピングして吸収
液から分離し、これをガスタービンからの燃焼排ガスと
共に脱硝装置で処理することにより、吸収液に吸収され
たNH3を有効に利用して排ガス中のSOX,NOXの低減を行な
う。In the present invention, a part of the gas supplied to the gas turbine produced in the coal gasification furnace is extracted, processed by a wet absorption device, and H 2 S, NH 3 and the like that become air pollutants are removed and then the gas turbine Supply to. Therefore, SO X and NO X in the combustion exhaust gas of the gas turbine are reduced. In addition, NH 3 in the absorption liquid is stripped in the wet absorption device to separate it from the absorption liquid, and this is treated together with the combustion exhaust gas from the gas turbine in the denitrification device to make the NH 3 absorbed in the absorption liquid effective. To reduce SO X and NO X in exhaust gas.
更に本発明では、乾式脱硫装置を用いているので、プラ
ントの熱効率の低下等の問題も発生しない。Further, in the present invention, since the dry desulfurization device is used, problems such as reduction in thermal efficiency of the plant do not occur.
本発明の一実施例を第1図によって説明する。第1図に
おいて、バンカに貯えられた石炭1、ミル2、ガス化炉
3、顕熱回収熱交換器4、粗脱塵装置5、チヤー回収ラ
イン6、乾式脱硫装置7、精密脱塵装置8、ガスタービ
ン9、脱硝装置10、排ガスボイラ11、及び煙突12は第2
図に示す従来ものと同様であり、その説明を省略する。An embodiment of the present invention will be described with reference to FIG. In FIG. 1, coal 1 stored in a bunker, a mill 2, a gasification furnace 3, a sensible heat recovery heat exchanger 4, a rough dedusting device 5, a chair recovery line 6, a dry desulfurization device 7, a precision dedusting device 8 The gas turbine 9, the denitration device 10, the exhaust gas boiler 11, and the chimney 12 are second
Since it is similar to the conventional one shown in the figure, its explanation is omitted.
本実施例においては、粗脱塵を終えた生成ガスの一部を
バイパスライン13を用いて湿式吸収装置14に導入し、同
湿式吸収装置14において生成ガス中のH2S及びNH3等の硫
黄分と窒素分を吸収液に吸収する。吸収後の生成ガスは
バイパスライン15を通って、湿式吸収装置14からガスタ
ービン9に供給され同ガスタービン9で燃焼される。一
方湿式吸収装置14においては、吸収液からのNH3のスト
リッピングを行ない、排出されたNH3をNH3供給ライン16
を経て、ガスタービン9の燃焼排ガスと共に脱硝装置10
に供給する。この際供給ライン16から供給されるNH3の
量が不足するときには、これを補充するために、図示の
ように別にNH3が供給される。排ガスボイラ11と煙突12
間の配管にはSOX計17a及びNOX計17bが配設され、これら
を用いて排ガス中のSOX及びNOX濃度を検知し、これに基
づいてバイパスライン15に介装されたバルブ15aを制御
することによって湿式吸収装置14からガスタービン9に
供給されるガスのバイパス流量を制御することにより、
SOX,NOXの効果的な低減を計る。生成ガスからのH2S,NH3
の除去法としては、吸収液にメタノールを用いたレクチ
ゾール法、グリコールエーテルを用いたセレクゾール法
等を用いることができる。In the present embodiment, a part of the product gas that has undergone rough dedusting is introduced into the wet absorption device 14 using the bypass line 13, and in the wet absorption device 14, H 2 S and NH 3 etc. in the product gas are introduced. Absorbs sulfur and nitrogen in the absorbent. The generated gas after absorption is supplied to the gas turbine 9 from the wet absorption device 14 through the bypass line 15 and burned in the gas turbine 9. On the other hand, in the wet absorber 14 performs stripping of the NH 3 from the absorption liquid, NH 3 supply line 16 NH 3 is discharged
Through the exhaust gas of the gas turbine 9 and the denitration device 10
Supply to. At this time, when the amount of NH 3 supplied from the supply line 16 is insufficient, NH 3 is separately supplied as shown in the figure to replenish it. Exhaust gas boiler 11 and chimney 12
A SO X meter 17a and a NO X meter 17b are arranged in the pipe between them, and the SO X and NO X concentrations in the exhaust gas are detected by using these, and based on this, the valve 15a installed in the bypass line 15a. By controlling the bypass flow rate of the gas supplied from the wet absorption device 14 to the gas turbine 9 by controlling the
Measure effective reduction of SO X and NO X. H 2 S, NH 3 from generated gas
As a method for removing the above, a rectizole method using methanol as an absorbing solution, a selexol method using glycol ether, or the like can be used.
本実施例では以上の通り、石炭ガス化炉で生成されるガ
スの一部を抜き取って湿式吸収装置14に導き、こゝでH2
S,NH3等のS分及びN分を除去した上でガスタービン9
に供給して燃焼を行うために、燃焼排ガス中のSOX及びN
OXを低減させることができる。In this embodiment, as described above, a part of the gas generated in the coal gasification furnace is extracted and guided to the wet absorption device 14, where the H 2
After removing S and N components such as S and NH 3 , the gas turbine 9
The SO X and N in the flue gas to supply the
O X can be reduced.
また、湿式吸収装置14ではストリッピングを行って、NH
3を吸収液から分離し、これを燃焼排ガスと共に脱硝装
置で処理することによって、生成ガス中に含まれるNH3
を有効に脱硝作用に利用することができる。Further, in the wet absorption device 14, stripping is performed to
NH 3 contained in the produced gas by separating 3 from the absorbing liquid and treating this with the combustion exhaust gas in a denitration device.
Can be effectively used for denitration.
更に、脱硫装置としては乾式脱硫装置7を用いているの
で、熱効率の低下、吸収液の劣化等の問題が起ることも
ない。Further, since the dry desulfurization device 7 is used as the desulfurization device, problems such as a decrease in thermal efficiency and deterioration of the absorbing liquid do not occur.
また更に、脱硝後の排ガス中のSOX,NOXの濃度を検出し
てこれによってバイパスして湿式吸収装置14からガスタ
ービン9に供給されるバイパス流量を制御することによ
って、SOX,NOXの低減及びプラント効率上最適な運転を
行うことができる。Furthermore, by detecting the concentrations of SO X and NO X in the exhaust gas after denitration and by-passing by this to control the bypass flow rate supplied from the wet absorption device 14 to the gas turbine 9, the SO X and NO X are controlled. It is possible to perform optimum operation in terms of the reduction of power consumption and plant efficiency.
第1図の構成(但し排ガスボイラを除く)をもつ基礎実
験装置(石炭処理量100kg/H)を用いたテストで排ガス
中のSOX、及びNOX濃度を計測したところ第1表の結果を
得た。なお、第1表中の従来例は第2図に示される構成
の装置によるテスト結果を示す。The SO X and NO X concentrations in the exhaust gas were measured in a test using a basic experimental device (coal throughput of 100 kg / H) having the configuration of Fig. 1 (excluding the exhaust gas boiler), and the results in Table 1 were obtained. Obtained. In addition, the conventional example in Table 1 shows the test result by the apparatus having the configuration shown in FIG.
これによれば、本発明によって排ガス中のSOX及びNOXの
濃度を著しく低減させることができることが確認され
た。According to this, it was confirmed that the present invention can significantly reduce the concentrations of SO X and NO X in the exhaust gas.
〔発明の効果〕 以上説明したように、本発明によれば石炭ガス化炉で生
成されるガスを燃焼させるガスタービンの排ガス中のNO
X及びSOXを低減させることができ、かつ、上記生成ガス
中のNH3を脱硝に有効に使用することができる。 [Effects of the Invention] As described above, according to the present invention, NO in exhaust gas of a gas turbine that burns gas produced in a coal gasifier
X and SO X can be reduced, and NH 3 in the produced gas can be effectively used for denitration.
また、プラントの全体の熱効率を下げることがなくプラ
ントを運転することができる。In addition, the plant can be operated without reducing the overall thermal efficiency of the plant.
第1図は本発明を実施するための装置の系統図、第2図
は従来の石炭ガス化コンバインドプラントの系統図であ
る。 1……石炭、2……ミル、 3……ガス化炉、4……顕熱回収熱交換器、 5……粗脱塵装置、6……チャー回収ライン、 7……乾式脱硫装置、8……精密脱塵装置、 9……ガスタービン、10……脱硝装置、 11……排ガスボイラ、12……煙突、 13……バイパスライン、 14……湿式吸収装置、15……バイパスライン、 15a……バルブ、16……NH3供給ライン、 17a……SOX計、17b……NOX計FIG. 1 is a system diagram of an apparatus for carrying out the present invention, and FIG. 2 is a system diagram of a conventional coal gasification combined plant. 1 ... Coal, 2 ... Mill, 3 ... Gasification furnace, 4 ... Sensible heat recovery heat exchanger, 5 ... Coarse dedusting device, 6 ... Char recovery line, 7 ... Dry desulfurization device, 8 …… Precision dedusting device, 9 …… Gas turbine, 10 …… Denitration device, 11 …… Exhaust gas boiler, 12 …… Chimney, 13 …… Bypass line, 14 …… Wet absorption device, 15 …… Bypass line, 15a …… Valve, 16 …… NH 3 supply line, 17a …… SO X meter, 17b …… NO X meter
フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 // B01D 53/14 C 53/60 53/77 Continuation of the front page (51) Int.Cl. 6 Identification number Office reference number FI technical display location // B01D 53/14 C 53/60 53/77
Claims (1)
ビンを備えた石炭ガス化コンバインドプラントにおい
て、上記石炭ガス化炉で生成されガスタービンに供給さ
れるガスの一部を石炭ガス化炉とガスタービンの間から
抜き取って湿式吸収装置に導入してガス中の硫黄分と窒
素分を除去した後上記ガスタービンに供給すると共に、
上記湿式吸収装置で吸収液中のNH3を補集して上記ガス
タービンからの燃焼排ガスと共に脱硝装置に導入して処
理することを特徴とする石炭ガス化コンバインドプラン
トの運転方法。1. In a coal gasification combined plant equipped with a coal gasification furnace, a dry desulfurization apparatus and a gas turbine, a part of the gas produced in the coal gasification furnace and supplied to the gas turbine is used as a coal gasification furnace. Withdrawing from between the gas turbine and introducing it into the wet absorption device to remove the sulfur content and nitrogen content in the gas and then supplying it to the gas turbine,
A method for operating a coal gasification combined plant, characterized in that NH 3 in the absorption liquid is collected by the wet absorption device and introduced into a denitration device together with the combustion exhaust gas from the gas turbine for treatment.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP62231145A JPH0781152B2 (en) | 1987-09-17 | 1987-09-17 | Operation method of coal gasification combined plant |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP62231145A JPH0781152B2 (en) | 1987-09-17 | 1987-09-17 | Operation method of coal gasification combined plant |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6475586A JPS6475586A (en) | 1989-03-22 |
| JPH0781152B2 true JPH0781152B2 (en) | 1995-08-30 |
Family
ID=16918995
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP62231145A Expired - Fee Related JPH0781152B2 (en) | 1987-09-17 | 1987-09-17 | Operation method of coal gasification combined plant |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0781152B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| AU2010316579B2 (en) * | 2009-11-09 | 2013-06-13 | Ihi Corporation | Method and device for treating ammonia in gasification system |
-
1987
- 1987-09-17 JP JP62231145A patent/JPH0781152B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6475586A (en) | 1989-03-22 |
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