JPH01318082A - Method for decreasing ammonia concentration of gas from coal gasification - Google Patents

Method for decreasing ammonia concentration of gas from coal gasification

Info

Publication number
JPH01318082A
JPH01318082A JP63148288A JP14828888A JPH01318082A JP H01318082 A JPH01318082 A JP H01318082A JP 63148288 A JP63148288 A JP 63148288A JP 14828888 A JP14828888 A JP 14828888A JP H01318082 A JPH01318082 A JP H01318082A
Authority
JP
Japan
Prior art keywords
gas
coal gasification
catalyst layer
ammonia
concentration
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
JP63148288A
Other languages
Japanese (ja)
Other versions
JPH083105B2 (en
Inventor
Atsushi Morii
守井 淳
Osamu Naito
治 内藤
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 JP63148288A priority Critical patent/JPH083105B2/en
Publication of JPH01318082A publication Critical patent/JPH01318082A/en
Publication of JPH083105B2 publication Critical patent/JPH083105B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/52Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts

Landscapes

  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

PURPOSE:To decrease the NOX concentration of a waste gas by decreasing the NH3 concentration of a gas from coal gasification by providing a specified catalyst layer in a passage for feeding the gas to a burner and injecting a nitrogen oxide and an oxygen-containing gas into the passage on an upstream side of the catalyst layer. CONSTITUTION:A reaction 6 packed with a selective catalytic reduction/ denitrification catalyst in which ammonia is used as a reductant is provided at a position of a gas temperature of 200-500 deg.C of a passage 2 for feeding a gas produced from coal gasification in a coal gasification oven 1 to a gas turbine burner 3; a nitrogen oxide and an oxygen-containing gas are fed from an injector 5 on the upstream side of the reactor 6 to decrease the NH3 concentration of the coal gasification gas and to thereby decrease the NOX concentration of the gas discharged from a gas turbine waste gas pipe 4.

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炉で発生するガス中に含まれるアン
モニアを低減させる方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for reducing ammonia contained in gas generated in a coal gasifier.

〔従来の技術] 石炭ガス化炉とガスタービンを組み合せた従来の設備の
一態様lr:第3図によって説明する。
[Prior Art] One aspect of a conventional facility that combines a coal gasification furnace and a gas turbine will be explained with reference to FIG.

石炭ガス化炉1での反応は、還元雰囲気での反応である
ため、ガスタービン燃焼器3への経路2中の石炭ガス化
炉発生ガスはアンモニア< NHI )を多量に含んで
いる。このlaH,を多量に含んだガスをガスタービン
燃料として投入した場合、ガスタービン燃焼器3でNu
、はJIIOXになるためガスタービン排ガス配管4の
排ガス中のNOX 4度は非常に高くなり、Nowの櫨
境排出規制上好ましくない。
Since the reaction in the coal gasifier 1 is a reaction in a reducing atmosphere, the gas generated from the coal gasifier in the path 2 to the gas turbine combustor 3 contains a large amount of ammonia <NHI. When gas containing a large amount of laH, is input as gas turbine fuel, the gas turbine combustor 3
, is JIIOX, so the NOX level in the exhaust gas from the gas turbine exhaust gas piping 4 becomes extremely high, which is unfavorable in terms of the Now's forest boundary emission regulations.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

本発明は上記技術水準に鑑み、石炭ガス化ガス中のPi
n、を低減する合目的な方法を提供しようとするもので
ある。
In view of the above-mentioned technical level, the present invention has been made to solve the problem of Pi in coal gasification gas.
The aim is to provide a purposeful method for reducing n.

〔課題を解決するための手段] 本発明は石炭ガス化炉で発生する石炭ガス化ガスの燃焼
器への供給経路に、ガス温度200〜500℃の範囲内
の経路にアンモニア?還元剤とする選択接触還元脱硝触
媒層を設け、該触媒層の前流側に窒素酸化物及び酸素含
有ガスを注入することを特徴とする石炭ガス化ガス中の
アンモニアの低減法である。
[Means for Solving the Problems] The present invention provides a supply route for coal gasification gas generated in a coal gasification furnace to a combustor, in which ammonia is added to a route within a gas temperature range of 200 to 500°C. This is a method for reducing ammonia in coal gasification gas, which is characterized by providing a selective catalytic reduction denitrification catalyst layer as a reducing agent and injecting nitrogen oxide and oxygen-containing gas to the upstream side of the catalyst layer.

本発明において使用さnるアンモニアを還元剤とする選
択接触還元脱硝触媒としては、一般燃焼排ガス中のNO
Kをアンモニアを還元剤として選択的に除去する際に使
用さ几る脱硝触媒であれば任意のものが使用し得る。例
えばT10゜担体とし、活性成分としてv、W、MOl
Fe、Cu  などの酸化物を担持したものが使用でき
る。
The selective catalytic reduction denitrification catalyst using ammonia as a reducing agent used in the present invention is capable of reducing NO in general combustion exhaust gas.
Any denitrification catalyst that can be used to selectively remove K using ammonia as a reducing agent can be used. For example, T10° carrier and active ingredients v, W, MOL.
Those supporting oxides such as Fe and Cu can be used.

また、その触媒形状も任意のものが使用できるが、圧損
の少ないハニカム状のものを使用することが好ましい。
Moreover, any shape of the catalyst can be used, but it is preferable to use a honeycomb shape with less pressure loss.

また、これら触媒層の設置位置は経路中のガス温度が2
00〜500℃がよく、特に3σ0〜450℃の範囲が
よシ好ましいことを本発明者らの実験結果によって確認
した。
In addition, the installation position of these catalyst layers is such that the gas temperature in the path is 2.
The experimental results of the present inventors have confirmed that the temperature range is preferably 00 to 500°C, and particularly preferably 3σ0 to 450°C.

本発明においては石炭ガス化炉とガスタービン燃焼器の
経路のガス1211fLが200〜500℃の個所に、
上記した触媒層を設置し、その上流側に窒素酸化物(N
O)と酸素含有ガス(0,)を注入するものであるが、
これは石炭ガス化炉発生ガス中0BIB、と注入された
適量のNO及び0、t−反応させて下記式の反応により
yHs’+安定なN、に変えるためである。
In the present invention, 1211fL of gas in the path between the coal gasifier and the gas turbine combustor is at a temperature of 200 to 500°C,
The above catalyst layer is installed, and nitrogen oxides (N
O) and oxygen-containing gas (0,) are injected,
This is to cause 0BIB in the gas generated by the coal gasifier to react with an appropriate amount of injected NO and 0, t- to convert it into yHs'+stable N through the reaction of the following formula.

4111i、 + 4110 + O,→41!ffi
+6馬O上記反応によシ、ガスタービン燃焼器に投入さ
れるガス中に含まれるNO,は極力低減されhに変化し
ているためガスタービン燃焼器で発生するNOxは低く
ガスタービン排ガス中のNOxは低い値となる。
4111i, + 4110 + O, → 41! ffi
+6 O Due to the above reaction, the NO contained in the gas input to the gas turbine combustor is reduced as much as possible and changed to h, so the NOx generated in the gas turbine combustor is low and the amount of NOx in the gas turbine exhaust gas is NOx becomes a low value.

〔実施列〕[Implementation row]

以下、本発明の一実施列を第1図にしたがって説明する
。第1図において、第5図と同一符号は第3図と同一部
を示す。5は石炭ガス化ガス供給経路2に設けられた窒
素酸化物(No )及び酸素含有ガス(O3)注入器、
6はアンモニアを還元剤とする選択接触脱硝触媒を充填
した反応器である。
Hereinafter, one embodiment of the present invention will be explained with reference to FIG. In FIG. 1, the same reference numerals as in FIG. 5 indicate the same parts as in FIG. 3. 5 is a nitrogen oxide (No) and oxygen-containing gas (O3) injector provided in the coal gasification gas supply route 2;
6 is a reactor filled with a selective catalytic denitrification catalyst using ammonia as a reducing agent.

第1図のフローにおいて、石炭ガス化ガス中のME、に
対して、 4NEI、+4NO+O,→411.+6B、0の反応
に見合うNO及びO3を注入し、反応器6を設置した個
所の温度によって上記反応がどのように生起するかを調
べた結果を第2図に示す。
In the flow shown in Fig. 1, for ME in coal gasification gas, 4NEI, +4NO+O, → 411. FIG. 2 shows the results of injecting NO and O3 corresponding to the +6B,0 reaction and investigating how the above reaction occurred depending on the temperature at the location where the reactor 6 was installed.

第2図はガス温度(反↓6器6の設置t温度)(℃)と
脱NH,率(%)との関係を示す図表でこれより反応器
6を設置する個所の温度は200〜500℃、特に50
0〜450℃の範囲内が好ましいことが判る。
Figure 2 is a chart showing the relationship between gas temperature (temperature at which reactor 6 is installed) (℃) and NH removal rate (%). °C, especially 50
It turns out that the temperature within the range of 0 to 450°C is preferable.

次に、第1図の70−において、脱硝触媒を充填した反
応器6を最適温度の部位の経路2中に設置し、■0.の
み注入し、NOは注入しない場合(比較メ11)、■N
Oのみ注入し、0゜は注入しない場合(比較例2)及び
■NOと0゜の両者を注入した場合(実施列)を実施し
、下表のような結果を得た。
Next, at 70- in FIG. 1, the reactor 6 filled with the denitrification catalyst is installed in the path 2 at the optimum temperature point, and (1) 0. When only injecting NO and not injecting NO (comparison method 11), ■N
A case where only O was injected and no injection at 0° was carried out (Comparative Example 2) and a case where both NO and 0° were injected (implementation row) were carried out, and the results shown in the table below were obtained.

〔発明の効果〕〔Effect of the invention〕

ガスタービンに投入される石炭ガス化ガス中のNH,′
a度が低くなり、ガスタービン排ガス中の110x (
14度が低くなシ大気中に放出されるNOxが低減でき
る。
NH,′ in the coal gasification gas input to the gas turbine
The degree of a decreases, and 110x (
When the temperature is 14 degrees lower, NOx released into the atmosphere can be reduced.

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

第1図は本発明の一実施例のフローを説明するだめの図
、第2図は本発明のアンモニアを還元剤とする選択接触
脱硝触媒層の設置位置と脱NH,率の関係を示す区民、
第3図は従来の石炭ガス化炉とガスタービンとの組合せ
設備を示す図でろる。
Fig. 1 is a diagram for explaining the flow of an embodiment of the present invention, and Fig. 2 is a diagram showing the relationship between the installation position of the selective catalytic denitrification catalyst layer using ammonia as the reducing agent and the NH removal rate of the present invention. people,
FIG. 3 is a diagram showing a conventional combination equipment of a coal gasification furnace and a gas turbine.

Claims (1)

【特許請求の範囲】[Claims] 石炭ガス化炉で発生する石炭ガス化ガスの燃焼器への供
給経路に、ガス温度200〜500℃の範囲内の経路に
アンモニアを還元剤とする選択接触還元脱硝触媒層を設
け、該触媒層の前流側に窒素酸化物及び酸素含有ガスを
注入することを特徴とする石炭ガス化ガス中のアンモニ
アの低減法。
A selective catalytic reduction denitrification catalyst layer using ammonia as a reducing agent is provided in a route in which the gas temperature is within the range of 200 to 500°C in a supply route of coal gasification gas generated in a coal gasifier to a combustor, and the catalyst layer A method for reducing ammonia in coal gasification gas, characterized by injecting nitrogen oxide and oxygen-containing gas into the upstream side of the coal gasification gas.
JP63148288A 1988-06-17 1988-06-17 Ammonia reduction method in coal gasification gas. Expired - Fee Related JPH083105B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63148288A JPH083105B2 (en) 1988-06-17 1988-06-17 Ammonia reduction method in coal gasification gas.

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63148288A JPH083105B2 (en) 1988-06-17 1988-06-17 Ammonia reduction method in coal gasification gas.

Publications (2)

Publication Number Publication Date
JPH01318082A true JPH01318082A (en) 1989-12-22
JPH083105B2 JPH083105B2 (en) 1996-01-17

Family

ID=15449419

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63148288A Expired - Fee Related JPH083105B2 (en) 1988-06-17 1988-06-17 Ammonia reduction method in coal gasification gas.

Country Status (1)

Country Link
JP (1) JPH083105B2 (en)

Also Published As

Publication number Publication date
JPH083105B2 (en) 1996-01-17

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