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JPS5852010B2 - Denitrification method for sintering furnace exhaust gas - Google Patents
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JPS5852010B2 - Denitrification method for sintering furnace exhaust gas - Google Patents

Denitrification method for sintering furnace exhaust gas

Info

Publication number
JPS5852010B2
JPS5852010B2 JP55007601A JP760180A JPS5852010B2 JP S5852010 B2 JPS5852010 B2 JP S5852010B2 JP 55007601 A JP55007601 A JP 55007601A JP 760180 A JP760180 A JP 760180A JP S5852010 B2 JPS5852010 B2 JP S5852010B2
Authority
JP
Japan
Prior art keywords
exhaust gas
carbon monoxide
temperature
denitrification
sintering furnace
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
Application number
JP55007601A
Other languages
Japanese (ja)
Other versions
JPS56105434A (en
Inventor
智次 岩田
甲 山下
岱輔 西田
一夫 田島
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.)
JFE Engineering Corp
Original Assignee
Nippon Kokan 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 Nippon Kokan Ltd filed Critical Nippon Kokan Ltd
Priority to JP55007601A priority Critical patent/JPS5852010B2/en
Publication of JPS56105434A publication Critical patent/JPS56105434A/en
Publication of JPS5852010B2 publication Critical patent/JPS5852010B2/en
Expired legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Description

【発明の詳細な説明】 本発明は、焼結炉排ガスを一酸化炭素を利用して昇温し
、同時にこれを浄化した後脱硝する焼結炉排ガスの脱硝
方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for denitrating sintering furnace exhaust gas, in which the temperature of sintering furnace exhaust gas is raised using carbon monoxide, and at the same time, the gas is purified and then denitrified.

焼結炉排ガスのアンモニア接触還元による脱硝方法では
、反応前に排ガスを所定の温度まで昇温する必要がある
が、昇温に要する燃料費が大きな問題となっている。
In the denitrification method using ammonia catalytic reduction of sintering furnace exhaust gas, it is necessary to raise the temperature of the exhaust gas to a predetermined temperature before the reaction, but the fuel cost required for raising the temperature is a major problem.

このため焼結炉排ガスに含まれる一酸化炭素を触媒によ
って酸化し、その際発生する熱を有効に利用する脱硝方
法が提案されている。
For this reason, a denitrification method has been proposed in which carbon monoxide contained in sintering furnace exhaust gas is oxidized by a catalyst and the heat generated at the time is effectively utilized.

第1図の脱硝方法は、その一例を示し、この方法は脱硝
後の排ガスを熱交換器1を通して昇温した後更に加熱炉
2で加熱し、還元剤としてアンモニア3を添加して、脱
硝反応層4で脱硝し、次いでこれを白金、パラジウム等
の貴金属をアルミナの担体に含浸させて合成した合成触
媒からなる一酸化炭素酸化層5に通して一酸化炭素を酸
化し、排ガスを昇温した後上記熱交換器1にもどし、降
温排出する方法である。
The denitrification method shown in Fig. 1 is an example of this method. In this method, the exhaust gas after denitrification is heated through a heat exchanger 1, then further heated in a heating furnace 2, and ammonia 3 is added as a reducing agent to cause the denitrification reaction. The exhaust gas was denitrated in layer 4, and then passed through carbon monoxide oxidation layer 5, which was made of a synthetic catalyst synthesized by impregnating an alumina carrier with noble metals such as platinum and palladium, to oxidize carbon monoxide and raise the temperature of the exhaust gas. After that, the heat exchanger 1 is returned to the heat exchanger 1, and the temperature is lowered and discharged.

しかしこの方法で用いる合成触媒は、一酸化炭素の酸化
率を高めるためには300℃以上の高温でなければなら
ず、又コストが高いうえ、劣化後の触媒の処分に問題が
ある。
However, the synthetic catalyst used in this method must be heated to a high temperature of 300° C. or higher in order to increase the oxidation rate of carbon monoxide, is expensive, and has problems in disposing of the catalyst after it has deteriorated.

しかも一酸化炭素の酸化熱は熱交換器1を通じて利用さ
れるので利用効率が悪い欠点がある。
Moreover, the heat of oxidation of carbon monoxide is used through the heat exchanger 1, which has the drawback of poor utilization efficiency.

また別の脱硝方法として第2図に示すものがある。Another method of denitration is shown in FIG.

この方法は、脱硝後の排ガスを熱交換器11を通して昇
温した後、加熱炉12で加熱し、アンモニア13を添加
して、これを鉄鉱石を入れた脱硝反応層14に入れ、こ
こでNOxを還元するとともに一酸化炭素も鉄鉱石によ
って酸化させ、この後、上記熱交換器11を通すもので
ある。
In this method, the exhaust gas after denitrification is heated through a heat exchanger 11, then heated in a heating furnace 12, ammonia 13 is added thereto, and this is put into a denitrification reaction layer 14 containing iron ore, where NOx At the same time, carbon monoxide is also oxidized by iron ore, and then passed through the heat exchanger 11.

しかしこの方法は、第1図のものと同様に300℃以上
でなければ酸化率の向上を望むことができないとともに
酸化率を上げて昇温効率を高めれば逆に脱硝率の低下を
もたらすおそれがある。
However, with this method, as with the one in Figure 1, it is impossible to expect an improvement in the oxidation rate unless the temperature is above 300°C, and if the oxidation rate is increased to increase the temperature raising efficiency, there is a risk that the denitrification rate will decrease. be.

また焼結排ガスの脱硝処理とは別に、一酸化炭素の処理
技術として自動車排ガスの浄化が挙げられる。
In addition to denitrification treatment of sintering exhaust gas, purification of automobile exhaust gas is also mentioned as a treatment technology for carbon monoxide.

この方法は合成触媒を用いて処理する方法であるが、第
1図の例と同様コストが高く、活性が低下した触媒の処
分に問題がある。
This method uses a synthetic catalyst, but like the example shown in FIG. 1, the cost is high and there are problems in disposing of the catalyst whose activity has decreased.

本発明は上記事情に鑑みてなされたもので、その目的と
するところは、酸化熱を有効に利用でき、しかも触媒に
安価なものを用い活性が低下してもこれを資源として利
用できる焼結炉排ガスの脱硝方法を提供するものである
The present invention was made in view of the above circumstances, and its purpose is to create a sintering method that can effectively utilize oxidation heat, use an inexpensive catalyst, and use it as a resource even if the activity decreases. The present invention provides a method for denitrifying furnace exhaust gas.

すなわち本発明は、一酸化炭素ガスの酸化を、従来のよ
うに脱硝処理後又は処理と同時におこなうことはせずに
、脱硝処理前におこなうことにより一酸化炭素ガスの酸
化熱の利用効率を高めるものである。
That is, the present invention improves the efficiency of utilizing the heat of oxidation of carbon monoxide gas by oxidizing carbon monoxide gas before denitrification treatment, instead of oxidizing it after or simultaneously with denitrification treatment as in the conventional method. It is something.

この場合脱硝処理前の焼結排ガスの温度は、100〜2
50℃であり、従ってこの温度範囲で活性の高い触媒を
選択する必要がある。
In this case, the temperature of the sintering exhaust gas before denitration treatment is 100 to 2
50°C, and therefore it is necessary to select a catalyst that is highly active in this temperature range.

本発明は、自然界に産するマンガン鉱石が一酸化炭素の
酸化触媒として有効で、しかもこの触媒は300℃以下
の温度で活性が高いことに着目し、これを利用すること
により脱硝前の排ガス中の一酸化炭素ガスの酸化を可能
とした。
The present invention focuses on the fact that naturally occurring manganese ore is effective as a carbon monoxide oxidation catalyst, and that this catalyst is highly active at temperatures below 300°C. This made it possible to oxidize carbon monoxide gas.

しかもこのマンガン鉱石は製鉄所の資源として用いられ
るものであるから、これが劣化しても資源として有効に
利用できるものである。
Moreover, since this manganese ore is used as a resource in steel mills, even if it deteriorates, it can be effectively used as a resource.

以下本発明を図面を参照して詳細に説明する。The present invention will be described in detail below with reference to the drawings.

本焼結排ガスは、まず第3図に示すように熱交換器21
を通った後、脱硫機22で脱硫される。
The main sintering exhaust gas is first transferred to the heat exchanger 21 as shown in FIG.
After passing through, it is desulfurized by a desulfurizer 22.

この場合SOxは数ppm以下に脱硫されるのが好まし
い。
In this case, it is preferable that SOx be desulfurized to several ppm or less.

脱硫後の排ガスの化学組成は例えば第1表に示される如
くである。
The chemical composition of the exhaust gas after desulfurization is as shown in Table 1, for example.

湿式集しん機23で除しんされ、更に昇圧機24、上記
熱交換器21を通して移動床式の一酸化炭素酸化層25
に誘導される。
The dust is removed by a wet dust collector 23, and then passed through a booster 24 and the heat exchanger 21 to a moving bed type carbon monoxide oxidation layer 25.
be guided by.

この酸化層25内にはマンガン系鉱石あるいは鉄マンガ
ン系鉱石など一酸化炭素の酸化触媒として作用するマン
ガン鉱石が充填されている。
This oxidized layer 25 is filled with manganese ore, such as manganese ore or iron-manganese ore, which acts as a carbon monoxide oxidation catalyst.

その化学組成の一例をあげれば第2表に示す如きである
An example of its chemical composition is shown in Table 2.

ここで一酸化炭素酸化層25に流入する焼結排ガスは、
300℃以下とし、とくに100〜250℃の範囲が好
ましい。
Here, the sintering exhaust gas flowing into the carbon monoxide oxidation layer 25 is
The temperature is preferably 300°C or less, particularly preferably in the range of 100 to 250°C.

このことは20ONrrl’/hrのパイロットの実験
で明らかとなったものである。
This was revealed in a pilot experiment of 20ONrrl'/hr.

第4図は、一酸化炭素酸化層25に流入する焼結排ガス
の温度(’C’)と一酸化炭素の酸化率(%)との関係
を示したもので、図中曲線aは触媒として第2表に示す
A61の組成のマンガン鉱石を用い、5V=5000h
r−’とした場合の実験結を示している。
Figure 4 shows the relationship between the temperature ('C') of the sintering exhaust gas flowing into the carbon monoxide oxidation layer 25 and the oxidation rate (%) of carbon monoxide. Using manganese ore with the composition of A61 shown in Table 2, 5V = 5000h
The experimental result when r-' is shown.

また曲線すは/162の組成のマンガン鉱石を用い、5
V=5000hr−’の場合、曲線Cは涜3の組成のマ
ンガン鉱石で、S V= 3000hr−1の場合、曲
線dはA3の組成のマンガン鉱石で5V=5000 h
r−1の場合をそれぞれ示している。
In addition, using manganese ore with a composition of /162,
When V = 5000 hr-', curve C is manganese ore with composition 3, and when S V = 3000 hr-1, curve d is manganese ore with composition A3 and 5V = 5000 h.
The case of r-1 is shown respectively.

この実験でマンガン鉱石は8〜25mmに整粒されたも
のを用い、酸化層25は400朋φ×2000mmのも
のを用い、マンガン鉱石の充填物の厚さはSV= 30
00 hr−1で530關、SVニ5000−1で32
0i!iである。
In this experiment, manganese ore sized to 8 to 25 mm was used, the oxide layer 25 was 400 mm in diameter x 2000 mm, and the thickness of the manganese ore filling was SV = 30.
530 in 00 hr-1, 32 in SV Ni5000-1
0i! It is i.

この実験結果から/461、A62のものは活性が高く
、60℃で約50%、100〜200℃で約99%の酸
化率となる。
From this experimental result, /461 and A62 have high activity, with an oxidation rate of about 50% at 60°C and about 99% at 100 to 200°C.

又A3のものでも200〜300℃で約40%の酸化率
となる。
Also, even with A3, the oxidation rate is about 40% at 200 to 300°C.

従って300℃以上では十分な酸化率が得られず、涜1
〜/162のものはとくに100〜250℃が好ましい
ことがわかる。
Therefore, a sufficient oxidation rate cannot be obtained at temperatures above 300°C, resulting in
It can be seen that temperatures of 100 to 250°C are particularly preferable for those with a temperature of 162 to 162.

このようにして一酸化炭素酸化層25で焼結排ガス中の
一酸化炭素を酸化するが、この排ガスは熱交換器26を
経て加熱炉27を所定温度に昇温されアンモニア28を
添加した後脱硝反応層29で脱硝した後上記熱交換器2
6を通って外部に排出される。
In this way, carbon monoxide in the sintering exhaust gas is oxidized in the carbon monoxide oxidation layer 25, but this exhaust gas is heated to a predetermined temperature in the heating furnace 27 through the heat exchanger 26, and after adding ammonia 28, it is denitrified. After denitration in the reaction layer 29, the heat exchanger 2
6 and is discharged to the outside.

以上の如く本発明においては、脱硝前に一酸化炭素を酸
化させ、酸化熱をそのまま脱硝反応に利用するので酸化
熱の利用効率を高め燃料費の節約を図ることができる。
As described above, in the present invention, carbon monoxide is oxidized before denitrification, and the heat of oxidation is directly used for the denitrification reaction, so that the efficiency of using the heat of oxidation can be improved and fuel costs can be saved.

しかも反応用触媒としてマンガン鉱石を用いたので、安
価であるとともに活性が低下しても製鉄所の資源として
有効に利用できるなど顕著な効果を奏する。
Moreover, since manganese ore is used as a reaction catalyst, it is inexpensive and has remarkable effects such as being able to be used effectively as a resource in steel plants even if the activity decreases.

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

第1図及び第2図は先に提案されているそれぞれ異なる
脱硝方法を示したブロック図、第3図は本発明に係る脱
硝方法を示したブロック図、第4図は一酸化炭素酸化層
に流入する排ガスの平均温度と、一酸化炭素の酸化率と
の関係を示す特性図、第5図は一酸化炭素の酸化率と排
ガスの上昇温度との関係を示す特性図である。 21・・・・・・熱交換器、22・・・・・・脱硫機、
23・・・・・・湿式集じん機、24・・・・・・昇圧
機、25・・・・・・一酸化炭素酸化層、26・・・・
・・熱交換器、27・・・・・・加熱炉、28・・・・
・・アンモニア、29・・・・・・脱硝反応層。
Figures 1 and 2 are block diagrams showing the different denitrification methods previously proposed, Figure 3 is a block diagram showing the denitrification method according to the present invention, and Figure 4 is a block diagram showing the denitrification method according to the present invention. FIG. 5 is a characteristic diagram showing the relationship between the average temperature of inflowing exhaust gas and the oxidation rate of carbon monoxide, and FIG. 5 is a characteristic diagram showing the relationship between the oxidation rate of carbon monoxide and the rising temperature of the exhaust gas. 21... Heat exchanger, 22... Desulfurizer,
23... Wet type dust collector, 24... Booster, 25... Carbon monoxide oxidation layer, 26...
... Heat exchanger, 27 ... Heating furnace, 28 ...
... Ammonia, 29 ... Denitrification reaction layer.

Claims (1)

【特許請求の範囲】 1 焼結炉排ガス中に共存する一酸化炭素ガスを300
℃以下の温度条件でマンガン鉱石を触媒として酸化せし
めた後、該排ガスを脱硝処理することを特徴とする焼結
炉排ガスの脱硝方法。 2 一酸化炭素ガスの酸化温度条件は、100〜250
℃である特許請求の範囲第1項記載の焼結炉排ガスの脱
硝方法。
[Claims] 1. Carbon monoxide gas coexisting in the sintering furnace exhaust gas is
A method for denitrating sintering furnace exhaust gas, which comprises oxidizing the exhaust gas using manganese ore as a catalyst at a temperature of 0.degree. C. or lower, and then denitrating the exhaust gas. 2 The oxidation temperature conditions for carbon monoxide gas are 100 to 250
The method for denitrating sintering furnace exhaust gas according to claim 1, wherein the temperature is 0.degree.
JP55007601A 1980-01-25 1980-01-25 Denitrification method for sintering furnace exhaust gas Expired JPS5852010B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP55007601A JPS5852010B2 (en) 1980-01-25 1980-01-25 Denitrification method for sintering furnace exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP55007601A JPS5852010B2 (en) 1980-01-25 1980-01-25 Denitrification method for sintering furnace exhaust gas

Publications (2)

Publication Number Publication Date
JPS56105434A JPS56105434A (en) 1981-08-21
JPS5852010B2 true JPS5852010B2 (en) 1983-11-19

Family

ID=11670316

Family Applications (1)

Application Number Title Priority Date Filing Date
JP55007601A Expired JPS5852010B2 (en) 1980-01-25 1980-01-25 Denitrification method for sintering furnace exhaust gas

Country Status (1)

Country Link
JP (1) JPS5852010B2 (en)

Also Published As

Publication number Publication date
JPS56105434A (en) 1981-08-21

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