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JPH0788334A - Low temperature denitration method - Google Patents

Low temperature denitration method

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Publication number
JPH0788334A
JPH0788334A JP5257467A JP25746793A JPH0788334A JP H0788334 A JPH0788334 A JP H0788334A JP 5257467 A JP5257467 A JP 5257467A JP 25746793 A JP25746793 A JP 25746793A JP H0788334 A JPH0788334 A JP H0788334A
Authority
JP
Japan
Prior art keywords
denitration
catalyst
manganese
peaks
temperature
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.)
Withdrawn
Application number
JP5257467A
Other languages
Japanese (ja)
Inventor
Hisatsugu Kitaguchi
久継 北口
Toshiyuki Irita
俊幸 入田
Yasuyuki Sensui
康幸 泉水
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.)
Nippon Steel Corp
Original Assignee
Nippon Steel Corp
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 Steel Corp filed Critical Nippon Steel Corp
Priority to JP5257467A priority Critical patent/JPH0788334A/en
Publication of JPH0788334A publication Critical patent/JPH0788334A/en
Withdrawn legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
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Abstract

(57)【要約】 【目的】 本発明は、窒素酸化物を含む排ガス中から窒
素酸化物を除去,低減するにあたり、90℃〜150℃
の低温度領域で有効な脱硝方法を提供する。 【構成】 含有する二酸化マンガン(MnO2 )重量分
率と比表面積の積が5m2 /g以上のマンガン鉱石、ま
たはX線回折で回折面間隔2.15±0.05Å,2.
39±0.05Å,3.11±0.05Åにピークを有
し、かつ三つのピークのうち2.39±0.05Åのピ
ーク強度が最も強く、このピークに対する他の二つのピ
ークの強度比が0.2以上の構造を有するマンガン鉱石
を触媒として用い、90℃以上150℃以下の温度で脱
硝を行う。 【効果】 マンガン鉱石を利用して安価な脱硝触媒を提
供することができる。
(57) [Summary] [Object] The present invention is to remove and reduce nitrogen oxides from exhaust gas containing nitrogen oxides at 90 ° C to 150 ° C.
To provide an effective denitration method in the low temperature region of. [Constitution] Manganese ore having a product of manganese dioxide (MnO 2 ) weight fraction and specific surface area of 5 m 2 / g or more, or an X-ray diffraction diffraction plane spacing of 2.15 ± 0.05Å, 2.
It has peaks at 39 ± 0.05Å and 3.11 ± 0.05Å, and the peak intensity of 2.39 ± 0.05Å is the strongest among the three peaks, and the intensity ratio of the other two peaks to this peak. Is used as a catalyst, and denitration is performed at a temperature of 90 ° C. or more and 150 ° C. or less. [Effect] An inexpensive denitration catalyst can be provided using manganese ore.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、例えば製鉄所や発電所
等で発生する窒素酸化物を含む排ガス中から窒素酸化物
を除去ないし低減するための脱硝方法に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a denitration method for removing or reducing nitrogen oxides in exhaust gas containing nitrogen oxides generated in, for example, ironworks and power plants.

【0002】[0002]

【従来の技術】一般に排ガス中の窒素酸化物除去には、
「触媒講座」第7巻(触媒学会)253ページ5行目
に示されるように、アンモニア還元脱硝触媒としてV2
5 −TiO2 触媒が利用されている。製鉄原料を利用
する方法として、特開昭57−15824号公報に見
られるような、鉄鉱石を脱硝触媒として利用する方法も
考えられている。
2. Description of the Related Art Generally, for removing nitrogen oxides in exhaust gas,
As shown in page 5, line 253, "Catalyst Lecture" Vol. 7 (Catalyst Society), V 2 as an ammonia reduction denitration catalyst was used.
O 5 -TiO 2 catalyst has been used. As a method of utilizing an iron-making raw material, a method of utilizing iron ore as a denitration catalyst as disclosed in JP-A-57-15824 is also considered.

【0003】また特開昭51−62181号公報に見
られるように、二酸化マンガンは脱硝触媒として低温で
高活性であることが知られている。
Further, as seen in JP-A-51-62181, manganese dioxide is known to be highly active as a denitration catalyst at low temperatures.

【0004】[0004]

【発明が解決しようとする課題】しかし「触媒講座」
第7巻に示される方法は、バナジウムを使用するため触
媒が非常に高価であるという問題点があった。さらに
特開昭57−15824号公報に示される方法では、反
応温度が300〜370℃であり、製鉄所焼結排ガスの
ような、150℃以下の低温排ガスに適用するためには
加熱が必要であった。また特開昭51−62181号
公報に示される二酸化マンガンを利用する方法では、
と同様に触媒が高価であるという問題点があった。
[Problems to be solved by the invention] However, "catalyst course"
The method shown in Volume 7 has a problem that the catalyst is very expensive because vanadium is used. Further, in the method disclosed in JP-A-57-15824, the reaction temperature is 300 to 370 ° C., and heating is required for application to low temperature exhaust gas of 150 ° C. or lower, such as steel plant sintering exhaust gas. there were. Further, in the method using manganese dioxide disclosed in JP-A-51-62181,
Similarly, the catalyst is expensive.

【0005】本発明は、窒素酸化物を含む排ガスから窒
素酸化物を除去ないし低減するに当たり、安価でかつ9
0℃〜150℃の低温度領域で有効に除去ないし低減さ
せ得る低温脱硝方法を提供することを目的とする。
The present invention is inexpensive and effective in removing or reducing nitrogen oxides from exhaust gas containing nitrogen oxides.
It is an object of the present invention to provide a low-temperature denitration method capable of effectively removing or reducing in a low temperature range of 0 ° C to 150 ° C.

【0006】[0006]

【課題を解決するための手段】本発明は、かかる課題を
解決するために低温脱硝触媒として有効な二酸化マンガ
ンを含有するマンガン鉱石に着目し、種々のマンガン鉱
石について脱硝活性の調査および様々な方法で解析を行
った結果、本発明に至った。
The present invention focuses on a manganese ore containing manganese dioxide which is effective as a low temperature denitration catalyst for solving the above problems, and investigates the denitration activity of various manganese ores and various methods. As a result of the analysis by the present invention, the present invention was achieved.

【0007】すなわち第1の本発明は、窒素酸化物(N
Ox)含有排ガスからアンモニアを還元剤とし、触媒を
用いて窒素酸化物を除去ないし低減する低温脱硝方法に
おいて、含有する二酸化マンガン(MnO2 )重量分率
と比表面積の積が5m2 /g以上のマンガン鉱石を触媒
として用い、90℃以上150℃以下の温度で脱硝を行
う低温脱硝方法である。
That is, the first aspect of the present invention relates to nitrogen oxide (N
In the low temperature denitration method of removing or reducing nitrogen oxides using a catalyst with ammonia as a reducing agent, the product of manganese dioxide (MnO 2 ) weight fraction and specific surface area contained is 5 m 2 / g or more. Is a low temperature denitration method in which denitration is performed at a temperature of 90 ° C. or higher and 150 ° C. or lower using the manganese ore of No. 1 as a catalyst.

【0008】また第2の本発明は、窒素酸化物(NO
x)含有排ガスからアンモニアを還元剤とし、触媒を用
いて窒素酸化物を除去ないし低減する低温脱硝方法にお
いて、X線回折で回折面間隔2.15±0.05Å,
2.39±0.05Å,3.11±0.05Åにピーク
を有し、かつ三つのピークのうち2.39±0.05Å
のピーク強度が最も強く、このピークに対する他の二つ
のピークの強度比が0.2以上の構造を有するマンガン
鉱石を触媒として用い、90℃以上150℃以下の温度
で脱硝を行う低温脱硝方法である。
The second aspect of the present invention is directed to nitrogen oxides (NO
x) A low-temperature denitration method in which ammonia is used as a reducing agent from the exhaust gas contained and a nitrogen oxide is removed or reduced by using a catalyst, and the diffraction plane spacing is 2.15 ± 0.05Å by X-ray diffraction
It has peaks at 2.39 ± 0.05Å and 3.11 ± 0.05Å, and of the three peaks is 2.39 ± 0.05Å
Is the strongest peak intensity, and a low temperature denitration method in which denitration is performed at a temperature of 90 ° C to 150 ° C using a manganese ore having a structure in which the intensity ratio of the other two peaks to this peak is 0.2 or more. is there.

【0009】なおここで用いるマンガン鉱石は、製鉄プ
ロセスにおいて用いられるものを流用し、整粒,粉砕せ
ずに使用可能であるが、通気性を確保するために整粒,
粉砕が望ましい。
As the manganese ore used here, the one used in the iron making process can be diverted and used without sizing and crushing, but in order to ensure air permeability,
Grinding is desirable.

【0010】[0010]

【作用】二酸化マンガンを含む種々のマンガン鉱石を用
いて様々な温度条件で脱硝性能評価を行ったところ、二
酸化マンガン重量分率がほぼ同じ鉱石でも低温領域で脱
硝性能が大きく異なることを見出した。
[Function] When various manganese ores containing manganese dioxide were used to evaluate the denitration performance under various temperature conditions, it was found that the denitrification performance was significantly different in the low temperature region even if the ores having almost the same manganese dioxide weight fraction were used.

【0011】この原因を調査した結果、90℃以上15
0℃以下の温度条件では、脱硝性能に二酸化マンガン重
量分率だけでなく比表面積が関与しており、この温度条
件においては比表面積と二酸化マンガン重量分率の積
が、脱硝性能と非常に相関がよいことが判った。
As a result of investigating the cause, 90 ° C. or higher 15
Under the temperature condition of 0 ° C or less, not only the manganese dioxide weight fraction but also the specific surface area are involved in the denitration performance. Under this temperature condition, the product of the specific surface area and the manganese dioxide weight fraction is highly correlated with the denitration performance. Turned out to be good.

【0012】また脱硝性能評価に用いたマンガン鉱石に
ついてX線回折を行ったところ、上記温度条件で脱硝性
能が良かったマンガン鉱石が、特有の回折パターンを有
することを見出した。
When X-ray diffraction was performed on the manganese ore used for the denitration performance evaluation, it was found that the manganese ore having good denitration performance under the above temperature conditions has a unique diffraction pattern.

【0013】ここで比表面積は、吸着ガスに窒素を用い
BET法(「触媒講座」第3巻(触媒学会)204ペー
ジ)により測定を行った。また二酸化マンガン重量分率
は、しゅう酸ナトリウム分解過マンガン酸カリウム滴定
法(JIS−M8233マンガン鉱石中の活性酸素定量
方法)により活性酸素の定量を行い、下記数1に示す換
算式を用いて二酸化マンガン量とした。
Here, the specific surface area was measured by the BET method ("Catalyst Lecture", Vol. 3, p. 204) using nitrogen as an adsorption gas. The weight fraction of manganese dioxide was determined by measuring the amount of active oxygen by the sodium oxalate decomposition potassium permanganate titration method (JIS-M8233 method for determining active oxygen in manganese ore) and using the conversion formula shown in Formula 1 below. The amount of manganese was used.

【0014】[0014]

【数1】 (二酸化マンガン量)=(活性酸素)×5.434## EQU1 ## (Amount of manganese dioxide) = (active oxygen) × 5.434

【0015】以下に述べる実施例では、すべてこれらの
方法に依った。しかし本発明における比表面積及び二酸
化マンガン重量分率は、これらの方法によらなくともほ
ぼ同等の測定結果が得られる測定方法ならば、何れの方
法で調べても良い。
In the examples described below, these methods were all used. However, the specific surface area and the manganese dioxide weight fraction in the present invention may be examined by any method as long as the measurement results can obtain substantially the same measurement results without using these methods.

【0016】[0016]

【実施例】以下に実施例を用いて本発明を具体的に説明
する。
EXAMPLES The present invention will be specifically described below with reference to examples.

【0017】実施例1として、比表面積と二酸化マンガ
ン重量分率を測定したマンガン鉱石a(比表面積;28
2 /g,二酸化マンガン重量分率;67%)を用い
て、80〜200℃,空間速度約5000hr-1,NO
x(NO+NO2 );200ppm(NO;195pp
m,NO2 ;5ppm),H2 O;10%,O2 ;15
%,N2 ;75%のモデルガスにNH3 を200ppm
添加して脱硝試験を行い、各温度における脱硝性能(脱
硝率)と比表面積,二酸化マンガン重量分率の相関を調
べた。
As Example 1, manganese ore a (specific surface area; 28, specific surface area and manganese dioxide weight fraction were measured)
m 2 / g, manganese dioxide weight fraction; 67%), 80-200 ° C., space velocity of about 5000 hr −1 , NO
x (NO + NO 2 ); 200 ppm (NO; 195 pp
m, NO 2 ; 5 ppm), H 2 O; 10%, O 2 ; 15
%, N 2 ; NH 3 200 ppm in 75% model gas
A denitration test was conducted by adding the above components, and the correlation between the denitration performance (denitration rate) at each temperature, the specific surface area, and the manganese dioxide weight fraction was investigated.

【0018】表1に示すように、90℃以上150℃以
下で、脱硝性能に対して比表面積,二酸化マンガン重量
分率個々の相関よりも、二酸化マンガン重量分率と比表
面積の積の相関の方が良くなる。
As shown in Table 1, at 90 ° C. or higher and 150 ° C. or lower, the correlation of the product of the manganese dioxide weight fraction and the specific surface area is more than the correlation of the specific surface area and the manganese dioxide weight fraction with respect to the denitration performance. Better.

【0019】ここで90℃未満では、温度が低すぎるた
めに脱硝性能が極端に低下し、脱硝性能に対する相関も
悪くなる。また150℃超では脱硝性能に対する比表面
積の影響が小さくなり、二酸化マンガン重量分率が脱硝
性能を決定する最も強い因子となる。
If the temperature is lower than 90 ° C., the temperature is too low, so that the denitration performance is extremely deteriorated and the correlation with the denitration performance is deteriorated. Further, when the temperature exceeds 150 ° C, the influence of the specific surface area on the denitration performance becomes small, and the manganese dioxide weight fraction becomes the strongest factor that determines the denitration performance.

【0020】[0020]

【表1】 [Table 1]

【0021】一例として、90℃における二酸化マンガ
ン重量分率と比表面積の積と脱硝率の関係を、図1に示
す。使用した二酸化マンガンの比表面積および二酸化マ
ンガン重量分率を、表2に示す。
As an example, FIG. 1 shows the relationship between the product of the manganese dioxide weight fraction and the specific surface area at 90 ° C. and the denitration rate. Table 2 shows the specific surface area and the manganese dioxide weight fraction of the manganese dioxide used.

【0022】図1に示すように、マンガン鉱石は脱硝性
能に対して3つのグループに分類できた。すなわち、二
酸化マンガン重量分率と比表面積の積が5m2 /g以上
で脱硝率が30%以上のAグループ,二酸化マンガン重
量分率と比表面積の積が3以上5m2 /g未満で脱硝率
が10%以上20%未満のBグループ,二酸化マンガン
重量分率と比表面積の積が3m2 /g未満で脱硝率が1
0%未満のCグループに分類できる。
As shown in FIG. 1, manganese ores could be classified into three groups with respect to denitration performance. That is, the group A having a product of manganese dioxide weight fraction and specific surface area of 5 m 2 / g or more and a denitrification rate of 30% or more, a denitrification rate of manganese dioxide weight fraction and specific surface area of 3 or more and less than 5 m 2 / g. Group B of 10% or more and less than 20%, the product of manganese dioxide weight fraction and specific surface area is less than 3 m 2 / g, and the denitrification rate is 1
It can be classified into C group of less than 0%.

【0023】これらの関係は90℃以上150℃以下の
温度範囲では成立する。従って、Aグループに属するマ
ンガン鉱石を触媒として用いることにより、90℃以上
150℃以下の温度領域における脱硝を効率的に進める
ことができる。
These relationships are established in the temperature range of 90 ° C to 150 ° C. Therefore, by using the manganese ore belonging to the A group as a catalyst, it is possible to efficiently proceed denitration in the temperature range of 90 ° C. or higher and 150 ° C. or lower.

【0024】[0024]

【表2】 [Table 2]

【0025】実施例2として、実施例1のマンガン鉱石
に対してX線回折を行い、含まれるマンガンの形態を調
べた。マンガン鉱石は鉱石であるので、マンガンの他に
鉄をはじめとする多くの元素で構成されているため、回
折ピークの高さや位置は純粋なマンガン化合物のX線回
折パターンと厳密には一致しないが、実施例1で示した
3つのグループは、それぞれ特徴的なX線回折パターン
を有することを見出した。
As Example 2, the manganese ore of Example 1 was subjected to X-ray diffraction to examine the form of manganese contained therein. Since manganese ore is an ore and is composed of many elements such as iron in addition to manganese, the height and position of the diffraction peak do not exactly match the X-ray diffraction pattern of the pure manganese compound. It was found that the three groups shown in Example 1 each had a characteristic X-ray diffraction pattern.

【0026】表3に、マンガン化合物のピークと推定さ
れるピークのうちピーク強度で3番目までの回折面間隔
と、これらのピークのうち最強回折面間隔のピーク強度
を1とした時のピーク強度比を示す。
Table 3 shows diffraction surface spacings up to the third in terms of peak intensity among peaks estimated to be manganese compound peaks, and peak intensity when the peak intensity of the strongest diffraction surface spacing among these peaks is 1. The ratio is shown.

【0027】[0027]

【表3】 [Table 3]

【0028】すなわち表2に示すように、低温脱硝性能
の良いAグループでは回折面間隔2.15±0.05
Å,2.39±0.05Å,3.11±0.05Åにピ
ークを有し、かつ三つのピークのうち2.39±0.0
5Åのピーク強度が最も強く、このピークに対する他の
二つのピークの強度比が0.2以上である。このピーク
はα−MnO2 と推定される。
That is, as shown in Table 2, in the group A, which has good low-temperature denitration performance, the diffraction surface spacing is 2.15 ± 0.05.
Has peaks at Å, 2.39 ± 0.05 Å, 3.11 ± 0.05 Å, and 2.39 ± 0.0 of the three peaks
The peak intensity of 5Å is the strongest, and the intensity ratio of the other two peaks to this peak is 0.2 or more. This peak is estimated to be α-MnO 2 .

【0029】これに対して脱硝性能の低いBグループで
はAグループと2箇所共通する位置に回折面間隔ピーク
を有するが、ピーク強度のパターンが異なっており、A
グループの2.15±0.05Åにおけるピークも存在
するが、そのピーク強度は最強回折面間隔に対する強度
比で0.1で小さい。BグループではAグループと同じ
種類のマンガン化合物も含有しているが、主成分は別の
マンガン化合物(β−MnO2 と推定される)であると
考えられる。
On the other hand, the group B, which has a low denitration performance, has diffraction surface spacing peaks at two common positions with the group A, but the peak intensity patterns are different, and
There is also a peak at 2.15 ± 0.05 Å in the group, but the peak intensity is small at 0.1 in terms of intensity ratio to the strongest diffraction plane spacing. Although the B group also contains the same type of manganese compound as the A group, it is considered that the main component is another manganese compound (presumed to be β-MnO 2 ).

【0030】また脱硝性能をほとんど示さないCグルー
プでは、A,Bグループとひとつだけ共通するピークを
有しているが、ピークパターンも全く異なっており、主
成分はA,Bグループと全く異なっていると考えられる
(Mn2 3 、Mn3 4 と推定)。
The C group, which shows almost no denitration performance, has only one peak in common with the A and B groups, but the peak patterns are also completely different, and the main components are completely different from those of the A and B groups. (Mn 2 O 3 and Mn 3 O 4 are estimated).

【0031】以上のことより、回折面間隔2.15±
0.05Å,2.39±0.05Å,3.11±0.0
5Åにピークを有し、かつ三つのピークのうち2.39
±0.05Åのピーク強度が最も強く、このピークに対
する他の二つのピークの強度比が0.2以上のマンガン
鉱石を触媒として用いることにより、90℃以上150
℃以下の温度領域における脱硝を効率的に進めることが
できる。
From the above, the diffraction plane spacing is 2.15 ±
0.05Å, 2.39 ± 0.05Å, 3.11 ± 0.0
It has a peak at 5Å and 2.39 out of the three peaks.
The peak intensity of ± 0.05Å is the strongest and the intensity ratio of the other two peaks to this peak is 0.2 or more.
It is possible to efficiently proceed denitration in a temperature range of ℃ or less.

【0032】[0032]

【発明の効果】本発明による低温脱硝方法を適用する場
合、以下の効果がある。 (1)マンガン鉱石を利用することにより、安価な脱硝
触媒を提供することができる。 (2)製鉄所等の排煙脱硝に使用する場合、劣化した鉱
石を製鉄のマンガン源として再利用できる。
When the low temperature denitration method according to the present invention is applied, the following effects are obtained. (1) An inexpensive denitration catalyst can be provided by using manganese ore. (2) When it is used for flue gas denitration in a steelworks, the deteriorated ore can be reused as a manganese source for ironmaking.

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

【図1】二酸化マンガン重量分率と比表面積の積と脱硝
率の関係を示す図である。
FIG. 1 is a diagram showing a relationship between a product of a manganese dioxide weight fraction and a specific surface area and a denitration rate.

─────────────────────────────────────────────────────
─────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成5年11月2日[Submission date] November 2, 1993

【手続補正1】[Procedure Amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0024[Name of item to be corrected] 0024

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0024】[0024]

【表2】 [Table 2]

───────────────────────────────────────────────────── 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 B01J 23/34 ZAB A 8017−4G F01N 3/08 B 3/10 A ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location B01J 23/34 ZAB A 8017-4G F01N 3/08 B 3/10 A

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 窒素酸化物(NOx)含有排ガスからア
ンモニアを還元剤とし、触媒を用いて窒素酸化物を除去
ないし低減する低温脱硝方法において、含有する二酸化
マンガン(MnO2 )重量分率と比表面積の積が5m2
/g以上のマンガン鉱石を触媒として用い、90℃以上
150℃以下の温度で脱硝を行う低温脱硝方法。
1. A low-temperature denitration method for removing or reducing nitrogen oxides by using a catalyst with ammonia as a reducing agent from exhaust gas containing nitrogen oxides (NOx), and the ratio to the weight fraction of manganese dioxide (MnO 2 ) contained. Surface area product is 5m 2
/ G or more manganese ore as a catalyst, a low temperature denitration method of performing denitration at a temperature of 90 ° C or higher and 150 ° C or lower.
【請求項2】 窒素酸化物(NOx)含有排ガスからア
ンモニアを還元剤とし、触媒を用いて窒素酸化物を除去
ないし低減する低温脱硝方法において、X線回折で回折
面間隔2.15±0.05Å,2.39±0.05Å,
3.11±0.05Åにピークを有し、かつ三つのピー
クのうち2.39±0.05Åのピーク強度が最も強
く、このピークに対する他の二つのピークの強度比が
0.2以上の構造を有するマンガン鉱石を触媒として用
い、90℃以上150℃以下の温度で脱硝を行う低温脱
硝方法。
2. A low temperature denitration method in which ammonia is used as a reducing agent from a nitrogen oxide (NOx) -containing exhaust gas and a catalyst is used to remove or reduce the nitrogen oxide, and a diffraction plane interval of 2.15 ± 0. 05Å, 2.39 ± 0.05Å,
It has a peak at 3.11 ± 0.05Å and the peak intensity of 2.39 ± 0.05Å is the strongest among the three peaks, and the intensity ratio of the other two peaks to this peak is 0.2 or more. A low-temperature denitration method in which denitration is performed at a temperature of 90 ° C. or higher and 150 ° C. or lower using a structured manganese ore as a catalyst.
JP5257467A 1993-09-22 1993-09-22 Low temperature denitration method Withdrawn JPH0788334A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5257467A JPH0788334A (en) 1993-09-22 1993-09-22 Low temperature denitration method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5257467A JPH0788334A (en) 1993-09-22 1993-09-22 Low temperature denitration method

Publications (1)

Publication Number Publication Date
JPH0788334A true JPH0788334A (en) 1995-04-04

Family

ID=17306722

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5257467A Withdrawn JPH0788334A (en) 1993-09-22 1993-09-22 Low temperature denitration method

Country Status (1)

Country Link
JP (1) JPH0788334A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08173796A (en) * 1994-09-02 1996-07-09 Sakai Chem Ind Co Ltd Nitrogen oxide oxidizing adsorbent and nitrogen oxide removing method
WO1998052681A1 (en) * 1997-05-17 1998-11-26 Korea Power Engineering Company, Inc. Method for removing nitrogen oxides using natural manganese ores
KR100348142B1 (en) * 2000-05-24 2002-08-09 주식회사 매그린 A Method for Removing Stink by Ammonia And/Or Amine Using A Manganese Ore
KR20030023344A (en) * 2001-09-13 2003-03-19 주식회사 매그린 Method for Removing Ozone Using Natural Manganese Ore as a Catalyst
KR100473080B1 (en) * 2000-12-22 2005-03-08 한국전력기술 주식회사 Method for Improving NOx Removal Efficiency from Flue Gas and Reducing Consumption of Ammonia and Emission of Nitrogen Dioxide Using Modified Natural Manganese Ores
KR100686381B1 (en) * 2005-09-27 2007-02-22 한국전력기술 주식회사 Vanadium / Titania-based catalysts containing natural manganese ores for removing nitrogen oxides and dioxins over a wide range of active temperatures and methods of using them
CN116272962A (en) * 2023-03-21 2023-06-23 张永生 Catalytic material for treating automobile exhaust

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08173796A (en) * 1994-09-02 1996-07-09 Sakai Chem Ind Co Ltd Nitrogen oxide oxidizing adsorbent and nitrogen oxide removing method
WO1998052681A1 (en) * 1997-05-17 1998-11-26 Korea Power Engineering Company, Inc. Method for removing nitrogen oxides using natural manganese ores
DE19882409B3 (en) * 1997-05-17 2012-01-19 Kepco Engineering & Construction Company Process for the preparation of a catalyst, catalyst thus obtained and process for removing nitrogen oxides with the catalyst thus obtained
KR100348142B1 (en) * 2000-05-24 2002-08-09 주식회사 매그린 A Method for Removing Stink by Ammonia And/Or Amine Using A Manganese Ore
KR100473080B1 (en) * 2000-12-22 2005-03-08 한국전력기술 주식회사 Method for Improving NOx Removal Efficiency from Flue Gas and Reducing Consumption of Ammonia and Emission of Nitrogen Dioxide Using Modified Natural Manganese Ores
KR20030023344A (en) * 2001-09-13 2003-03-19 주식회사 매그린 Method for Removing Ozone Using Natural Manganese Ore as a Catalyst
KR100686381B1 (en) * 2005-09-27 2007-02-22 한국전력기술 주식회사 Vanadium / Titania-based catalysts containing natural manganese ores for removing nitrogen oxides and dioxins over a wide range of active temperatures and methods of using them
WO2007037593A1 (en) * 2005-09-27 2007-04-05 Korea Power Engineering Company, Inc. Vanadium/titania catalyst comprising natural manganese ore for removing nitrogen oxides and dioxin in wide operating temperature rangeand method of using the same
CN116272962A (en) * 2023-03-21 2023-06-23 张永生 Catalytic material for treating automobile exhaust

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