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JPS6018450B2 - Method for treating exhaust gas containing nitrogen oxides - Google Patents
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JPS6018450B2 - Method for treating exhaust gas containing nitrogen oxides - Google Patents

Method for treating exhaust gas containing nitrogen oxides

Info

Publication number
JPS6018450B2
JPS6018450B2 JP54083422A JP8342279A JPS6018450B2 JP S6018450 B2 JPS6018450 B2 JP S6018450B2 JP 54083422 A JP54083422 A JP 54083422A JP 8342279 A JP8342279 A JP 8342279A JP S6018450 B2 JPS6018450 B2 JP S6018450B2
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
oxide
nitrogen oxides
protective film
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
JP54083422A
Other languages
Japanese (ja)
Other versions
JPS567636A (en
Inventor
恭 藤田
雄三 名和
茂和 高木
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators 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 NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP54083422A priority Critical patent/JPS6018450B2/en
Publication of JPS567636A publication Critical patent/JPS567636A/en
Publication of JPS6018450B2 publication Critical patent/JPS6018450B2/en
Expired legal-status Critical Current

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

Description

【発明の詳細な説明】 本発明は各種ボイラー等から排出される窒素酸化物を含
有する排ガスの処理方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating exhaust gas containing nitrogen oxides discharged from various boilers and the like.

従来、窒素酸化物たとえばN○,N02などをアンモニ
アの存在の下で還元し、窒素と水に分解する触媒が数多
く知られている。
Conventionally, many catalysts have been known that reduce nitrogen oxides such as N◯ and N02 in the presence of ammonia and decompose them into nitrogen and water.

その代表的なものとしては例えばチタニア、バナジウム
、タングステン、モリブデン、鉄、銅等であるが、これ
らの有用な触媒を用いた場合であっても、例えば300
00以下の比較的低温度で使用した場合には、排ガス中
のS02やS03ガスとアンモニアとの反応生成物が触
媒表面に生成し触媒活性の低下をきたして耐久性に欠け
る欠点がある。また300午C以上の温度で使用した場
合にも排ガス中に含まれるダスト成分、特にアルカリ金
属塩が触媒表面に付着し徐々に触媒成分元素と反応して
アルカリ金属塩を形成すること、およびダスト成分によ
り触媒成分が摩耗すること等によって活性低下する欠点
も有していた。また触媒の活性低下以外にも、排ガス中
に含まれる大量のSQガスが触媒成分によりS03に酸
化転化されることによってアンモニアとの化合物や硫酸
ミストを形成し触媒反応装置やボイラー機材を腐食させ
てしまう等の欠点を有していた。
Typical examples include titania, vanadium, tungsten, molybdenum, iron, copper, etc. Even when these useful catalysts are used, for example, 300
When used at a relatively low temperature of 0.00 or lower, reaction products between S02 and S03 gases in the exhaust gas and ammonia are formed on the catalyst surface, resulting in a decrease in catalyst activity and a disadvantage of lack of durability. Furthermore, when used at temperatures above 300 pm, dust components contained in the exhaust gas, especially alkali metal salts, adhere to the catalyst surface and gradually react with the catalyst component elements to form alkali metal salts. It also had the disadvantage that the catalyst components were worn out by the components, resulting in a decrease in activity. In addition to the reduction in catalyst activity, a large amount of SQ gas contained in the exhaust gas is oxidized and converted to S03 by the catalyst component, forming compounds with ammonia and sulfuric acid mist, which corrodes the catalytic reaction equipment and boiler equipment. It had drawbacks such as being stowed away.

本発明者らは上記の欠点を解決すべく研究を行なった結
果、触媒の表面に酸化チタン、酸化ジルコニウム、酸化
スズの少なくも1種又は1種以上の保護膜層を担持する
ことによって触媒の活性を損うことなく硫黄酸化物やダ
スト成分を含有する排ガスを処理した場合であっても、
触媒成分が排ガス中に含まれるダスト成分によって摩耗
せず、更にダスト成分による被毒も受けず、長期間にわ
たり活性の低下が起らない150〜650ooの広い温
度範囲で極めて安定した脱硝性能を長期間にわたり維持
しうる触媒を見し、出し、本発明を成し得たものである
。すなわち本発明は、前記のような窒素酸化物の除去の
目的に使用される公知の触媒の表面に、酸化チタン、酸
化ジルコニウム、酸化スズの少なくとも1種以上からな
る1〜100ムの保護膜層を形成するもので、この保護
膜層は、触媒に担持する際には、必ずしも酸化物の形態
を有している必要はなく理持後、焼成終了時点において
酸化物の形態を有しているものであればよい。
The present inventors conducted research to solve the above-mentioned drawbacks, and found that by supporting at least one or more protective film layers of titanium oxide, zirconium oxide, and tin oxide on the surface of the catalyst, Even when exhaust gas containing sulfur oxides and dust components is treated without loss of activity,
The catalyst component is not worn out by the dust components contained in the exhaust gas, nor is it poisoned by the dust components, and has extremely stable denitrification performance over a wide temperature range of 150 to 650 oo without deterioration of activity over a long period of time. The present invention was achieved by discovering and developing a catalyst that can be maintained for a long period of time. That is, the present invention provides a protective film layer of 1 to 100 μm consisting of at least one of titanium oxide, zirconium oxide, and tin oxide on the surface of the known catalyst used for the purpose of removing nitrogen oxides as described above. This protective film layer does not necessarily have to be in the form of an oxide when it is supported on the catalyst, but it has the form of an oxide at the end of the calcination after holding. It is fine as long as it is something.

そして保護膜層は、好ましくは30%〜70%程度の気
孔率を有する多孔原村で形成され、さらにその保護膜層
を構成する粒子径は好ましくは1ム以下の粒子が95%
程度であることが最もよいものである。
The protective film layer is preferably formed of porous material having a porosity of about 30% to 70%, and the protective film layer is preferably made up of 95% particles with a particle size of 1 μm or less.
The best thing to do is to be moderate.

そして保護膜層の材質としては酸化チタン、酸化ジルコ
ニウム、酸化スズの少なくとも1種又は1種以上が最も
触媒の耐久性を向上させるうえに効果があり、それ以外
の材質では実施例に述べるように触媒の耐久性向上に顕
著な効果は認められない。また、その材質の厚さについ
ては1〜100仏が最もよく100〃を越える厚さにな
るとガスの透過性が悪くなって脱硝特性が低下する。ま
た1仏未満の薄い厚さになると、触媒の保護膜としての
効果が少なくなるので好ましくない。そして、本発明の
酸化チタン、酸化ジルコニウム、酸化スズの少なくとも
1種からなる保護膜層を調整する原料としては、酸化チ
タン、酸化ジルコニウム、酸化スズまたは加熱によりこ
れらの酸化物を生成する各種の化合物、たとえばチタン
酸、水酸化チタンン、硫酸チタン、水酸化ジルコニウム
、ハロゲン化スズ、硫酸チンなどを水、アンモニア水、
か性アルカリなどで沈殿させた水酸化物や水酸化物を加
熱分解して得た酸化チタンも好ましい原料である。また
、酸化チタン、酸化ジルコニウム、酸化スズの少なくと
も1種からなる保護膜層を触媒表面表面に担持する方法
は、適状用いられる酸化チタン、酸化ジルコニウム、酸
化スズの少なくとも1種又は1種以上からなる酸化物を
水又は必要に応じ他のバインダーや溶剤とともに解砕し
、スラリ‐状態にしてスプレー等で基材触媒上に吹付け
ても、またスラリー中に基材触媒を合浸し、その後乾燥
しついで400〜600qCで焼成してもよい。
As for the material of the protective film layer, at least one or more of titanium oxide, zirconium oxide, and tin oxide are most effective in improving the durability of the catalyst. No significant effect on improving the durability of the catalyst was observed. The thickness of the material is best between 1 and 100 mm, and if the thickness exceeds 100 mm, the gas permeability becomes poor and the denitrification properties deteriorate. Moreover, if the thickness is less than 1 mm, the effect as a protective film for the catalyst will be reduced, which is not preferable. The raw materials for preparing the protective film layer of at least one of titanium oxide, zirconium oxide, and tin oxide of the present invention include titanium oxide, zirconium oxide, tin oxide, and various compounds that produce these oxides when heated. For example, titanic acid, titanium hydroxide, titanium sulfate, zirconium hydroxide, tin halide, tin sulfate, etc. can be mixed with water, aqueous ammonia,
Hydroxide precipitated with a caustic alkali or the like and titanium oxide obtained by thermally decomposing the hydroxide are also preferred raw materials. In addition, a method for supporting a protective film layer consisting of at least one of titanium oxide, zirconium oxide, and tin oxide on the catalyst surface includes at least one or more of titanium oxide, zirconium oxide, and tin oxide, which are appropriately used. It is also possible to crush the oxide with water or other binders and solvents as necessary, make it into a slurry, and spray it onto the base catalyst, or to mix the base catalyst in the slurry and then dry it. Then, it may be fired at 400 to 600 qC.

さらに硫酸ジルコニル、硝酸ジルコニル、炭酸ジルコニ
ルアンモニゥム、塩化ジルコニル、四塩化チタン、四塩
化ジルコニウム、四塩化スズや硫酸チタンなどの溶液中
に基材触媒を含浸し、チタンやジルコニウム、スズを吸
着させ、乾燥後、400〜6004℃で焼成してもよい
。また酸化チタン、酸化ジルコニア、酸化スズの少なく
とも1種又は1種以上からなる保護膜層を担持する基材
触媒の形態は、通常用いられるビーズ形状、ハニカム形
状等の最終的な使用形態に成形された触媒が好ましい。
そしてさらに、窒素酸化物の除去を実際に行なうには、
還元剤としてアンモニアを排ガス中に窒素酸化物の0.
5モル倍以上好ましくは1〜2倍モル程度加える。
Furthermore, a base catalyst is impregnated in a solution of zirconyl sulfate, zirconyl nitrate, zirconyl ammonium carbonate, zirconyl chloride, titanium tetrachloride, zirconium tetrachloride, tin tetrachloride, titanium sulfate, etc., and titanium, zirconium, and tin are adsorbed. After drying, it may be fired at 400 to 6004°C. In addition, the form of the base catalyst supporting the protective film layer consisting of at least one or more of titanium oxide, zirconia oxide, and tin oxide may be formed into the final use form such as a commonly used bead shape or honeycomb shape. preferred catalysts.
Furthermore, in order to actually remove nitrogen oxides,
Ammonia is used as a reducing agent to reduce the amount of nitrogen oxides in the exhaust gas.
It is added by 5 moles or more, preferably about 1 to 2 moles.

また得られた混合ガスは酸化チタン、酸化ジルコニア、
酸化スズの少なくとも1種以上からなる保護膜層を表面
に担持した触媒上を空間速度(空塔基準)で200〜1
00000/時間好ま0しくは5000〜50000/
時間の範囲で通過させる。さらに反応時の温度は150
〜650qo好まし〈は250〜500℃の範囲である
。また本発明を実施する反応器の形式としては煙道ガス
の場合には処理するガスの流量が多いためタ各種の工夫
を必要とするが、基本的には通常の固定床、移動床など
固体触媒に使用する各種の反応器形式が使用しうる。
In addition, the obtained mixed gas contains titanium oxide, zirconia oxide,
The space velocity (space velocity based on the sky column) of 200 to 1
00000/hour preferably 5000-50000/hour
Let it pass within the time range. Furthermore, the temperature during the reaction is 150
-650qo is preferably in the range of 250-500°C. In addition, in the case of flue gas, various measures are required for the type of reactor in which the present invention is carried out, since the flow rate of the gas to be treated is large. A variety of reactor types for use with catalysts can be used.

次に実施例に基づいて本発明を詳細に説明する。Next, the present invention will be explained in detail based on examples.

組成比が重量%でV2051%,W035%,Ti02
94%よりなり一辺が6柳、肉厚が1柳の四角セルが3
針固からなる長さ15仇奴のハニカム形状触媒を用意し
、第1表に記載する材質よりなる保護膜層を形成するス
ラリー中にハニカム触媒を合浸し、取出し後120qo
の熱風で3M分乾燥した後、500ooで3時間の焼成
を行なって第1表に記載する本発明の保護膜層を担持し
た触媒を得た。
Composition ratio is V2051%, W035%, Ti02 in weight%
94%, 6 willows on one side, 3 square cells with wall thickness of 1 willow
Prepare a honeycomb-shaped catalyst with a length of 15 cm made of needles, dip the honeycomb catalyst into a slurry that forms a protective film layer made of the materials listed in Table 1, and after taking it out, add 120 qo of honeycomb catalyst.
After drying with hot air for 3M, the catalyst was calcined at 500 oo for 3 hours to obtain a catalyst supporting a protective film layer of the present invention as shown in Table 1.

な々この触媒の表面に坦持された保護膜層の厚さは第1
表に記載するとおりであった。これらの触媒の性能評価
は内径800、長さ1000豚のステンレス製反応器に
同一の触媒を6個充填し、B重油焚ボイラー排ガスと下
記条件で接触させて脱硝率を測定し、この脱硝率の経時
変化とS02のS03への転化率をも測定した。
The thickness of the protective film layer supported on the surface of this catalyst is
It was as described in the table. To evaluate the performance of these catalysts, six of the same catalysts were filled in a stainless steel reactor with an inner diameter of 800 mm and a length of 1,000 mm, and the NOx removal rate was measured by contacting with B heavy oil-fired boiler exhaust gas under the following conditions. The change over time and the conversion rate of S02 to S03 were also measured.

結果は第1表に示すとおりである。なお、試験排ガスに
はN0x:150〜20のpm,S0x:400〜50
蛇pm,02:3〜6%,ダクト:50の9/Nのを含
有しておりガス温度350CC,SV値10000Hr
−1,NH3/NO=1.1で耐久試験を行なったもの
である。な々N○xの測定は化学発光方式減圧型のNO
/NQ分析計(柳本製作所ECL−77A型)で行なっ
た。またSQのS03への転化率を測定する際には、ア
ンモニアの注入を止め5時間経過後にNDIR方式S0
2分析計で入口と出口のS02濃度を検出し次式により
S03への転化率を求めた。S02転化率餅0入口S0
2濃度−出口S02濃度XI。
The results are shown in Table 1. In addition, the test exhaust gas contained NOx: 150-20 pm, S0x: 400-50 pm.
Snake pm, 02: 3-6%, duct: Contains 9/N of 50, gas temperature 350CC, SV value 10000Hr
-1, a durability test was conducted at NH3/NO=1.1. Measurement of N○x is carried out using chemiluminescence method reduced pressure type NO.
/NQ analyzer (Yanagimoto Seisakusho model ECL-77A). In addition, when measuring the conversion rate of SQ to S03, stop the injection of ammonia and wait 5 hours before measuring the conversion rate of SQ to S03 using the NDIR method.
The S02 concentration at the inlet and outlet was detected using two analyzers, and the conversion rate to S03 was determined using the following equation. S02 Conversion rate Mochi 0 Entrance S0
2 concentration - outlet S02 concentration XI.

〇入口S02濃度 なお、比較のために保護膜層を施さない触媒および本発
明に規定した以外の材質および厚さの保護膜層を使用し
た触媒についても前記と同様な試験を実施し、その結果
を第1表に伴せ記載した。
〇Inlet S02 concentration For comparison, the same test as above was conducted on a catalyst without a protective film layer and a catalyst using a protective film layer of a material and thickness other than those specified in the present invention, and the results were as follows. are listed in Table 1.

S船 郷 S 雌 燐 第1表の結果より明らかなとおり、本発明の方法によれ
ば触媒の耐久性が極めてよく長期間高い脱硝率を安定し
て得ることがきるとともに、S02のS03への転化が
極めて少ないものであるのに対して、従来例および比較
例ともに触媒の耐久性が悪く、しかもS02のS03へ
の転化が極めて高いものであった。
As is clear from the results in Table 1, according to the method of the present invention, the durability of the catalyst is extremely high, and a high denitrification rate can be stably obtained for a long period of time. While the conversion was extremely low, the durability of the catalysts in both the conventional example and the comparative example was poor, and the conversion of S02 to S03 was extremely high.

以上述べたとおり、表面に1〜100仏の酸化チタン、
酸化ジルコニア、酸化スズの少なくとも1種又は1種以
上からなる保護膜層を担持した触媒の存在下で排ガスと
アンモニアと混合し150qC〜650℃の温度で窒素
酸化物の除去を行なう本発明法によれば、従来の保護膜
層のない触媒を用いる場合と比べて触媒の耐久性が向上
するだけでなく排ガス中のS02をS03に転化する酸
化反応も抑制するという極めて優れた効果を有するもの
であり、各種の燃焼炉より排出される排ガス中の窒素酸
化物を長期間安定して高率に除去できるものであって、
産業上極めて有用な窒素酸化物の処理方法である。
As mentioned above, titanium oxide of 1 to 100 degrees on the surface,
In the method of the present invention, nitrogen oxides are removed at a temperature of 150 qC to 650 °C by mixing exhaust gas and ammonia in the presence of a catalyst carrying a protective film layer consisting of at least one or more of zirconia oxide and tin oxide. According to the research, this method not only improves the durability of the catalyst compared to conventional catalysts without a protective film layer, but also has an extremely excellent effect of suppressing the oxidation reaction that converts S02 in exhaust gas to S03. It is capable of removing nitrogen oxides from exhaust gas emitted from various combustion furnaces stably and at a high rate over a long period of time.
This is an industrially extremely useful method for treating nitrogen oxides.

Claims (1)

【特許請求の範囲】[Claims] 1 窒素酸化物を含有する排ガスを、表面に1〜100
μの酸化チタン、酸化ジルコニウム、酸化スズの少なく
とも1種以上からなる保護膜層を担持した触媒の存在下
でアンモニアと混合、150〜650℃の温度範囲で加
熱することを特徴とする窒素酸化物を含有する排ガスの
処理方法。
1 Exhaust gas containing nitrogen oxides is applied to the surface at 1 to 100%
Nitrogen oxide, which is mixed with ammonia in the presence of a catalyst supporting a protective film layer consisting of at least one of titanium oxide, zirconium oxide, and tin oxide of μ, and heated in a temperature range of 150 to 650°C. A method for treating exhaust gas containing
JP54083422A 1979-07-03 1979-07-03 Method for treating exhaust gas containing nitrogen oxides Expired JPS6018450B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP54083422A JPS6018450B2 (en) 1979-07-03 1979-07-03 Method for treating exhaust gas containing nitrogen oxides

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP54083422A JPS6018450B2 (en) 1979-07-03 1979-07-03 Method for treating exhaust gas containing nitrogen oxides

Publications (2)

Publication Number Publication Date
JPS567636A JPS567636A (en) 1981-01-26
JPS6018450B2 true JPS6018450B2 (en) 1985-05-10

Family

ID=13801990

Family Applications (1)

Application Number Title Priority Date Filing Date
JP54083422A Expired JPS6018450B2 (en) 1979-07-03 1979-07-03 Method for treating exhaust gas containing nitrogen oxides

Country Status (1)

Country Link
JP (1) JPS6018450B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62108750U (en) * 1985-12-24 1987-07-11

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57174143A (en) * 1981-04-18 1982-10-26 Babcock Hitachi Kk Catalyst for denitration

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62108750U (en) * 1985-12-24 1987-07-11

Also Published As

Publication number Publication date
JPS567636A (en) 1981-01-26

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