JPS6012907B2 - Method for regenerating nitrogen oxide purification catalyst - Google Patents
Method for regenerating nitrogen oxide purification catalystInfo
- Publication number
- JPS6012907B2 JPS6012907B2 JP52060446A JP6044677A JPS6012907B2 JP S6012907 B2 JPS6012907 B2 JP S6012907B2 JP 52060446 A JP52060446 A JP 52060446A JP 6044677 A JP6044677 A JP 6044677A JP S6012907 B2 JPS6012907 B2 JP S6012907B2
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- hydrogen
- activity
- water
- treatment
- 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
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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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/50—Improvements relating to the production of bulk chemicals
- Y02P20/584—Recycling of catalysts
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Description
【発明の詳細な説明】
本発明は窒素酸化物(たとえば酸化窒素N○、二酸化窒
素N02、など以下N○xと略記する。DETAILED DESCRIPTION OF THE INVENTION The present invention uses nitrogen oxides (for example, nitrogen oxide N◯, nitrogen dioxide N02, etc., hereinafter abbreviated as N◯x).
)浄化用触媒の再生方法に関する。詳しく述べると本発
明は、N0x含有ガズ中にアンモニアを添加し、N○x
を接触的に窒素と水とに転化するための触媒の再生方法
に関するものである。ボイラーからの排ガスや化学工業
プラント、鉄鉱石隣鯖炉およびガラス溶解炉などからの
排ガス中にはN0xが含有されこのN○xを除去浄化す
るための方法としてN○xをアンモニアと共に触媒上を
通過せしめて接触的に反応を行ない、N0xを選択的に
無害な窒素と水とに転化する方法が広く知られている。) Relating to a method for regenerating a purification catalyst. To explain in detail, the present invention adds ammonia to NOx-containing gas, and
The present invention relates to a method for regenerating a catalyst for catalytically converting nitrogen into nitrogen and water. Exhaust gas from boilers, chemical industry plants, iron ore furnaces, glass melting furnaces, etc. contains NOx, and as a method to remove and purify this N○x, it is passed over a catalyst together with ammonia. A widely known method is to selectively convert NOx into harmless nitrogen and water by passing it through and carrying out a catalytic reaction.
この方法に使用される触媒としては、アルミナ、シリカ
、シリカアルミナ、酸化チタンなどの坦体に銅、鉄、バ
ナジウム、タングステンなどの金属酸化物を活性成分と
して恒侍し、あるいは混合して成型してなる触媒が知ら
れている。The catalyst used in this method is a carrier such as alumina, silica, silica-alumina, or titanium oxide in which metal oxides such as copper, iron, vanadium, or tungsten are kept as active ingredients, or mixed and formed. There are known catalysts.
そして、これらの触媒はLNG焚きボイラーなどのクリ
ーン排ガスに使用する限り、触媒活性をほとんど低下さ
せることなく長期にわたり安定したN○x浄化の性能が
認められるものである。しかしながら、N○x浄化の対
象となる排ガスの多くはガス中に硫黄酸化物(たとえば
二酸化硫黄S02、三酸化硫黄S03など以下S○xと
略記する。)やダストなどが含まれ、これらの影響で上
記触媒の活性は経時的に低下する頃向が見られる。本発
明者らが上記種々の触媒について、その活性の低下原因
を詳細に検討したところ、触媒毒を形成するものとして
、ダスト中の金属酸化物、緋ガス中のS○x、そして排
ガスに添加されたアンモニアから生成する硫酸アンモニ
ウム、酸性硫酸アンモニウムなどが知見され、ダスト中
の金属酸化物は、触媒に付着し触媒の比表面積や紬孔容
積を減少させ、そればかりか、特に鉄鉱石暁結炉及びガ
ラス熔解炉排ガスを対象とする場合には、ナトリウム、
カリウム等のアルカリ金属の化合物やマグネシウム、カ
ルシウム等のアルカリ士類金属の化合物が触媒に対し化
学的にも作用し、またS○x、硫酸アンモニウムおよび
酸性硫酸アンモニウムなどは担体成分や触媒成分と結合
して硫酸塩や酸性硫酸塩のような化合物あるいはコンプ
レックスを形成し、これらの結果触媒活性の低下をきた
すことが知見された。As long as these catalysts are used for clean exhaust gas from LNG-fired boilers and the like, stable N*x purification performance over a long period of time is recognized with almost no reduction in catalytic activity. However, many of the exhaust gases targeted for N○x purification contain sulfur oxides (for example, sulfur dioxide S02, sulfur trioxide S03, etc., hereinafter abbreviated as S○x), dust, etc. It can be seen that the activity of the above catalyst tends to decrease over time. The present inventors investigated in detail the causes of the decrease in the activity of the various catalysts mentioned above, and found that metal oxides in dust, S○x in scarlet gas, and substances added to exhaust gas form catalyst poisons. It has been discovered that ammonium sulfate, acidic ammonium sulfate, etc. are produced from the ammonia produced by dust, and metal oxides in dust adhere to the catalyst and reduce the specific surface area and pore volume of the catalyst. When targeting glass melting furnace exhaust gas, sodium,
Compounds of alkali metals such as potassium and compounds of alkali metals such as magnesium and calcium act chemically on the catalyst, and S○x, ammonium sulfate, and acidic ammonium sulfate combine with carrier components and catalyst components. It has been found that compounds or complexes such as sulfates and acidic sulfates are formed, resulting in a decrease in catalytic activity.
このような活性の低下した触媒を再生する方法としては
、付着物質を物理的に取り除く方法や水洗により除去す
る方法が知られている。As a method for regenerating such a catalyst whose activity has decreased, there are known methods of physically removing adhering substances and methods of removing them by washing with water.
しかしながら、前者の方法で付着物質を未使用の触媒に
近い状態までに除去することは困難であり、また後者の
方法は決して得策ではないことが判明した。すなわち、
本発明者らが知見したところでは、上述のように活性の
低下した触媒を水洗すると、触媒の強度が著しく低下し
た。そして、その原因を検討すると、活性の低下した触
媒中には硫黄化合物の蓄積が認められ、これらが水洗処
理の際、触媒内部で強酸性の水溶液となって触媒成分を
溶解流失するとか水可溶性の含硫黄化合物に変質した触
媒物質もまた水性媒体による洗浄処理の際に流失するた
めであることが判明した。したがって触媒内部に蓄積し
た硫黄化合物に基づく強酸性水溶液に溶解する成分とか
それ自身が水可溶性含硫黄化合物に変質する成分から構
成された触媒の再生賦活法において単に水性媒体による
洗浄法を適用することは十分に有効とはいえない。本発
明者らは、したがって上記の公知の方法に代わる活性低
下触媒の再生法を提供する目的を持って、研究したとこ
ろ活性の低下した触媒を水素雰囲気中、加熱処理した後
、水性媒体、即ち水もしくはアンモニア溶液もしくは酸
性溶液で洗浄することを特徴とする本発明を完成するに
至ったものである。However, it has been found that it is difficult to remove the adhering substances to a state close to that of an unused catalyst using the former method, and that the latter method is by no means a good idea. That is,
The present inventors have found that when a catalyst whose activity has been reduced as described above is washed with water, the strength of the catalyst is significantly reduced. When examining the cause, it was found that sulfur compounds accumulate in the catalyst with decreased activity, and when washed with water, these become a strongly acidic aqueous solution inside the catalyst, dissolving the catalyst components and causing them to become water-soluble. It has been found that this is because the catalyst material that has changed into a sulfur-containing compound is also washed away during the cleaning treatment with an aqueous medium. Therefore, simply applying a cleaning method using an aqueous medium in a reactivation method for a catalyst that is composed of components that dissolve in a strongly acidic aqueous solution based on sulfur compounds accumulated inside the catalyst, or components that themselves transform into water-soluble sulfur-containing compounds. cannot be said to be sufficiently effective. Therefore, the present inventors conducted research with the aim of providing a method for regenerating a catalyst with decreased activity as an alternative to the above-mentioned known method. After heat-treating the catalyst with decreased activity in a hydrogen atmosphere, The present invention, which is characterized by washing with water, an ammonia solution, or an acidic solution, has been completed.
本発明方法により示される効果の第1は、水素雰囲気下
で活性の低下した触媒を処理することにより触媒に蓄積
した硫黄化合物が除去され活性が回復する点である。The first effect exhibited by the method of the present invention is that by treating a catalyst whose activity has decreased in a hydrogen atmosphere, sulfur compounds accumulated in the catalyst are removed and the activity is restored.
本発明方法によれば、活性低下した触媒を500℃以下
、好ましくは200〜450o○の温度で処理すること
の有効性が認められた。According to the method of the present invention, the effectiveness of treating the catalyst whose activity has been reduced at a temperature of 500° C. or lower, preferably 200 to 450° C. has been recognized.
また、本発明方法により示される効果の第2は、水素雰
囲気下の処理により触媒の担体や触媒の活性成分中に生
成した水可溶性化合物が灘溶ないし不溶物に変化せしめ
られ、以後の水性媒体による洗浄操作時に溶出すること
を防止出来るということである。The second effect exhibited by the method of the present invention is that the water-soluble compounds generated in the catalyst carrier and the active components of the catalyst are changed into soluble or insoluble substances by the treatment under a hydrogen atmosphere, and are used in the subsequent aqueous medium. This means that it can prevent elution during cleaning operations.
第2の効果の必要性は触媒に対し無用ないし触媒毒とな
る劣化触媒に蓄積したダスト成分を水洗などによって十
分に除去せねばならないからである。本発明方法により
示される効果の第3は、水素雰囲気下処理された触媒を
水もしくはアンモニア溶液もしくは酸性溶液等の水性媒
体で洗浄することにより、触媒に蓄積したダストが除去
され触媒活性が回復する点である。The second effect is necessary because the dust components accumulated on the deteriorated catalyst, which are useless or poisonous to the catalyst, must be sufficiently removed by washing with water or the like. The third effect exhibited by the method of the present invention is that by washing the catalyst treated under a hydrogen atmosphere with an aqueous medium such as water, ammonia solution, or an acidic solution, the dust accumulated on the catalyst is removed and the catalytic activity is restored. It is a point.
触媒に蓄積したダストによって洗浄の効果は異なり、水
洗、アンモニア溶液による洗浄、酸性溶液による洗浄を
適宜選択することで十分に効果が認められる。本発明の
触媒再生方法は、特に競結炉、ガラス熔解炉排ガス等の
ごとく、硫黄酸化物の他のダスト成分としてアルカリ金
属化合物を含む排ガスの脱硝に使用して劣化した触媒を
対象とする場合に顕著な効果が認められる。The cleaning effect varies depending on the dust accumulated on the catalyst, and sufficient effects can be recognized by appropriately selecting washing with water, washing with an ammonia solution, or washing with an acidic solution. The catalyst regeneration method of the present invention is particularly applicable to catalysts that have deteriorated by being used for denitrification of exhaust gas that contains alkali metal compounds as dust components other than sulfur oxides, such as exhaust gas from competitive furnaces and glass melting furnaces. A remarkable effect was observed.
本発明方法においては、水素雰囲気中処理する場合、気
相状態で水素処理することが適しているが、適当な溶媒
中で水素処理してもさしつかえがない。In the method of the present invention, when the treatment is carried out in a hydrogen atmosphere, it is suitable to carry out the hydrogen treatment in a gas phase, but it is also possible to carry out the hydrogen treatment in a suitable solvent.
処理温度は50〜500ooであるが、200qo以下
では還元速度が遅いとか、還元効率が悪い等の欠点があ
り、また450qo以上の高温では昇温に伴う経済的損
失などのため、処理温度としてとくに好ましくは200
〜450ooの範囲が選ばれる。The processing temperature is 50 to 500oo, but if it is less than 200qo, there are disadvantages such as slow reduction rate or poor reduction efficiency, and if it is high temperature above 450qo, there will be economic loss due to temperature rise, so Preferably 200
A range of ˜450oo is chosen.
水素を気相状態で用いる場合、窒素で希釈して用いるの
が通常であるが、水素単独ガスでも、また一酸化炭素、
炭酸ガス、水蒸気等で希釈して使用することもできる。
用いられる水素量については、触媒の劣化状態によって
異なるものである。水素量を充分用いる程効果は大きい
が経済的でなく、その判断の目安は、活性の低下した触
媒中に蓄積した硫黄量によって水素量を決定することが
好ましい。すなわち、活性の低下した触媒中の硫黄量の
0.5〜90とくに好ましくは2〜25モル倍の水素を
用いることが好ましい。処理圧力は特に制限がないが、
通常常圧で効果を挙げることができる。処理する方法は
、移動床反応器を用いる場合には、別に設けた水素含有
ガスを導入し得る加熱炉に、反応系外に抜き出した活性
の低下した触媒を入れ、昇塩するものであるが、通常の
還元炉がこの場合適している。もっとも、N○x浄化用
触媒を反応器に充填したままの状態でN○x含有ガスの
代りに水素含有ガスを供給して再生処理する方法が工業
的には採用しうる。都市ガスなどの原料として多量に供
給される石炭ガス、水性ガス、発生炉ガス、油分解ガス
なども本発明方法の水素含有ガスとして使用しうる。も
ちろん、これらのガスは脱硫処理されたのち使用される
のが好ましい。水素によって処理される機構については
、触媒中に蓄積した硫黄分が二酸化硫黄および硫化水素
等になり触媒中から除去されることが認められた。暁給
炉ガスを対象としたような、被毒性の強いダストが多量
に付着した触媒の再生には、水素雰囲気中、加熱処理し
た後に触媒を洗浄することが必要であるが、この洗浄方
法としては、水、もしくはアンモニア溶液、もしくは酸
性溶液が適宜に洗浄液として用いることができる。When hydrogen is used in a gas phase, it is usually diluted with nitrogen, but hydrogen alone can also be used as a gas, as well as carbon monoxide,
It can also be used after being diluted with carbon dioxide gas, water vapor, etc.
The amount of hydrogen used varies depending on the state of deterioration of the catalyst. Although the effect is greater if a sufficient amount of hydrogen is used, it is not economical, and it is preferable to determine the amount of hydrogen based on the amount of sulfur accumulated in the catalyst whose activity has decreased. That is, it is preferable to use hydrogen in an amount of 0.5 to 90 times, particularly preferably 2 to 25 times, the amount of sulfur in the catalyst with reduced activity. There are no particular restrictions on the processing pressure, but
It is usually effective under normal pressure. When using a moving bed reactor, the treatment method is to place the catalyst with reduced activity extracted from the reaction system into a separately provided heating furnace into which hydrogen-containing gas can be introduced, and to raise the salt content. , a conventional reduction furnace is suitable in this case. However, it is possible to adopt industrially a method of regenerating the catalyst by supplying a hydrogen-containing gas instead of the N○x-containing gas while the reactor is still filled with the N○x purification catalyst. Coal gas, water gas, generator gas, oil cracking gas, etc., which are supplied in large quantities as raw materials for city gas, etc., can also be used as the hydrogen-containing gas in the method of the present invention. Of course, it is preferable that these gases be used after being desulfurized. Regarding the mechanism of treatment with hydrogen, it was confirmed that the sulfur content accumulated in the catalyst becomes sulfur dioxide, hydrogen sulfide, etc. and is removed from the catalyst. To regenerate a catalyst that has a large amount of highly toxic dust attached to it, such as one used for Akatsuki feeder gas, it is necessary to clean the catalyst after heat treatment in a hydrogen atmosphere. Water, an ammonia solution, or an acidic solution can be appropriately used as the cleaning liquid.
洗浄液の選択は触媒活性成分および触媒上のダストの種
類によって決まるものである。例えば触媒上に付着した
アルカリ金属化合物を除去する場合、酸性溶液で洗浄す
ることが好ましいが、水もしくはアンモニア溶液でも十
分洗浄することで効果は認められる。本発明に使用する
アンモニア溶液とはpHが8〜13のものであり、通常
アンモニア水溶液が使用される。The choice of cleaning fluid depends on the catalyst active components and the type of dust on the catalyst. For example, when removing an alkali metal compound adhering to the catalyst, it is preferable to wash with an acidic solution, but sufficient washing with water or an ammonia solution can also be effective. The ammonia solution used in the present invention has a pH of 8 to 13, and an aqueous ammonia solution is usually used.
また本発明に使用する酸性溶液とはpHが2〜6のもの
であり、通常硝酸の希薄水溶液が使用される。また洗浄
液は上記溶液を組合せて使用することもできる。洗浄時
における洗浄液の温度および圧力には特に制限がないが
、通常10〜80午0の温度で常圧で処理することがで
きる。Further, the acidic solution used in the present invention has a pH of 2 to 6, and usually a dilute aqueous solution of nitric acid is used. Moreover, the cleaning liquid can also be used in combination with the above solutions. There are no particular restrictions on the temperature and pressure of the cleaning solution during cleaning, but the treatment can usually be carried out at a temperature of 10 to 80 o'clock and normal pressure.
本発明における洗浄処理方法としては、ベルト上あるい
は容器内に活性の低下した触媒をとり、この上に洗浄液
を流下させて洗浄処理する方法、あるいは洗浄液の入っ
た容器に活性の低下した触媒を浸潰させ、静層もしくは
燈梓下洗浄処理するなどがある。The cleaning method of the present invention includes a method in which a catalyst with decreased activity is placed on the belt or in a container and a cleaning solution is poured onto the catalyst, or a catalyst with decreased activity is immersed in a container containing the cleaning solution. It can be crushed and treated with a static layer or under-washing treatment.
洗浄の効果は、洗浄液中のダスト金属化合物の濃度を原
子吸光分析等で分析し、その濃度の減少割合で知ること
ができる。The effectiveness of cleaning can be determined by analyzing the concentration of dust metal compounds in the cleaning solution using atomic absorption spectroscopy or the like and determining the rate of decrease in the concentration.
また洗浄処理の後で処理された触媒を20ぴ0以下で乾
燥することが好ましい。以上の方法によって得られた再
生触媒のN○x浄化性能は、活性の低下した触媒に比べ
て著しく増加し、未使用の触媒と同等またはそれ以上に
回復している。Further, it is preferable to dry the treated catalyst after the washing treatment at a temperature of 20 mm or less. The N*x purification performance of the regenerated catalyst obtained by the above method is significantly increased compared to the catalyst whose activity has decreased, and has recovered to the same level or higher than that of the unused catalyst.
また触媒の圧嬢強度もこの再生処理によってほとんど低
下は認められなかった。以下に実施例を用いて本発明を
更に詳細に説明するが、本発明はこれら実施例のみに限
定されるものではない。Furthermore, the crushing strength of the catalyst was hardly reduced by this regeneration treatment. The present invention will be explained in more detail below using Examples, but the present invention is not limited to these Examples.
実施例 1電気集塵機を用し、含塵量を40の9′Nの
にした鉄鉱石暁結炉排ガスにアンモニア(Nは)を添加
してN○x浄化用反応器に供給した。Example 1 Using an electrostatic precipitator, ammonia (N) was added to iron ore sintering furnace exhaust gas whose dust content was adjusted to 409'N, and the mixture was supplied to a reactor for purification of N○x.
排ガス組成は平均してN0x180脚、S○x25■m
、酸素1弦容量%、一酸化炭素0.虫容量%、炭酸ガス
8容量%、水蒸気10容量%、残り窒素であり、NH3
/N○x=1.2(モル比)となるようにNH3を添加
してなるものである。The average exhaust gas composition is NO x 180 m, S○ x 25 m
, oxygen 1 string volume %, carbon monoxide 0. insect volume %, carbon dioxide gas 8 volume %, water vapor 10 volume %, remaining nitrogen, NH3
NH3 is added so that /N○x=1.2 (molar ratio).
反応器に充填した触媒は酸化物としての重量組成比でV
205:Ti02=10:90(重量比)なるものを押
出し成型し、これを空気中10時間400ooで焼成し
てなるものである。The catalyst packed in the reactor has a weight composition ratio of V as an oxide.
205:Ti02=10:90 (weight ratio) was extrusion molded, and this was fired in air at 400 oo for 10 hours.
反応器は金網支持の円筒形のもので、上記触媒粒子を充
填してなり、これに上記排ガスを空間速度800皿r‐
1(STP)、ガス入口温度を260q0の温度で延1
50加持間の活性テストに供した。The reactor is a cylindrical one supported by a wire mesh, filled with the above catalyst particles, and into which the above exhaust gas is fed at a space velocity of 800 r-
1 (STP), the gas inlet temperature is extended at a temperature of 260q0.
It was subjected to an activity test for 50 cycles.
この間1日1回触媒を排ガスで流動化してダストによる
触媒層の閉塞を防止した。触媒の経時変化を見るため、
活性、触媒の物性および触媒に蓄積した化合物について
それぞれ測定し、第1表に示す結果をえた。During this period, the catalyst was fluidized with exhaust gas once a day to prevent clogging of the catalyst layer by dust. To see the changes in the catalyst over time,
The activity, physical properties of the catalyst, and compounds accumulated on the catalyst were measured, and the results shown in Table 1 were obtained.
活性についてはN○xの浄化率をN○x計(ケミルミ式
)で測定し、触媒の分析については、比表面積をBET
法による表面積計で、また触媒に蓄積した化合物につい
ては蟹光X線分析で測定した。そして、活性の低下した
触媒約lk9を還元炉に入れ、窒素ガスで置換してから
水素を5容量%含む窒素ガスを35そ/分(STP)の
流速で流し、40000で3時間処理した。For activity, the purification rate of N○x was measured using an N○x meter (Chemilumi type), and for analysis of the catalyst, the specific surface area was measured using BET.
Compounds accumulated on the catalyst were measured by crab light X-ray analysis. Then, about 1k9 of the catalyst with reduced activity was placed in a reduction furnace, and after replacing with nitrogen gas, nitrogen gas containing 5% by volume of hydrogen was flowed at a flow rate of 35 SO/min (STP) and treated at 40,000 for 3 hours.
次に温水が2そ入った容器に水素処理された触媒を加え
、6000に保つたまま2時間放置し、洗浄水を抜く。Next, add the hydrogen-treated catalyst to a container containing two bottles of hot water, leave it at 6,000 ℃ for 2 hours, and drain the washing water.
この操作を4回線返した後、処理された触媒を120℃
で1畑時間乾燥した。この時洗浄液中のバナジウム、チ
タンおよびカリウム等の濃度を源子吸光分析によって測
定し、第2表に示す結果をえた。このようにして再生処
理した触媒の強度は未使用の触媒と変らず、またNOx
浄化性能や物性なども第1表に示す如くほとんど同じ状
態に回復していた。After repeating this operation four times, the treated catalyst was heated to 120°C.
The field was dried for one hour. At this time, the concentrations of vanadium, titanium, potassium, etc. in the cleaning solution were measured by source absorption spectrometry, and the results shown in Table 2 were obtained. The strength of the catalyst regenerated in this way is the same as that of an unused catalyst, and the NOx
The purification performance and physical properties were also restored to almost the same state as shown in Table 1.
第1表
未使用触媒 1,500時間使用 再生触
媒N○x浄化率(%) 93
73 93比表面積(が/夕)
35 18 3
5触媒中の硫黄(重量雑) 0.08
4.80 0.12触
媒中のカリウム(重量滋) −
1.75 0.08第2表(元素燐
/淡)
第1回第2回第3回第4回
バナジウム 0.033 0.039 0.047 0
.047チ タ ン 0.007 0.007 0.0
06 0.001カリウム 4.87 1.84
0.72 0.19比較例 1実施例1に示された活
性の低下した触媒を水素処理せずに実施例1と同様にし
て水洗した。Table 1 Unused catalyst Used for 1,500 hours Regenerated catalyst N○x purification rate (%) 93
73 93 Specific surface area (ga/even)
35 18 3
5 Sulfur in catalyst (weight miscellaneous) 0.08
4.80 0.12 Potassium in catalyst (weight) −
1.75 0.08 Table 2 (Elemental phosphorus/light) 1st 2nd 3rd 4th Vanadium 0.033 0.039 0.047 0
.. 047 Titanium 0.007 0.007 0.0
06 0.001 potassium 4.87 1.84
0.72 0.19 Comparative Example 1 The catalyst with reduced activity shown in Example 1 was washed with water in the same manner as in Example 1 without being subjected to hydrogen treatment.
洗浄液中に熔解した元素の濃度を実施例1と同様にして
測定し、第3表の結果を得た。水洗処理によって触媒は
割れ、強度は弱くなった。The concentration of elements dissolved in the cleaning solution was measured in the same manner as in Example 1, and the results shown in Table 3 were obtained. The water washing treatment cracked the catalyst and weakened its strength.
洗浄液中に触媒成分が港出しており、水素処理した後水
洗する本発明の方法が優れていることがわかる。第
3 表 (元素燐/雌)
第1回 第2回 第3回 第4回
バナジウム 4.74 2.60 1.18
0.66チ タ ン 2.32 2.18
1.82 1.18第1回 第2回 第3回 第4回
カリウム 4.72 2.05 0.66 0
.16実施例 2NOX浄化用触媒として、汀j02・
P205の組成をもつリン酸チタンを用い、V2Q:リ
ン酸チタン=30:70(重量比)なる組成の触媒を空
間速度700肌r‐1(STP)、ガス入口温度280
qo、使用時間延150加時間とするほかはまった〈実
施例1の方法と同様にしてN○x浄化反応に供し、第4
表に示す結果をえた。It can be seen that the catalyst component was released into the cleaning solution, and the method of the present invention, which involves hydrogen treatment and then washing with water, is superior. No.
3 Table (Elemental phosphorus/female) 1st 2nd 3rd 4th Vanadium 4.74 2.60 1.18
0.66 Titanium 2.32 2.18
1.82 1.18 1st 2nd 3rd 4th Potassium 4.72 2.05 0.66 0
.. 16 Example 2 As a catalyst for purification of NOx, TAJ02.
Using titanium phosphate with a composition of P205, a catalyst with a composition of V2Q: titanium phosphate = 30:70 (weight ratio) was heated at a space velocity of 700 skin r-1 (STP) and a gas inlet temperature of 280.
qo, except that the usage time was increased to 150 hours.
We obtained the results shown in the table.
活性の低下した触媒約lk9を還元炉に入れ、窒素ガス
で置換してから水素を2畔容量%含む窒素ガスを10そ
/分(STP)の流速で流し、370qoで4時間処理
した。Approximately 1k9 of the catalyst with reduced activity was placed in a reduction furnace, replaced with nitrogen gas, and nitrogen gas containing 2% by volume of hydrogen was flowed at a flow rate of 10 som/min (STP), and treated at 370 qo for 4 hours.
次に0.3%の硝酸水溶液2そで60℃で洗浄処理を3
回行なった。Next, wash with 2 sleeves of 0.3% nitric acid solution at 60°C for 3 times.
I went around.
洗浄液中に溶解した元素の濃度を実施例1と同様にして
測定し、第5表の結果を得た。再生処理した触媒は触媒
の強度、活性共に禾使用の触媒とほとんど同じ状態に回
復していた。The concentration of elements dissolved in the cleaning solution was measured in the same manner as in Example 1, and the results shown in Table 5 were obtained. Both the strength and activity of the regenerated catalyst had been restored to almost the same state as the catalyst using clay.
第4表未使用触媒 1,500時間使用
再生触媒NOX浄化率(多) 92
82 92比表面積(材/
夕) 16 11
16触媒中の硫黄(重量努) 0
.02 3.76 0
.08触媒中のカリウム(重量※)
1.40 0.04第
5 表 (元素の夕/cZ)第1回 第2回 第3
回
バナジウム 0.13 0.11
0.14チ タ ン 0.014 0.005
0.002カリウ ム 3‐24
2.19 1.17比較例 2実施例2に示さ
れた活性の低下した触媒を水素処理せずに実施例2と同
様にして硝酸水溶液で洗浄した。Table 4 Unused catalyst Used for 1,500 hours
Regenerated catalyst NOX purification rate (high) 92
82 92 Specific surface area (material/
Evening) 16 11
16 Sulfur in catalyst (by weight) 0
.. 02 3.76 0
.. 08 Potassium in catalyst (weight*)
1.40 0.04th
5 Table (Evening of the Elements/cZ) 1st 2nd 3rd
Vanadium 0.13 0.11
0.14 Titanium 0.014 0.005
0.002 Potassium 3-24
2.19 1.17 Comparative Example 2 The catalyst with reduced activity shown in Example 2 was washed with an aqueous nitric acid solution in the same manner as in Example 2 without being subjected to hydrogen treatment.
洗浄液中に溶解した元素の濃度を実施例1と同様にして
測定し、第6表の結果をえた。The concentration of elements dissolved in the cleaning solution was measured in the same manner as in Example 1, and the results shown in Table 6 were obtained.
硝酸水溶液処理によって触媒は割れ、強度は弱くなった
。The catalyst cracked and its strength weakened due to treatment with nitric acid aqueous solution.
洗浄液中に触媒成分が溶出しており、水素処理した後硝
酸水溶液で洗浄する本発明の方法が優れていることがわ
かる。第 6 表 (元素燐/雌)
第1回 第2回 第3回
バナジウム 7.10 5.79
3.81チ タ ン 0.85 0.
75 0.34カリウム 2.75
1.88 1.10☆実施例 3N○x浄化用触媒
として、y−ァルミナ迫体を四塩化チタンで処理し、y
−N203:Ti02=70:20(重量比)のチタン
処理y−アルミナ担体とし、この担体をバナジン酸アン
モニウム水溶液に合浸してあとは実施例1におけると同
様にしてV2Q:Ti02:ッ−山203=10:20
:70(重量比)の組成の触媒を調製した。The catalyst component was eluted into the cleaning solution, indicating that the method of the present invention, which involves hydrogen treatment and then cleaning with a nitric acid aqueous solution, is superior. Table 6 (Element phosphorus/female) 1st 2nd 3rd Vanadium 7.10 5.79
3.81 Titanium 0.85 0.
75 0.34 Potassium 2.75
1.88 1.10 ☆Example As a catalyst for 3N○x purification, y-alumina morsel was treated with titanium tetrachloride, and y
A titanium-treated y-alumina carrier with -N203:Ti02=70:20 (weight ratio) was used, and this carrier was immersed in an aqueous ammonium vanadate solution, and the rest was carried out in the same manner as in Example 1. =10:20
:70 (weight ratio).
この触媒を、空間速度500皿r‐1(STP)、使用
時間延150畑時間とするほかはまった〈実施例1の方
法と同様にしてN○x浄化反応に供し、第7表に示す結
果をえた。This catalyst was subjected to the N○x purification reaction in the same manner as in Example 1 except that the space velocity was 500 dish r-1 (STP) and the total usage time was 150 field hours.The results are shown in Table 7. I got it.
活性の低下した触媒を350qoの温度で5容量%の水
素を含む窒素ガスを65そ/分(STP)で4時間流通
させ水素処理を行った。Hydrogen treatment was carried out through the catalyst with reduced activity by flowing nitrogen gas containing 5% by volume of hydrogen at 65 SO/min (STP) for 4 hours at a temperature of 350 qo.
次に2.3%のアンモニア水溶液2〆、25℃で洗浄処
理を3回行った。Next, washing treatment was performed three times at 25° C. with 2.3% ammonia aqueous solution.
洗浄液中に溶解した元素の濃度を実施例1と同様にして
測定し、第8表の結果を得た。再生処理した触媒は、触
媒の強度、活性共に未使用の触媒とほとんど同じ状態に
回復していた。The concentration of elements dissolved in the cleaning solution was measured in the same manner as in Example 1, and the results shown in Table 8 were obtained. The regenerated catalyst had recovered to almost the same strength and activity as the unused catalyst.
第7表未使用触媒 1,500時間使用
再生触媒NOX浄化率(略) 93
66 90比表面積(で/夕
) 78 42
75触媒中の硫黄(重量%) 0
.01 7.84
0.83触媒中のカリウム(重量多)
0.78 0.
03第 8 表 (元素物/め)第1回 第2回 第
3回
バナジウム 0.084 0.103
0.102チ タ ン 0.008 0.00
5 0.001カリウム 1.72 1.
14 0.69比較例 3実施例3に示された活性
の低下した触媒を水素処理せずに実施例3とまったく同
様にアンモニア水溶液で処理し、第9表の結果を得た。Table 7 Unused catalyst Used for 1,500 hours
Regenerated catalyst NOX purification rate (omitted) 93
66 90 Specific surface area (de/y) 78 42
75 Sulfur in catalyst (wt%) 0
.. 01 7.84
0.83 Potassium in catalyst (by weight)
0.78 0.
03 Table 8 (Elements/Metals) 1st 2nd 3rd Vanadium 0.084 0.103
0.102 Titanium 0.008 0.00
5 0.001 potassium 1.72 1.
14 0.69 Comparative Example 3 The catalyst with reduced activity shown in Example 3 was treated with an ammonia aqueous solution in exactly the same manner as in Example 3 without being subjected to hydrogen treatment, and the results shown in Table 9 were obtained.
水洗処理により触媒の強度は比較例1と同様に触媒は割
れ強度は弱くなった。第 9 表 (元素の夕/磯)
第1回 第2回 第3回
バナジウム 3.46 1.80
0.94チ タ ン 1.36 1.29
1.11カリウム 1.58 1.2
4 0.56実施例 4N○x浄化用触媒としてV
205:Ti02:Si02i15:72:13なる組
成の触媒を用いたほかは実施例1の方法と同様にしてN
○x浄化反応に供し、第10表に示す結果をえた。As a result of the water washing treatment, the strength of the catalyst was similar to that of Comparative Example 1, and the cracking strength of the catalyst was weakened. Table 9 (Evening of the Elements/Iso) 1st 2nd 3rd Vanadium 3.46 1.80
0.94 Titanium 1.36 1.29
1.11 Potassium 1.58 1.2
4 0.56 Example 4N○x purification catalyst V
205:Ti02:Si02i15:72:13 N
○x It was subjected to a purification reaction, and the results shown in Table 10 were obtained.
活性の低下した触媒を400℃の温度で約50%の水素
を含む石炭ガスを4と/分(STP)で3時間流通させ
水素処理した。The catalyst with reduced activity was subjected to hydrogen treatment by flowing coal gas containing about 50% hydrogen at a rate of 4 1/min (STP) for 3 hours at a temperature of 400°C.
使用した石炭ガスの組成は日25群容量%、CH43位
容量%、C07容量%、N25容量%、C2比2容量%
、C2日61容量%、C022容量%であった。次に0
.3%の硝酸水溶液2そで60℃で洗浄処理*を3回行
った。The composition of the coal gas used was: Day 25 group volume%, CH43 volume%, C07 volume%, N25 volume%, C2 ratio 2 volume%.
, C2 day was 61% by volume, and C022% by volume. then 0
.. Washing treatment* was performed three times at 60°C using two 3% nitric acid aqueous solutions.
洗浄液中に溶解した元素の濃度を実施例1と同様にして
測定し、第11表の結果を得た。再生処理した触媒は、
触媒の強度、活性共に未使用の触媒とほとんど同じ状態
に回復していた。The concentration of elements dissolved in the cleaning solution was measured in the same manner as in Example 1, and the results shown in Table 11 were obtained. The regenerated catalyst is
Both the strength and activity of the catalyst had recovered to almost the same state as the unused catalyst.
第10表未使用触媒 1,500時間使用
再生触媒N0x浄化率(略) 94
77 95比表面積(
で/夕) 95
46 95触媒中の硫黄(重量物)
0.07 4.42
0.08触媒中のカリウム(重量)
− 1.73
0.05第 11 表 (元素物/雌)第1回
第2回 第3回
バナジウム 0.051 0.047 0.
058チ タ ン 0.008 0.004
0.001カリウム 4.93 2.0
2 1‐35 .実施例 5N○x浄化用触媒とし
て、高表面積を有する酸化チタンを用いV2Q:Ti0
2=15:85(重量比)なる組成の触媒をまったく実
施例1と同様にして、活性テスト、再生処理を行った。Table 10 Unused catalyst Used for 1,500 hours
Regenerated catalyst NOx purification rate (omitted) 94
77 95 specific surface area (
evening) 95
46 95 Sulfur in catalyst (heavy)
0.07 4.42
0.08 Potassium in catalyst (weight)
−1.73
0.05 Table 11 (Elements/Female) 1st
2nd 3rd Vanadium 0.051 0.047 0.
058 Titanium 0.008 0.004
0.001 potassium 4.93 2.0
2 1-35. Example 5 Using titanium oxide with a high surface area as a catalyst for N○x purification, V2Q: Ti0
A catalyst having a composition of 2=15:85 (weight ratio) was subjected to an activity test and a regeneration treatment in the same manner as in Example 1.
その経時変化および洗浄液中に溶解した元素の濃度を実
施例1と同様にして測定し、表12、表13の結果を得
た。The change over time and the concentration of elements dissolved in the cleaning solution were measured in the same manner as in Example 1, and the results shown in Tables 12 and 13 were obtained.
第12表
未使用触媒 1,500時間使用 再生触媒N
○x浄化率(孫) 94
78 94比表面積(で/夕)
110 51 11
0触媒中の硫黄(重量協) 0.13
5.25 0.21
触媒中のカリウム(重量※)
1.78 0.06第 13
表 (元素俊/淡)第1回第2回第3回第4回
バナジウム 0.038 0.059 0.070
0.072チ タ ン 0,007 0.007 0.
005 0,001力リウム 5.19 2.02
0.76 0.22比較例 4実施例1に示され
た活性の低下した触媒約lk9を還元炉に入れ、実施例
1とまったく同様に水素処理を行い、その後水洗処理を
行なわず、測定した結果第14表の結果を得た。Table 12 Unused catalyst Used for 1,500 hours Regenerated catalyst N
○x Purification rate (grandchild) 94
78 94 Specific surface area (de/even)
110 51 11
0 Sulfur in catalyst (weight association) 0.13
5.25 0.21
Potassium in catalyst (weight*)
1.78 0.06th 13th
Table (Element Shun/Light) 1st 2nd 3rd 4th Vanadium 0.038 0.059 0.070
0.072 Titanium 0,007 0.007 0.
005 0,001 Chirikurium 5.19 2.02
0.76 0.22 Comparative Example 4 Approximately 1k9 of the catalyst with reduced activity shown in Example 1 was placed in a reduction furnace and subjected to hydrogen treatment in exactly the same manner as in Example 1, and then measured without water washing treatment. Results The results shown in Table 14 were obtained.
第14 表
′未使用触媒 1,500時間使用 水素処理
触媒N○x浄化率(%) 93
73 78比表面積(み/夕)
35 18
31触媒中の硫黄(重量滋) 0.0
8 4.80 0.1
3触媒中のカリウム(重量孫)
1.75 1.77実施例 6Mo
o3:Ti02=10:90(重量比)の組成のN○x
浄化用触媒を空間速度700皿r‐1(STP)、ガス
入口温度280午○、使用時間延1500時間とするほ
かは、まったく実施例1の方法と同様にしてN0x浄化
反応に供し、第15銭こ示す結果を得た。Table 14: Unused catalyst Used for 1,500 hours Hydrogen treatment catalyst N○x purification rate (%) 93
73 78 Specific surface area (Mi/Even)
35 18
31 Sulfur in catalyst (weight) 0.0
8 4.80 0.1
3 Potassium in catalyst (weight scale)
1.75 1.77 Example 6Mo
N○x with a composition of o3:Ti02=10:90 (weight ratio)
The purification catalyst was subjected to the NOx purification reaction in the same manner as in Example 1, except that the space velocity was 700 plate r-1 (STP), the gas inlet temperature was 280 pm, and the usage time was 1500 hours. I got the results showing this.
活性の低下した触媒を水洗回数を3回とするほかは、実
施例1と同様の方法で再生処理を行ない、第16表の結
果を得た。第15表
未使用触媒 1,500時間使用 水素処理触
媒N○x浄化率(雄) 88
77 87比表面積くみ/夕)
45 35
42触媒中の硫黄(重量%)
0.03 4.50
0.10触媒中のカリウム(重量密)
1.60 0.07第 16
表(元素物/め)第1回 第2回 第3回
モリブデン 0.051 0.044 0.0
52チ タ ン 0.007 0.006
0.003カリウム 5.33 1.30
0.30なお、150餌時間使用後の触媒を水素処
理せずに水洗したところ、触媒の割れが著しく、再度使
用が不能となった。The regeneration treatment was carried out in the same manner as in Example 1, except that the catalyst whose activity had decreased was washed three times with water, and the results shown in Table 16 were obtained. Table 15 Unused catalyst Used for 1,500 hours Hydrogen treatment catalyst N○x purification rate (male) 88
77 87 specific surface area (kumi/evening)
45 35
42 Sulfur in catalyst (wt%)
0.03 4.50
0.10 Potassium in catalyst (weight density)
1.60 0.07 16th
Table (Elements/Metals) 1st 2nd 3rd Molybdenum 0.051 0.044 0.0
52 Titanium 0.007 0.006
0.003 potassium 5.33 1.30
0.30 Note that when the catalyst was washed with water after being used for 150 feeding hours without being subjected to hydrogen treatment, the catalyst cracked significantly and could no longer be used again.
Claims (1)
の窒素酸化物をアンモニアで還元し窒素と水に転化する
ための、チタンを含有しさらにバナジウムまたはモリブ
デンを含有してなる触媒を再生するにあたり、活性の低
下した触媒を水素含有ガス雰囲気中加熱処理した後、水
性媒体で洗浄することを特徴とする窒素酸化物浄化用触
媒の再生方法。1. When regenerating a catalyst containing titanium and further containing vanadium or molybdenum for reducing nitrogen oxides in exhaust gas containing sulfur compounds and alkali metal compounds with ammonia and converting them into nitrogen and water, A method for regenerating a nitrogen oxide purifying catalyst, which comprises heat-treating a degraded catalyst in a hydrogen-containing gas atmosphere and then washing it with an aqueous medium.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP52060446A JPS6012907B2 (en) | 1977-05-26 | 1977-05-26 | Method for regenerating nitrogen oxide purification catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP52060446A JPS6012907B2 (en) | 1977-05-26 | 1977-05-26 | Method for regenerating nitrogen oxide purification catalyst |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS53146293A JPS53146293A (en) | 1978-12-20 |
| JPS6012907B2 true JPS6012907B2 (en) | 1985-04-04 |
Family
ID=13142501
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP52060446A Expired JPS6012907B2 (en) | 1977-05-26 | 1977-05-26 | Method for regenerating nitrogen oxide purification catalyst |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6012907B2 (en) |
-
1977
- 1977-05-26 JP JP52060446A patent/JPS6012907B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS53146293A (en) | 1978-12-20 |
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