JPS6147576B2 - - Google Patents

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Publication number
JPS6147576B2
JPS6147576B2 JP55000514A JP51480A JPS6147576B2 JP S6147576 B2 JPS6147576 B2 JP S6147576B2 JP 55000514 A JP55000514 A JP 55000514A JP 51480 A JP51480 A JP 51480A JP S6147576 B2 JPS6147576 B2 JP S6147576B2
Authority
JP
Japan
Prior art keywords
catalyst
enamel
layer
base material
catalyst component
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
JP55000514A
Other languages
Japanese (ja)
Other versions
JPS5697547A (en
Inventor
Teishiro Watanabe
Tetsuyoshi Wada
Hideto Mitsutake
Kazuo Sekimoto
Kosuke Sawashige
Tokio Fujioka
Yoshihiro Kusanagi
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
Nippon Steel Nisshin Co Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
Nisshin Steel Co 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, Nisshin Steel Co Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP51480A priority Critical patent/JPS5697547A/en
Publication of JPS5697547A publication Critical patent/JPS5697547A/en
Publication of JPS6147576B2 publication Critical patent/JPS6147576B2/ja
Granted legal-status Critical Current

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  • Other Surface Treatments For Metallic Materials (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Description

【発明の詳现な説明】[Detailed description of the invention]

本発明は、各皮有害ガスを無公害化陀去する際
に䜿甚される觊媒に関し、特に䞀酞化炭玠や炭化
氎玠化合物は酞化觊媒ずしお、窒玠酞化物には還
元觊媒ずしお、アンモニアには酞玠あるいは窒玠
酞化物ずの反応における酞化觊媒ずしお、適甚す
る堎合に有効である觊媒の構成に関する。 䟋えば、排ガス䞭の窒玠酞化物以䞋、NOx
ず略すの陀去方法ずしおは、埌凊理䞍芁の觊媒
還元法が経枈的、技術的にも有利であり、特に排
ガス䞭の酞玠濃床の圱響を受けない遞択的還元法
が有利であるず蚀われおいる。 埓来、この皮還元法に適甚される觊媒ずしお
は、アルミナ、チタニア、ゞルコニア等の倚孔性
耐火物を単独あるいは組合わせお担䜓ずしおいる
が、いずれも造粒しお䜿甚するため高䟡であ぀
た。 たた、重油、石炭等を燃料ずするボむラ排ガス
等のダストを倚量に含有する排ガスを被凊理ガス
ずする堎合には、觊媒䞊ぞのダストの蓄積による
性胜䜎䞋ずいう問題があ぀た。この問題解決のた
めに、觊媒圢状を円筒状、ハニカム状等にしおダ
ストの通過を容易にする方法、觊媒を粒状ずしお
該粒状觊媒を移動するこずで付着ダストを飛散さ
せる方法等が怜蚎されおおり、その倖に觊媒を
板、構造䜓の局ずしお排ガスを該觊媒局に平行に
流す方法があり、該板状構造䜓の觊媒ずしおは安
䟡に補造できる無機物から成る非金属耐火ボヌド
を利甚したものが提案されおいる。しかし、この
皮の無機物から成るボヌドは、匷床䞊の問題から
倧型化に䌎ない板厚を増加させる必芁があり、該
ボヌドを板状構造䜓の觊媒ずしお利甚する堎合に
は、觊媒が倧型化し、蚭定堎所の制玄や脱硝装眮
のコストアツプ等の問題がある。そこで、このよ
うな板状觊媒の薄板化を蚈るために、金属を基材
ずする觊媒の開発が進められおいる。金属自身は
比重が倧きいが、板厚を0.6〜10mm皋床にしおも
十分䜿甚に耐え埗る匷床を有しおおり、䞊蚘の無
機物から成る非金属耐火ボヌドを基材ずする堎合
に比范しお装眮をコンパクト化できる利点があ
る。 以䞊のNOx還元甚觊媒に限らず、金属を基材
ずする各皮の觊媒に関しおは、皮々の補造方法が
知られおいるが、倧郚分は金属基材衚面䞊に觊媒
成分を担持させる方法である。しかし、觊媒成分
は倧郚分が金属酞化物であるため、熱膚脹係数が
基材である金属ず異なり、基材ずの付着性が䞍良
である堎合が倚い。このため、この基材ず觊媒成
分ずの付着性向䞊を目的ずしお皮々の補造方法が
提案されおいる。 それらの䞭で、金属基材ず觊媒成分ずの付着力
を向䞊させる手段ずしおホヌロヌを利甚するもの
がある。䟋えば、(1)金属基材衚面にガラス質を焌
付け、このガラス質をその軟化点以䞊の枩床に保
持し、これに觊媒成分粒子を固着させる方法特
開昭52−127913号、(2)ホヌロヌ甚フリツトず觊
媒成分を混合しおスリツプを䜜り、これを金属基
材䞊に圢成された゚ナメルホヌロヌ基質䞊に
焌付ける方法特公昭47−17832号、(3)金属基材
衚面に該金属甚ホヌロヌのスリツプを斜釉し、該
スリツプが也燥する前に耐火性の埮粉末を均䞀に
散垃し、也燥、焌成した埌、觊媒成分を付着担持
させる方法等である。 しかし、䞊蚘(1)の方法は、ガラス質の軟化点以
䞊の高枩500℃皋床で觊媒成分粒子を付着さ
せるため、䜜業性が悪く、觊媒成分を均䞀に散垃
させるこずが困難であり、しかもこの方法で補造
された觊媒は、第図にその断面を瀺すように、
觊媒成分粒子は金属基材䞊に圢成されたホヌ
ロヌ䞊に䞀局しか付着させるこずができず、付
着量が少ないずいう問題がある。たた䞊蚘(2)の方
法は、第図にその断面を瀺すように、反応に寄
䞎する衚面に出おいる觊媒成分粒子はホヌロヌ
甚フリツトず混合されおいるため、その量が少
なく、性胜が䜎いずいう問題点を有しおいる。曎
に䞊蚘(3)の方法は第図にその断面を瀺すよう
に、衚面に厚い觊媒成分の局′を圢成させるこ
ずが可胜であり、性胜的には問題ないが、ホヌロ
ヌ甚スリツプを塗垃した埌でか぀也燥する前に
耐火性の埮粉末を散垃しなければならず、時間
的制玄を受けるばかりでなく、該埮粉末を均䞀
に散垃するこずが困難であり、しかも工皋が耇雑
なためにコスト高になるずいう欠点がある。 以䞊のような事情に鑑み、本発明者等は簡単な
工皋で性胜の優れた觊媒を提䟛すべく鋭意研究の
結果、金属基材䞊にホヌロヌず觊媒成分ずの混合
物局を圢成し、該混合物局䞊に觊媒成分局を付着
担持させるこずにより、優れた觊媒が埗られるこ
ずを芋出し、本発明に到達したものである。 第図は、本発明觊媒を説明するための断面図
である。 第図から明らかなように、金属基材衚面に
圢成された混合物局αは、ホヌロヌ粒ず觊媒成
分粒ずから構成されおおり、倚孔質ずな぀おい
るず共に衚面が埮现な凹凞に富んでいるため、觊
媒成分局′ずの付着力が高い。たた、倚孔質で
ある混合物局αは、吞氎性であるため、觊媒成分
局′を圢成するための觊媒スラリヌず良くなじ
みはじかない、しかも該混合物局α䞭の觊媒
成分粒ず觊媒成分局′ずは同䞀の物性を有す
るため、匷固に結合し、党䜓ずしおは觊媒成分が
ホヌロヌ䞭に喰い蟌んだような状態ずなり、匷固
な結合力を瀺すこずができる。なお、混合物局α
䞭のホヌロヌ粒は金属基材ず匷固に結合する
こずは蚀うたでもない。このように本発明觊媒
は、本来結合力の匱い觊媒成分ず金属基材ずが、
その䞡者に察しお結合力の匷い混合物局によ぀お
匷固に結合されたものである。 本発明觊媒においお、混合物局のホヌロヌ成分
ず觊媒成分ずの混合割合は、ホヌロヌ成分が倚い
堎合、混合物局ず金属基材ずの結合力は増倧する
が、混合物局ず觊媒成分局ずの結合力が枛少する
ため、通垞は、ホヌロヌ成分觊媒成分
〜重量比皋床が奜たしいが、混合物局
を倚局にすればこの範囲にしなくおもよい。すな
わち、䞋局をホヌロヌ成分の倚い局ずし、䞊局を
觊媒成分の倚い局ずすればよい。最も理想的に
は、金属基材衚面にホヌロヌ局を有し、その䞊方
に次第にホヌロヌ成分の少なくな぀お行く混合物
局が有り、最衚面に觊媒成分局を有するものであ
る。 本発明觊媒の金属基材ずしおは、鉄、鋌、ステ
ンレス鋌、アルミニりム、アルミニりム合金、ア
ルミニりムメツキ鋌板等ホヌロヌがけが可胜で、
しかもその䜿甚環境に耐え埗るものが䜿甚でき、
その圢状ずしおは、板状、棒状、線状、管状ある
いは金網状等任意のものが䜿甚できる。 たたホヌロヌずしおは、軟鋌甚ホヌロヌ、アル
ミニりム甚ホヌロヌ、ステンレス鋌甚ホヌロヌ
等、金属基材の材質に察応させお任意のものを遞
定すればよい。なお、前蚘した(2)の埓来法におい
おは、ホヌロヌず觊媒成分の混合物を゚ナメル基
質䞊に焌付けお觊媒衚面局ずしおいるが、焌成枩
床の高いホヌロヌを䜿甚するず、この高い焌成枩
床によ぀お觊媒成分の性胜が䜎䞋するこずがある
ため、䜿甚できるホヌロヌに制玄がある。これに
察し、本発明觊媒における混合物局は䞭間局であ
るため、このような制玄を受けるものではない。
もちろん䞭間局ずいえども、ある皋床の觊媒性胜
を有しおいれば、觊媒成分局の厚さを薄くするこ
ずができるため、觊媒成分の焌成枩床に近い焌成
枩床を有するホヌロヌを䜿甚するこずが奜たしい
こずは蚀うたでもない。 本発明觊媒における混合物局に䜿甚される觊媒
成分は、觊媒成分局ず同䞀のものを䜿甚すればよ
いのであるが、混合物局における觊媒性胜が期埅
できない堎合には、掻性賊䞎成分を陀いたものを
䜿甚しおもよく、コスト䜎枛に぀ながる。これ
は、䞀般に、掻性賊䞎成分は埮量であり、これを
陀いおもその物性は殆んど倉化しないためであ
る。 ホヌロヌず觊媒成分ずの混合物局を前蚘の金属
基材に被芆させる方法は、通垞のホヌロヌがけの
堎合ず党く同様の方法で実斜するこずが可胜であ
り、塗垃、スプレヌがけ、浞挬等、任意の方法で
觊媒成分を含むスリツプを被芆し、也燥、焌成す
ればよい。 このようにしお金属基材に被芆された混合物局
の衚面郚に觊媒成分局を付着担持させれば、付着
力に優れた金属を基材ずする本発明觊媒を埗るこ
ずができる。 この觊媒成分は、アルミナ、シリカ、チタニ
ア、ゞルコニア、硫酞カルシりム等の倚孔性耐火
物に、癜金、パラゞりム、ロゞりム、ルテニりム
等の貎金属元玠の単独あるいは組合せたもの、た
たは銅、バナゞりム、クロム、マンガン、鉄、コ
バルト、ニツケル、ニオブ、モリブデン、タング
ステン等の卑金属元玠の酞化物あるいは硫酞塩化
合物を単独あるいは組合せたものを䞻たる掻性賊
䞎成分ずしお担持させたもので、自動車、その他
の各皮排ガス䞭のCO、炭化氎玠化合物、NOxを
陀去する酞化觊媒、還元觊媒あるいは䞉元觊媒
COの酞化、炭化氎玠化合物の酞化、NOxの還
元を同時に行なう觊媒ずしお提䟛し埗るもので
ある。たた、䞊蚘の掻性賊䞎成分ず共に、SO2の
酞化抑制や觊媒の安定化を蚈るために、スズ、亜
鉛、セリりム、ランタン、バリりム等の酞化物を
少量添加するこずもでき、NH3を還元剀ずする
NOx陀去觊媒、あるいは排ガス䞭のNOxや酞玠
によるNH3分解觊媒ずしお䜿甚できる。 䞊蚘觊媒成分の混合物局ぞの付着担持方法は、
特に限定されるものではなく、倚孔性耐火物の粉
末に掻性賊䞎成分等を混緎法、含浞法で添加した
スラリヌを塗垃、浞挬、スプレヌ法等で付着させ
た埌、也燥あるいは必芁に応じお焌成すればよ
い。なお、觊媒成分ずホヌロヌずの焌成枩床が等
しい堎合には、混合物局の焌成ず觊媒成分の焌成
を同時に行なうこずも可胜である。 以䞋、実斜䟋によ぀お本発明觊媒を具䜓的に説
明する。 実斜䟋  觊媒調補䟋 SiO245.2wt、Al2O38.5wt、B2O3
17.1wt、CaO3.0wt、K2O4.1wt、
Na2O15.0wt、NiO1.2wt、CoO2.9wt
、MnO2.5wt、ZnO0.5wtから成るフリ
ツト100重量郚に、粘土重量郚、珪石粉15重量
郚、硌砂0.5重量郚、亜硝酞゜ヌダ0.3重量郚、氎
50重量郚を加えお混合し、スリツプを調補し
た。 次にアナタヌれ型の酞化チタン粉末100重量郹
に五酞化バナゞりム重量郚ず酞化タングステン
重量郚および氎150重量郚を加えお混合し、觊
媒スラリヌを調補した。 50重量郚のスリツプず50重量郚の觊媒スラリ
ヌから成る混合スラリヌを調補し、これをmm
厚さの冷間圧延鋌板SPCCを脱脂、酞掗、ニ
ツケル凊理等の前凊理をした基材に塗垃し、也燥
させた埌、820℃で分間焌成しお凊理基材を
埗た。 次いで、該凊理基材䞊に觊媒スラリヌを塗
垃し、150℃で時間也燥しお觊媒を埗た。 該觊媒をカツタヌによる匕぀かき詊隓に䟛し
た結果、きずの䞡偎に剥離は認められず良奜な密
着性を瀺した。 実斜䟋  觊媒調補䟋 SiO220wt、TiO225wt、PbO28wt
、Na2O15wt、K2O5wt、B2O35wt
、CaO5wtから成るスリツプを調補し、
50重量郚のスリツプず50重量郚の觊媒スラリヌ
から成る混合スラリヌを調補した。この混合
スラリヌをmm厚さの溶融アルミニりムメツキ
鋌板目付量40/m2片面およびmm厚さのス
テンレス鋌板SUS 304を脱脂した基材に塗垃
し、也燥埌、550℃で分間焌成しお凊理基材
およびを埗た。 次いで、該凊理基材および䞊に觊媒スラリ
ヌを塗垃し、150℃で時間也燥しお觊媒お
よびを埗た。 觊媒およびはいずれも觊媒ず同様に良奜
な密着性を有しおいた。 実斜䟋  觊媒調補䟋 メタバナゞン酞アンモニりム2.5重量郚ずパ
ラタングステン酞アンモニりム10重量郚に、モノ
゚タノヌルアミン15重量郚ず氎30重量郚を添加
し、加熱溶解した溶液に、氎80重量郚ず酞化チタ
ン粉末100重量郚を加えお撹拌し、觊媒スラリヌ
を調補した。 次に、スリツプ觊媒スラリヌ
重量比から成る混合スラリヌ、およびスリ
ツプ觊媒スラリヌ重量比から
成る混合スラリヌを調補した。 脱脂凊理したステンレス鋌板SUS 304、mm
厚さ䞊に先ず混合スラリヌを塗垃、也燥した
埌、この䞊に混合スラリヌを塗垃、也燥し、曎
に觊媒スラリヌを塗垃、也燥埌、550℃で時
間焌成しお觊媒を埗た。 この觊媒も匕぀かき詊隓で剥離は認められず
良奜な密着性を有しおいた。 実斜䟋  觊媒性胜評䟡䟋 觊媒〜はアンモニアを還元剀ずする脱硝觊
媒ずしお䜿甚するものであり、その脱硝性胜を次
の芁領で評䟡した。 各觊媒に぀いおmm厚さ×10mm×100mmの詊隓
片18枚を22mmφ×100mmのステンレス鋌補反応噚
に充填し、NO200ppm、NH3200ppm、
SO2150ppm、O22vol、CO212vol、
H2O10vol、N2残りのガスをガス量220N
で流し、枩床360℃における脱硝率を枬定し
た。結果はいずれの觊媒も90以䞊の高い脱硝率
を有しおいた。 実斜䟋  觊媒調補䟋および觊媒性胜評䟡䟋 スリツプず衚に瀺す觊媒成分を䜿甚し、実
斜䟋ず同様にしお觊媒〜17を埗た。
The present invention relates to catalysts used in the non-pollution removal of various harmful gases, in particular carbon monoxide and hydrocarbon compounds as an oxidation catalyst, nitrogen oxides as a reduction catalyst, and ammonia as an oxygen or nitrogen oxidation catalyst. The present invention relates to the structure of a catalyst that is effective when applied as an oxidation catalyst in a reaction with a substance. For example, nitrogen oxides (hereinafter referred to as NOx) in exhaust gas
It is said that the catalytic reduction method, which does not require post-treatment, is economically and technically advantageous as a method for removing oxidants, and the selective reduction method, which is not affected by the oxygen concentration in the exhaust gas, is particularly advantageous. ing. Conventionally, as catalysts applied to this type of reduction method, porous refractories such as alumina, titania, zirconia, etc. are used alone or in combination as carriers, but all of them are expensive because they are used in granulated form. Furthermore, when the gas to be treated is exhaust gas containing a large amount of dust, such as exhaust gas from a boiler fueled by heavy oil, coal, etc., there is a problem of performance deterioration due to accumulation of dust on the catalyst. In order to solve this problem, methods are being considered, such as making the catalyst shape cylindrical or honeycomb-like to make it easier for dust to pass through, and making the catalyst granular and moving the granular catalyst to scatter the adhering dust. In addition, there is a method in which the catalyst is formed into a plate or structure layer and the exhaust gas flows parallel to the catalyst layer.As the catalyst for the plate structure, a nonmetallic fireproof board made of an inorganic material that can be manufactured at low cost is used. something is proposed. However, due to strength issues, it is necessary to increase the thickness of this type of board made of inorganic materials as the size of the board increases, and when the board is used as a catalyst for a plate-like structure, the catalyst becomes larger. However, there are problems such as restrictions on the installation location and increased costs for the denitrification equipment. Therefore, in order to make such plate-shaped catalysts thinner, progress is being made in developing catalysts based on metals. Although the metal itself has a high specific gravity, it has enough strength to withstand use even if the board thickness is reduced to about 0.6 to 10 mm, and compared to the case where the base material is a non-metallic fireproof board made of inorganic materials, it is easier to use. It has the advantage of being compact. Various manufacturing methods are known for not only the above-mentioned NOx reduction catalysts but also various metal-based catalysts, but most of them involve supporting catalyst components on the surface of a metal base material. . However, since most of the catalyst components are metal oxides, their coefficient of thermal expansion is different from that of the base metal, and their adhesion to the base material is often poor. For this reason, various manufacturing methods have been proposed for the purpose of improving the adhesion between the base material and the catalyst component. Among them, there are those that utilize enamel as a means to improve the adhesion between the metal base material and the catalyst component. For example, (1) a method of baking a glassy substance on the surface of a metal substrate, holding this glassy substance at a temperature above its softening point, and fixing catalyst component particles to it (Japanese Patent Application Laid-open No. 127913/1989); (2) ) A method of making a slip by mixing a frit for enamel and a catalyst component and baking this onto an enamel (enamel) substrate formed on a metal base material (Special Publication No. 17832/1983), (3) Metal base material The surface of the enamel slip is glazed, and before the slip is dried, refractory fine powder is uniformly sprinkled thereon, and after drying and firing, the catalyst component is adhered and supported. However, method (1) above has poor workability because the catalyst component particles are deposited at a high temperature (approximately 500°C) above the softening point of glass, and it is difficult to uniformly disperse the catalyst component. Moreover, the catalyst produced by this method, as shown in the cross section in Figure 1,
There is a problem that the catalyst component particles 3 can be deposited in only one layer on the enamel 2 formed on the metal base material 1, and the amount of the catalyst component particles 3 deposited is small. In addition, in the method (2) above, as the cross section is shown in FIG. 2, the catalyst component particles 3 on the surface contributing to the reaction are mixed with the enamel frit 4, so the amount thereof is small. It has the problem of low performance. Furthermore, as shown in the cross section of FIG. 3, the method (3) above allows the formation of a thick layer 3' of catalyst components on the surface, which poses no problem in terms of performance. The refractory fine powder 5 must be sprinkled after coating and before drying, which not only imposes time constraints, but also makes it difficult to uniformly distribute the fine powder 5, and the process is time-consuming. The drawback is that it is complicated and therefore costly. In view of the above circumstances, the present inventors conducted intensive research to provide a catalyst with excellent performance through a simple process, and as a result, formed a layer of a mixture of enamel and catalyst components on a metal base material, and created a layer of the mixture of enamel and catalyst components. The present invention was achieved by discovering that an excellent catalyst can be obtained by depositing and supporting a catalyst component layer on the layer. FIG. 4 is a sectional view for explaining the catalyst of the present invention. As is clear from FIG. 4, the mixture layer α formed on the surface of the metal base material 1 is composed of enamel grains 4 and catalyst component grains 3, and is porous and has fine irregularities on the surface. Since it is rich in carbon dioxide, it has a high adhesive force with the catalyst component layer 3'. In addition, since the porous mixture layer α has water absorption properties, it is compatible with (does not repel) the catalyst slurry for forming the catalyst component layer 3', and moreover, the catalyst component particles 3 in the mixture layer α and the catalyst Since it has the same physical properties as the component layer 3', it is strongly bonded to the component layer 3', and the overall state is as if the catalyst component is embedded in the enamel, thus exhibiting a strong bonding force. In addition, the mixture layer α
Needless to say, the enamel grains 4 inside are firmly bonded to the metal base material 1. In this way, in the catalyst of the present invention, the catalyst component and the metal base material, which originally have a weak bonding force,
Both of them are firmly bonded by a mixture layer with a strong bonding force. In the catalyst of the present invention, the mixing ratio of the enamel component and the catalyst component in the mixture layer is such that when the enamel component is large, the bonding force between the mixture layer and the metal base material increases, but the bonding force between the mixture layer and the catalyst component layer increases. Usually, the enamel component: catalyst component = 4:6.
The ratio is preferably about 6:4 (weight ratio), but it does not need to be within this range if the mixture layer is made into multiple layers. That is, the lower layer may be a layer containing many enamel components, and the upper layer may be a layer containing many catalyst components. Most ideally, it would have a enamel layer on the surface of the metal substrate, a mixture layer above which the enamel component gradually decreases, and a catalyst component layer on the outermost surface. Enamelable metal base materials for the catalyst of the present invention include iron, steel, stainless steel, aluminum, aluminum alloys, aluminum-plated steel plates, etc.
Moreover, you can use materials that can withstand the usage environment.
Any shape can be used, such as a plate, rod, line, tube, or wire mesh shape. Further, as the enamel, any enamel may be selected depending on the material of the metal base material, such as enamel for mild steel, enamel for aluminum, and enamel for stainless steel. In the conventional method (2) mentioned above, a mixture of enamel and catalyst components is baked onto the enamel substrate to form the catalyst surface layer. However, when enamel with a high firing temperature is used, the catalyst is There are restrictions on the types of enamel that can be used because the performance of the ingredients may deteriorate. On the other hand, since the mixture layer in the catalyst of the present invention is an intermediate layer, it is not subject to such restrictions.
Of course, even though it is an intermediate layer, if it has a certain level of catalytic performance, the thickness of the catalyst component layer can be made thinner, so it is preferable to use enamel that has a firing temperature close to the firing temperature of the catalyst component. Needless to say. The catalyst component used in the mixture layer of the catalyst of the present invention may be the same as the catalyst component layer, but if the catalyst performance in the mixture layer cannot be expected, the catalyst component used in the mixture layer may be the same as the catalyst component layer. may be used, leading to cost reduction. This is because the active-imparting component is generally in a trace amount, and its physical properties hardly change even if this component is removed. The method for coating the metal base material with the mixture layer of enamel and the catalyst component can be carried out in exactly the same manner as for ordinary enamel coating, and can be carried out by any method such as coating, spraying, dipping, etc. The slip containing the catalyst component may be coated, dried, and calcined using a method. If the catalyst component layer is adhered and supported on the surface of the mixture layer coated on the metal base material in this manner, it is possible to obtain the catalyst of the present invention having a metal base material with excellent adhesive strength. This catalyst component is composed of porous refractories such as alumina, silica, titania, zirconia, and calcium sulfate, and noble metal elements such as platinum, palladium, rhodium, and ruthenium, alone or in combination, or copper, vanadium, chromium, manganese, It supports oxides or sulfate compounds of base metal elements such as iron, cobalt, nickel, niobium, molybdenum, and tungsten, singly or in combination, as the main active ingredient, and is effective against CO in automobile and other various exhaust gases. It can be provided as an oxidation catalyst that removes hydrocarbon compounds and NOx, a reduction catalyst, or a three-way catalyst (a catalyst that simultaneously oxidizes CO, oxidizes hydrocarbon compounds, and reduces NOx). In addition, in addition to the above-mentioned activation-imparting components, a small amount of oxides such as tin, zinc, cerium, lanthanum, barium, etc. can be added in order to suppress SO 2 oxidation and stabilize the catalyst . to be
It can be used as a NOx removal catalyst or as a NH3 decomposition catalyst using NOx and oxygen in exhaust gas. The method for depositing and supporting the catalyst component on the mixture layer is as follows:
Although not particularly limited, a slurry in which active ingredients, etc. are added to porous refractory powder by a kneading method or an impregnation method is applied by coating, dipping, spraying, etc., and then dried or baked as necessary. do it. Note that if the firing temperatures of the catalyst component and the enamel are the same, it is also possible to fire the mixture layer and the catalyst component at the same time. The catalyst of the present invention will be specifically explained below with reference to Examples. Example 1 (Catalyst Preparation Example) SiO 2 : 45.2wt%, Al 2 O 3 : 8.5wt%, B 2 O 3 :
17.1wt%, CaO: 3.0wt%, K2O : 4.1wt%,
Na2O : 15.0wt%, NiO: 1.2wt%, CoO: 2.9wt
%, MnO: 2.5 wt%, ZnO: 0.5 wt%, 100 parts by weight of frit, 5 parts by weight of clay, 15 parts by weight of silica powder, 0.5 parts by weight of borax, 0.3 parts by weight of sodium nitrite, water.
Slip 1 was prepared by adding 50 parts by weight and mixing. Next, 8 parts by weight of vanadium pentoxide, 3 parts by weight of tungsten oxide, and 150 parts by weight of water were added to 100 parts by weight of anatase-type titanium oxide powder and mixed to prepare catalyst slurry 1. Mixed slurry 1 consisting of 50 parts by weight of slip 1 and 50 parts by weight of catalyst slurry was prepared, and this was mixed into a 1 mm
A thick cold-rolled steel plate (SPCC) was applied to a base material that had been pretreated by degreasing, pickling, nickel treatment, etc., dried, and then baked at 820°C for 2 minutes to obtain treated base material 1. . Next, catalyst slurry 1 was applied onto the treated substrate 1 and dried at 150° C. for 5 hours to obtain catalyst 1. When Catalyst 1 was subjected to a scratch test using a cutter, no peeling was observed on both sides of the scratch, indicating good adhesion. Example 2 (Catalyst preparation example) SiO 2 : 20wt%, TiO 2 : 25wt%, PbO: 28wt
%, Na2O : 15wt%, K2O : 5wt%, B2O3 : 5wt
%, CaO: prepared slip 2 consisting of 5 wt%,
A mixed slurry 2 consisting of 50 parts by weight of slip 2 and 50 parts by weight of catalyst slurry 1 was prepared. This mixed slurry 2 was applied to a degreased base material of a 1 mm thick molten aluminum plated steel plate (fabric weight 40 g/m 2 on one side) and a 1 mm thick stainless steel plate (SUS 304), and after drying, it was heated at 550℃ for 5 minutes. Firing and processing base material 2
and 3 were obtained. Next, catalyst slurry 1 was applied onto the treated substrates 2 and 3 and dried at 150° C. for 5 hours to obtain catalysts 2 and 3. Catalysts 2 and 3 both had good adhesion similar to catalyst 1. Example 3 (Catalyst Preparation Example) 15 parts by weight of monoethanolamine and 30 parts by weight of water were added to 2.5 parts by weight of ammonium metavanadate and 10 parts by weight of ammonium paratungstate, and 80 parts by weight of water was added to the heated solution. and 100 parts by weight of titanium oxide powder were added and stirred to prepare catalyst slurry 2. Next, slip 2: catalyst slurry 2 = 8:2
A mixed slurry 3 consisting of (weight ratio) and a mixed slurry 4 consisting of slip 2:catalyst slurry 2 = 2:8 (weight ratio) were prepared. Degreased stainless steel plate (SUS 304, 1mm
First, mix slurry 3 was applied on top of the slurry (thickness) and dried, then mixed slurry 4 was applied on top of this, dried, and then catalyst slurry 2 was applied, and after drying, it was fired at 550°C for 3 hours to obtain catalyst 4. Ta. This Catalyst 4 also had good adhesion with no peeling observed in the stick test. Example 4 (Catalyst performance evaluation example) Catalysts 1 to 4 are used as denitration catalysts using ammonia as a reducing agent, and their denitration performance was evaluated in the following manner. For each catalyst, 18 test pieces of 1 mm thickness x 10 mm x 100 mm were packed into a 22 mmφ x 100 mm stainless steel reactor, NO: 200 ppm, NH 3 : 200 ppm,
SO2 : 150ppm, O2 : 2vol%, CO2 : 12vol%,
H2O : 10vol%, N2 : Remaining gas volume 220N
/H, and the denitrification rate was measured at a temperature of 360°C. The results showed that all catalysts had high denitrification rates of over 90%. Example 5 (Catalyst Preparation Example and Catalyst Performance Evaluation Example) Catalysts 5 to 17 were obtained in the same manner as in Example 1 using Slip 1 and the catalyst components shown in Table 1.

【衚】 物に察する含有量を瀺す。
觊媒、15、16はCO、炭化氎玠化合物の酞化
觊媒ずしお、觊媒は自動車等の内燃機関から排
出されるNOx浄化甚觊媒ずしお、觊媒17はこれ
ら䞉成分を同時に䜎枛する䞉元觊媒ずしお、自動
車排ガスで性胜評䟡詊隓を行な぀た。結果は、い
ずれの觊媒も良奜な性胜を瀺した。もちろん、埓
来の排ガス浄化觊媒ずしお䜿甚される粒状觊媒、
ハニカム状觊媒に比しお觊媒量が少ないため、埓
来品ず同等の性胜を埗るこずは困難であるが、排
気管、その他排ガスが通過する管内を本発明觊媒
にするこずで20〜30皋床の浄化が行なわれるの
で、觊媒䜿甚量が埓来よりも枛少できる点でメリ
ツトがある。 觊媒〜14はアンモニアを還元剀ずする脱硝觊
媒ずしお䜿甚するものであり、実斜䟋ず同じ排
ガス源を甚いお脱硝性胜評䟡詊隓を行な぀た。こ
の時、各觊媒はmm厚さ×50mm×200mmのものを
mm間隔で10枚段にしお段配眮ずし、ガス量
10Nm3/H、ガス枩床350℃、NH3NOx1.0ずし
た。 結果は、衚に瀺す通りであ぀た。
[Table] Shows the content of each substance.
Catalysts 5, 15, and 16 are used as oxidation catalysts for CO and hydrocarbon compounds, catalyst 6 is used as a catalyst for purifying NOx emitted from internal combustion engines such as automobiles, and catalyst 17 is used as a three-way catalyst that simultaneously reduces these three components. Performance evaluation tests were conducted using automobile exhaust gas. The results showed that all catalysts exhibited good performance. Of course, the granular catalyst used as a conventional exhaust gas purification catalyst,
Since the amount of catalyst is small compared to honeycomb-shaped catalysts, it is difficult to achieve the same performance as conventional products, but by using the catalyst of the present invention in the exhaust pipe and other pipes through which exhaust gas passes, it is possible to improve the performance by 20 to 30%. This method has the advantage that the amount of catalyst used can be reduced compared to the conventional method. Catalysts 7 to 14 are used as denitration catalysts using ammonia as a reducing agent, and a denitration performance evaluation test was conducted using the same exhaust gas source as in Example 4. At this time, each catalyst was arranged in three stages with 10 sheets/stage of 1 mm thick x 50 mm x 200 mm at 7 mm intervals, and the gas amount
The conditions were 10Nm 3 /H, gas temperature 350°C, and NH 3 /NOx = 1.0. The results were as shown in Table 2.

【衚】 以䞊説明したように、本発明觊媒は、その甚途
も広く、皮々の分野で実甚性の倧きい優れた觊媒
である。
[Table] As explained above, the catalyst of the present invention has a wide range of uses and is an excellent catalyst with great practicality in various fields.

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

第〜図は埓来の觊媒の断面を瀺す暡匏図、
第図は本発明觊媒の断面を瀺す暡匏図である。 第〜図䞭、は金属基材、はホヌロヌ
局、は觊媒成分粒、′は觊媒成分局、はホ
ヌロヌ粒、は耐火性埮粒子である。
Figures 1 to 3 are schematic diagrams showing cross sections of conventional catalysts;
FIG. 4 is a schematic diagram showing a cross section of the catalyst of the present invention. In Figs. 1 to 4, 1 is a metal base material, 2 is an enamel layer, 3 is a catalyst component grain, 3' is a catalyst component layer, 4 is an enamel grain, and 5 is a refractory fine particle.

Claims (1)

【特蚱請求の範囲】[Claims]  金属基材、該基材䞊に圢成された觊媒成分局
および該金属基材ず觊媒成分局ずの䞭間に圢成さ
れたホヌロヌず媒成分ずの混合物局より成る金属
を基材ずする觊媒。
1. A metal-based catalyst comprising a metal base material, a catalyst component layer formed on the base material, and a mixture layer of enamel and a medium component formed between the metal base material and the catalyst component layer.
JP51480A 1980-01-09 1980-01-09 Catalyst containing metal as base material Granted JPS5697547A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51480A JPS5697547A (en) 1980-01-09 1980-01-09 Catalyst containing metal as base material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51480A JPS5697547A (en) 1980-01-09 1980-01-09 Catalyst containing metal as base material

Publications (2)

Publication Number Publication Date
JPS5697547A JPS5697547A (en) 1981-08-06
JPS6147576B2 true JPS6147576B2 (en) 1986-10-20

Family

ID=11475879

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51480A Granted JPS5697547A (en) 1980-01-09 1980-01-09 Catalyst containing metal as base material

Country Status (1)

Country Link
JP (1) JPS5697547A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0185956U (en) * 1987-11-30 1989-06-07

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5923031A (en) * 1982-07-09 1984-02-06 ミラヌド・チダヌルズ・トットマン Method and device for burning acidic catalyst

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0185956U (en) * 1987-11-30 1989-06-07

Also Published As

Publication number Publication date
JPS5697547A (en) 1981-08-06

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