JPS6333892B2 - - Google Patents
Info
- Publication number
- JPS6333892B2 JPS6333892B2 JP54149864A JP14986479A JPS6333892B2 JP S6333892 B2 JPS6333892 B2 JP S6333892B2 JP 54149864 A JP54149864 A JP 54149864A JP 14986479 A JP14986479 A JP 14986479A JP S6333892 B2 JPS6333892 B2 JP S6333892B2
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- carrier
- tio
- desulfurization
- experiment
- 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
Links
- 239000003054 catalyst Substances 0.000 claims description 26
- 238000000034 method Methods 0.000 claims description 14
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims description 12
- 239000007789 gas Substances 0.000 claims description 11
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 9
- 229910052815 sulfur oxide Inorganic materials 0.000 claims description 8
- 238000002485 combustion reaction Methods 0.000 claims description 6
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims description 6
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 claims description 4
- QGLKJKCYBOYXKC-UHFFFAOYSA-N nonaoxidotritungsten Chemical compound O=[W]1(=O)O[W](=O)(=O)O[W](=O)(=O)O1 QGLKJKCYBOYXKC-UHFFFAOYSA-N 0.000 claims description 2
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 claims description 2
- 229910001930 tungsten oxide Inorganic materials 0.000 claims description 2
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 claims 1
- 229910010413 TiO 2 Inorganic materials 0.000 description 14
- 238000006477 desulfuration reaction Methods 0.000 description 13
- 230000023556 desulfurization Effects 0.000 description 13
- 238000002474 experimental method Methods 0.000 description 13
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 13
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 10
- 230000000694 effects Effects 0.000 description 9
- 230000006866 deterioration Effects 0.000 description 8
- 239000002245 particle Substances 0.000 description 7
- 238000006243 chemical reaction Methods 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 3
- 239000000295 fuel oil Substances 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- BAVYZALUXZFZLV-UHFFFAOYSA-N Methylamine Chemical compound NC BAVYZALUXZFZLV-UHFFFAOYSA-N 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 239000000969 carrier Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 230000008929 regeneration Effects 0.000 description 2
- 238000011069 regeneration method Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 229910000349 titanium oxysulfate Inorganic materials 0.000 description 2
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 1
- 241000264877 Hippospongia communis Species 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- BPQQTUXANYXVAA-UHFFFAOYSA-N Orthosilicate Chemical compound [O-][Si]([O-])([O-])[O-] BPQQTUXANYXVAA-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 229910000323 aluminium silicate Inorganic materials 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 239000012876 carrier material Substances 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000010531 catalytic reduction reaction Methods 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 239000012050 conventional carrier Substances 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 238000007865 diluting Methods 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000011508 lime plaster Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000008188 pellet Substances 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- RMAQACBXLXPBSY-UHFFFAOYSA-N silicic acid Chemical compound O[Si](O)(O)O RMAQACBXLXPBSY-UHFFFAOYSA-N 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 230000019635 sulfation Effects 0.000 description 1
- 238000005670 sulfation reaction Methods 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
- CMPGARWFYBADJI-UHFFFAOYSA-L tungstic acid Chemical compound O[W](O)(=O)=O CMPGARWFYBADJI-UHFFFAOYSA-L 0.000 description 1
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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Description
本発明は含硫黄燃料の燃焼装置、例えばボイラ
などの排ガスをはじめとし、各種の燃焼排ガス中
に含有される硫黄酸化物(以下、SOxと略称す
る)や窒素酸化物(以下、Noxと略称する)を
同時に処理し浄化する方法ならびに、その触媒に
関するものである。
現在、燃焼排ガス中の成分で大気汚染の要因と
して、SOxとNOxがあげれ、その浄化対策が、
各方面で開発されている。
この対策としては脱硫は石灰石膏法、脱硝は接
触還元法が主流をなしているが、これらは各々単
独のプロセスである。また、この単独の浄化法が
採用された理由は、脱硫の必要な排ガスは脱硝触
媒に悪影響が大きく、脱硝プロセスは成立し難い
し、又反対に脱硝プロセスの成立する燃焼排ガス
はいわゆるクリーンガスであつて、脱硫が必要で
なかつた。ところで、石油類の逼迫した今日では
エネルギーの多様化から石炭燃料や重質油の利用
が検討されている。これらの石炭や重質油を燃焼
させた場合には排ガス中のNOxやSOxの濃度が
高いため両者の浄化が必要になつている。また従
来の、両者に対する別種の方法と装置による脱硝
や脱硫法の現況は、複雑な周辺機器が必要になつ
て、経済性を悪化させるため実用化に至つていな
い。
このような情勢において単一の方法と装置によ
る脱硫と脱硝(以下脱硫硝と略称する)が同時に
可能となれば、その社会への貢献は素清らしいも
のがある。
乾式の脱硫硝の試みは、すでに発表されている
が以下述べるような問題点があつて、実用化され
ていない。
まず、脱硫については、酸化鉄(Fe2O3)触媒
を使用する方法は公知であり原理としては(1)、(2)
式で示される。
Fe2O3+3SO3Fe2(SO4)3 ……(1)
Fe2O3+3SO2+3/2O2Fe2(SO4)3 ……(2)
この触媒の担体としてアルミナ(Al2O3)の使
用(特公昭52−43615)が報告されているがSOx
との反応によつてAl2(SO4)への転化があり、遂
次活性の低下を生じることが難点である。
この改良法として、アルミナの上にチタニアを
コートした触媒(特開昭49−97794)があるが上
述の如くアルミナの硫酸化の問題は免れない。
本発明者らは、耐SOx性を有し、かつ触媒性能
の高い担体材料について探策しアナターゼ型のチ
タニア(TiO2)が優れることを見出した。これ
は触媒討論会(昭和48年名工大村上教授)にも発
表されているように活性は小さい担体であり、こ
のTiO2の担体を実用化するためには、以下に述
べる二つの問題があつた。
第一の問題点はTiO2の熱安定性である。さき
に述べたとおり、活性のあるTiO2担体の結晶形
はアナターゼ型であるが、触媒上のFe2O3がFe2
(SO4)3となるとSOxの浄化作用はなくなるため
再生処理が必要である。この再生法としては加熱
による(1)、(2)式の左向きの反応や、CoやH2によ
る還元反応が知られている。この反応により600
℃以上の高温下に触媒が暴露され活性の高い
TiO2はこのような高温のもとではルチル型に転
化し活性を失うため再生しながら、反復利用でき
ないことが問題である。更にもう一つの問題点は
TiO2は従来の担体Al2O3と異つて成形性が極めて
悪いためペレツトやハニカムなどの触媒形状に保
持することが難しいことである。
このような事実から、TiO2をコートした先述
の特許出願がなされた理由がよく理解できる。
この点、本発明の触媒は熱安定化させたTiO2
担体を特徴とする、同時脱硫硝に関するものであ
る。
以下、実験例により、本発明の特徴ならびに優
位性について述べる。
実験例
本発明の脱硫硝の試験条件を表1に試験ガス性
状を表2に示す。
The present invention deals with sulfur oxides (hereinafter abbreviated as SOx) and nitrogen oxides (hereinafter abbreviated as Nox) contained in various types of combustion exhaust gas, including exhaust gas from sulfur-containing fuel combustion equipment such as boilers. ) and its catalyst. Currently, SOx and NOx are components of combustion exhaust gas that cause air pollution, and measures to purify them are
It is being developed in various areas. The main countermeasures against this problem are the lime plaster method for desulfurization and the catalytic reduction method for denitrification, but these are each independent processes. In addition, the reason why this single purification method was adopted is that exhaust gas that requires desulfurization has a large negative effect on the denitrification catalyst, making it difficult to carry out the denitration process, and conversely, the combustion exhaust gas that can undergo the denitrification process is so-called clean gas. In that case, desulfurization was not necessary. By the way, in these days of tight petroleum supplies, the use of coal fuel and heavy oil is being considered due to the diversification of energy sources. When these coals and heavy oils are burned, the concentrations of NOx and SOx in the exhaust gas are high, so it is necessary to purify both. Further, the current state of the conventional denitrification and desulfurization methods using different methods and equipment for both requires complicated peripheral equipment and deteriorates economic efficiency, so that they have not been put into practical use. Under these circumstances, if desulfurization and denitrification (hereinafter abbreviated as desulfurization/nitrification) could be performed simultaneously using a single method and device, the contribution to society would be of great value. Dry desulfurization attempts have already been announced, but they have not been put into practical use due to the following problems. First, regarding desulfurization, a method using an iron oxide (Fe 2 O 3 ) catalyst is publicly known, and the principle is (1) and (2).
It is shown by the formula. Fe 2 O 3 +3SO 3 Fe 2 (SO 4 ) 3 ...(1) Fe 2 O 3 +3SO 2 +3/2O 2 Fe 2 (SO 4 ) 3 ...(2) Alumina (Al 2 O) is used as a support for this catalyst. 3 ) has been reported (Special Publication No. 52-43615), but SOx
The problem is that the reaction with Al 2 (SO 4 ) causes conversion to Al 2 (SO 4 ), resulting in a subsequent decrease in activity. As an improved method, there is a catalyst (Japanese Patent Laid-Open No. 49-97794) in which titania is coated on alumina, but as mentioned above, the problem of sulfation of alumina cannot be avoided. The present inventors searched for a carrier material that has SOx resistance and high catalytic performance and found that anatase type titania (TiO 2 ) is excellent. As announced at the Catalyst Discussion Group (Professor Murakami, Nagoya Institute of Technology in 1971), this is a carrier with low activity, and in order to put this TiO 2 carrier to practical use, the following two problems must be met. Ta. The first problem is the thermal stability of TiO2 . As mentioned earlier, the crystal form of the active TiO 2 support is anatase type, but Fe 2 O 3 on the catalyst is
When it becomes (SO 4 ) 3 , the purification effect of SOx disappears, so regeneration treatment is necessary. Known methods for this regeneration include the leftward reactions of equations (1) and (2) by heating, and the reduction reaction by Co and H 2 . This reaction results in 600
The catalyst is exposed to high temperatures above ℃ and has high activity.
The problem is that TiO 2 converts to rutile form and loses its activity at such high temperatures, so it cannot be recycled and used repeatedly. Yet another problem is
Unlike the conventional carrier Al 2 O 3 , TiO 2 has extremely poor formability, making it difficult to hold it in catalyst shapes such as pellets or honeycombs. From these facts, it is easy to understand why the above-mentioned patent application for coating TiO 2 was filed. In this respect, the catalyst of the present invention is made of thermally stabilized TiO 2
This invention relates to simultaneous desulfurization, characterized by a carrier. The features and advantages of the present invention will be described below using experimental examples. Experimental Example The test conditions for the desulfurized nitrogen of the present invention are shown in Table 1, and the test gas properties are shown in Table 2.
【表】【table】
【表】【table】
【表】
(1) 実験1
硫酸チタニルをアンモニア水で中和し、沈澱
を生じせしめ、過分離して、これを400℃で
焼成した。このTiO2粉末に水酸化アルミナの
水溶液をAl2O3として5%相当を添加し、粒径
2〜4mmの粒状に成形して、600℃で3時間焼
成し、担体を得た。
この担体に硝酸第1鉄をFe2O3として10%と
なるように水溶液で含浸させ、500℃で3時間
焼成して触媒とし、表1、2、の条件で評価し
て、表3に示す結果を得た。
(2) 実験2
硫酸チタニルをアンモニア水で中和し、沈澱
を生じせしめ、過分離してこれを400℃で焼
成した。ここで、生成したTiO2にタングステ
ン酸をメチルアミンに溶解させた液をWO3と
して7重量%相当加え、700℃で焼成し、熱安
定化させたTiO2−WO3の粉末を得た。
次にこの粉末に水酸化アルミナをAl2O3で5
重量%相当添加し、粒径2〜4mmの粒状に成形
し、600℃で3時間焼成して、担体を得た。こ
の得られた担体を実験1と同様の処理をして
Fe2O3の触媒とし、表1、2の条件で評価して
表3の結果を得た。
(3) 実験3
市販の活性アルミナ(住友化学KHA)を粒
径2〜4mmに篩分けし、これを担体として実験
1と同様にFe2O3を10%担持し、触媒とした。
この触媒について表1、2の条件で性能を評価
し、表3に示す結果を得た。[Table] (1) Experiment 1 Titanyl sulfate was neutralized with aqueous ammonia to form a precipitate, which was overseparated and calcined at 400°C. To this TiO 2 powder, an aqueous solution of alumina hydroxide equivalent to 5% Al 2 O 3 was added, formed into particles with a particle size of 2 to 4 mm, and fired at 600° C. for 3 hours to obtain a carrier. This carrier was impregnated with an aqueous solution of ferrous nitrate to a concentration of 10% as Fe 2 O 3 and fired at 500°C for 3 hours to form a catalyst. The following results were obtained. (2) Experiment 2 Titanyl sulfate was neutralized with aqueous ammonia to form a precipitate, which was overseparated and calcined at 400°C. Here, 7% by weight of a solution of tungstic acid dissolved in methylamine as WO 3 was added to the produced TiO 2 and fired at 700° C. to obtain a thermally stabilized TiO 2 -WO 3 powder. Next, add alumina hydroxide to this powder with Al 2 O 3 for 5 minutes.
It was added in an amount equivalent to % by weight, formed into particles with a particle size of 2 to 4 mm, and fired at 600°C for 3 hours to obtain a carrier. The obtained carrier was treated in the same manner as in Experiment 1.
Using Fe 2 O 3 as a catalyst, evaluation was performed under the conditions shown in Tables 1 and 2, and the results shown in Table 3 were obtained. (3) Experiment 3 Commercially available activated alumina (Sumitomo Chemical KHA) was sieved to a particle size of 2 to 4 mm, and this was used as a carrier to support 10% Fe 2 O 3 in the same manner as in Experiment 1 to serve as a catalyst.
The performance of this catalyst was evaluated under the conditions shown in Tables 1 and 2, and the results shown in Table 3 were obtained.
【表】
この結果から判るように、Al2O3やTiO2の単
独より、TiO2−WO3系の担体(実験No.2)を
用いた本発明実施列の場合が、脱硫硝の作用が
秀れていることがわかる。
(4) 実験4
実験1〜3で使用した触媒において、Fe2O3
はFe2(SO4)3に転化する。これらの触媒につい
て再生の可否を確認するため、各々を700℃の
温度で3時間加熱し、熱分解により再生して、
再度表1、2の試験条件で触媒の性能評価を行
いその結果を表4に示した。
この結果から判るように本発明の実施例の場
合のTiO2−WO3系担体を用いた触媒は劣化が
殆どなく、他のものは、脱硫、脱硫性能におい
て著しい劣化が認められた。[Table] As can be seen from this result, the effect of desulfurization was higher in the case of the present invention using a TiO 2 -WO 3 carrier (Experiment No. 2) than with Al 2 O 3 or TiO 2 alone. It can be seen that he is excellent. (4) Experiment 4 In the catalyst used in Experiments 1 to 3, Fe 2 O 3
is converted to Fe 2 (SO 4 ) 3 . In order to confirm whether these catalysts can be regenerated, each was heated at a temperature of 700°C for 3 hours and regenerated by thermal decomposition.
The performance of the catalyst was evaluated again under the test conditions shown in Tables 1 and 2, and the results are shown in Table 4. As can be seen from the results, the catalyst using the TiO 2 -WO 3 carrier in the example of the present invention showed almost no deterioration, while the other catalysts showed significant deterioration in desulfurization and desulfurization performance.
【表】
(5) 実験5
実験2においてWO3の添加量を0、5、1、
0、3.0、5.0、9.0各重量%添加した担体を試作
し、実験1と同様にFe2O5を10重量%担持して
触媒を調製した。この各々について700℃の高
温で3時間、加速劣化処理し、表1、2に示す
試験条件で脱硝性能を評価した。ここで得た結
果を加速劣化処理前の脱硝性能に対する、加速
劣化処理後の脱硝性能への劣化度(〔処理前の
脱硝率−処理後の脱硝率〕÷処理前の脱硝率)
で表わし、表5に示した。[Table] (5) Experiment 5 In Experiment 2, the amount of WO 3 added was 0, 5, 1,
0, 3.0, 5.0, and 9.0% by weight of Fe 2 O 5 were added as trial carriers, and in the same manner as in Experiment 1, 10% by weight of Fe 2 O 5 was supported to prepare a catalyst. Each of these was subjected to accelerated deterioration treatment at a high temperature of 700°C for 3 hours, and the denitrification performance was evaluated under the test conditions shown in Tables 1 and 2. The results obtained here are the degree of deterioration of the denitrification performance after accelerated deterioration treatment relative to the denitrification performance before accelerated deterioration treatment ([denitrification rate before treatment - denitrification rate after treatment] ÷ denitrification rate before treatment)
It is expressed in Table 5.
【表】
この結果から判るようにWO3の添加量は3
%以上あれば劣化度は小さく、実用に支障なき
ことが理解できる。またWO3は高価なため最
大使用量は7wt%にとどめることが好ましい。
(6) 実験6
実験2において、水酸化アルミナの水溶液の
添加量を、Al2O3として、1、3、5、7、9
各重量%添加した担体を試作し、粒径3mmの担
体を篩分けして、各々につき圧縮強度を測定し
た。
この結果を表6に示す。なお、この強度の値
は100個のサンプルの平均値である。[Table] As you can see from this result, the amount of WO 3 added is 3
% or more, it can be understood that the degree of deterioration is small and there is no problem in practical use. Furthermore, since WO 3 is expensive, it is preferable to limit the maximum usage amount to 7wt%. (6) Experiment 6 In Experiment 2, the amount of aqueous solution of alumina hydroxide added was 1, 3, 5, 7, 9 as Al 2 O 3.
Prototype carriers containing each weight percent were prepared, and the carrier particles having a particle size of 3 mm were sieved, and the compressive strength of each carrier was measured. The results are shown in Table 6. Note that this intensity value is the average value of 100 samples.
【表】
この値から判るように、Al2O3の添加量は3
%以上あれば実用に支障ない強度である。
さらにAl2O3を増量すると、強度は幾分高く
はなるが、触媒性能の低下と、使用中にAl2
(SO4)3の生成が大きくなり触媒の劣化につな
がるので好ましくない。
従つて、本発明による触媒担体の好ましい組
成は、チタニア、酸化タングステン、アルミナ
質の重量%比で85〜94、7〜3、8〜3であ
る。
Al2O3の代替えとして水酸化シリカ(日産化
学製のシリカゾル)を使用したがTiO2の粘結
強度は得られなかつた。
又、アルミノシリケートについて、テストし
た結果、これは粘結剤として有効であるがシリ
ケート分は触媒組成を稀薄にするだけの作用し
か示さず、Al2O3だけが粘結作用の効果を生ぜ
しめているものと考える。
以上の試験において示した如く、本発明は極め
て優れた同時脱硫硝の方法と触媒を提供するもの
である。[Table] As you can see from this value, the amount of Al 2 O 3 added is 3
% or more, the strength is sufficient for practical use. Further increasing the amount of Al 2 O 3 will increase the strength somewhat, but will reduce the catalyst performance and increase the amount of Al 2 O 3 during use.
This is not preferable because it increases the production of (SO 4 ) 3 and leads to catalyst deterioration. Therefore, the preferred composition of the catalyst carrier according to the present invention is 85 to 94, 7 to 3, and 8 to 3 in weight percent ratio of titania, tungsten oxide, and alumina. Silica hydroxide (silica sol manufactured by Nissan Chemical) was used as a substitute for Al 2 O 3 , but the caking strength of TiO 2 could not be obtained. In addition, tests on aluminosilicate showed that it was effective as a binder, but the silicate component only had the effect of diluting the catalyst composition, and that only Al 2 O 3 had a caking effect. I think that there is. As shown in the above tests, the present invention provides an extremely excellent method and catalyst for simultaneous desulfurization.
Claims (1)
チタンを、アルミナ質にて粘結して担体とし、こ
の担体に酸化鉄を担持させた触媒により、燃焼排
ガス中の硫黄酸化物と窒素酸化物とを、同時に除
去することを特徴とする燃焼排ガスの浄化方法。1 Titanium oxide thermally stabilized with tungsten oxide is caked with alumina to form a carrier, and a catalyst with iron oxide supported on this carrier removes sulfur oxides and nitrogen oxides from combustion exhaust gas. A method for purifying combustion exhaust gas characterized by simultaneously removing the gas.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14986479A JPS5673527A (en) | 1979-11-19 | 1979-11-19 | Purification method for combustion exhaust gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14986479A JPS5673527A (en) | 1979-11-19 | 1979-11-19 | Purification method for combustion exhaust gas |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS5673527A JPS5673527A (en) | 1981-06-18 |
JPS6333892B2 true JPS6333892B2 (en) | 1988-07-07 |
Family
ID=15484315
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP14986479A Granted JPS5673527A (en) | 1979-11-19 | 1979-11-19 | Purification method for combustion exhaust gas |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5673527A (en) |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS50152974A (en) * | 1974-05-30 | 1975-12-09 | ||
JPS5171265A (en) * | 1974-12-17 | 1976-06-19 | Hitachi Shipbuilding Eng Co | |
JPS5395892A (en) * | 1977-02-03 | 1978-08-22 | Mizusawa Industrial Chem | Titanium oxide catalyst carrier mold product and manufacture thereof |
JPS5411093A (en) * | 1977-06-27 | 1979-01-26 | Sakai Chem Ind Co Ltd | Production of catalyst and denitration method |
JPS5483696A (en) * | 1977-12-16 | 1979-07-03 | Sakai Chem Ind Co Ltd | Production of catalyst and denitration method |
-
1979
- 1979-11-19 JP JP14986479A patent/JPS5673527A/en active Granted
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS50152974A (en) * | 1974-05-30 | 1975-12-09 | ||
JPS5171265A (en) * | 1974-12-17 | 1976-06-19 | Hitachi Shipbuilding Eng Co | |
JPS5395892A (en) * | 1977-02-03 | 1978-08-22 | Mizusawa Industrial Chem | Titanium oxide catalyst carrier mold product and manufacture thereof |
JPS5411093A (en) * | 1977-06-27 | 1979-01-26 | Sakai Chem Ind Co Ltd | Production of catalyst and denitration method |
JPS5483696A (en) * | 1977-12-16 | 1979-07-03 | Sakai Chem Ind Co Ltd | Production of catalyst and denitration method |
Also Published As
Publication number | Publication date |
---|---|
JPS5673527A (en) | 1981-06-18 |
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