JPH11285616A - Heavy oil lightening/flue gas treating device and method therefor - Google Patents
Heavy oil lightening/flue gas treating device and method thereforInfo
- Publication number
- JPH11285616A JPH11285616A JP10090485A JP9048598A JPH11285616A JP H11285616 A JPH11285616 A JP H11285616A JP 10090485 A JP10090485 A JP 10090485A JP 9048598 A JP9048598 A JP 9048598A JP H11285616 A JPH11285616 A JP H11285616A
- Authority
- JP
- Japan
- Prior art keywords
- plasma
- honeycomb
- gas
- lightening
- catalyst
- 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.)
- Pending
Links
- 238000000034 method Methods 0.000 title claims abstract description 54
- 239000000295 fuel oil Substances 0.000 title claims abstract description 39
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 18
- 239000003546 flue gas Substances 0.000 title claims abstract description 18
- 239000007789 gas Substances 0.000 claims abstract description 59
- 238000006243 chemical reaction Methods 0.000 claims abstract description 56
- 239000003054 catalyst Substances 0.000 claims abstract description 48
- 229910001410 inorganic ion Inorganic materials 0.000 claims abstract description 27
- 238000011282 treatment Methods 0.000 claims abstract description 26
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 claims description 30
- 238000001179 sorption measurement Methods 0.000 claims description 19
- 238000007254 oxidation reaction Methods 0.000 claims description 17
- 238000005984 hydrogenation reaction Methods 0.000 claims description 12
- 230000009467 reduction Effects 0.000 claims description 12
- 239000011248 coating agent Substances 0.000 claims description 11
- 238000000576 coating method Methods 0.000 claims description 11
- 229910052736 halogen Inorganic materials 0.000 claims description 8
- 150000002367 halogens Chemical class 0.000 claims description 7
- 238000006317 isomerization reaction Methods 0.000 claims description 7
- 239000000446 fuel Substances 0.000 claims description 5
- 238000004519 manufacturing process Methods 0.000 claims description 4
- 239000000779 smoke Substances 0.000 claims description 4
- 238000005336 cracking Methods 0.000 claims description 2
- 238000006356 dehydrogenation reaction Methods 0.000 claims description 2
- 239000003921 oil Substances 0.000 claims description 2
- 230000002265 prevention Effects 0.000 claims description 2
- 229910021536 Zeolite Inorganic materials 0.000 abstract description 59
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 abstract description 59
- 239000010457 zeolite Substances 0.000 abstract description 59
- 238000005342 ion exchange Methods 0.000 abstract description 8
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 description 27
- 238000000354 decomposition reaction Methods 0.000 description 21
- 229930195733 hydrocarbon Natural products 0.000 description 19
- 150000002430 hydrocarbons Chemical class 0.000 description 19
- 229910052739 hydrogen Inorganic materials 0.000 description 18
- 238000006722 reduction reaction Methods 0.000 description 18
- 239000012855 volatile organic compound Substances 0.000 description 17
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 13
- 230000005684 electric field Effects 0.000 description 13
- 239000001257 hydrogen Substances 0.000 description 13
- 238000010586 diagram Methods 0.000 description 12
- 239000008188 pellet Substances 0.000 description 11
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 10
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 9
- 238000002474 experimental method Methods 0.000 description 9
- -1 CH 4 or C 2 H 6 Chemical class 0.000 description 8
- 230000003647 oxidation Effects 0.000 description 8
- 230000000694 effects Effects 0.000 description 7
- 239000002245 particle Substances 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 239000006227 byproduct Substances 0.000 description 6
- 239000003638 chemical reducing agent Substances 0.000 description 6
- 238000005516 engineering process Methods 0.000 description 6
- 230000008569 process Effects 0.000 description 6
- 239000004215 Carbon black (E152) Substances 0.000 description 5
- 229910021529 ammonia Inorganic materials 0.000 description 5
- 229910052799 carbon Inorganic materials 0.000 description 5
- 238000002485 combustion reaction Methods 0.000 description 5
- 229910052751 metal Inorganic materials 0.000 description 5
- 239000002184 metal Substances 0.000 description 5
- 230000001737 promoting effect Effects 0.000 description 5
- 230000001603 reducing effect Effects 0.000 description 5
- XKRFYHLGVUSROY-UHFFFAOYSA-N Argon Chemical compound [Ar] XKRFYHLGVUSROY-UHFFFAOYSA-N 0.000 description 4
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- ATUOYWHBWRKTHZ-UHFFFAOYSA-N Propane Chemical compound CCC ATUOYWHBWRKTHZ-UHFFFAOYSA-N 0.000 description 4
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 4
- 239000004202 carbamide Substances 0.000 description 4
- 238000005253 cladding Methods 0.000 description 4
- 239000003502 gasoline Substances 0.000 description 4
- 150000002500 ions Chemical class 0.000 description 4
- 150000003254 radicals Chemical class 0.000 description 4
- 238000000629 steam reforming Methods 0.000 description 4
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 3
- 150000001298 alcohols Chemical class 0.000 description 3
- 125000004432 carbon atom Chemical group C* 0.000 description 3
- 229910002091 carbon monoxide Inorganic materials 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- 238000005695 dehalogenation reaction Methods 0.000 description 3
- 238000001784 detoxification Methods 0.000 description 3
- 239000002803 fossil fuel Substances 0.000 description 3
- 150000002576 ketones Chemical class 0.000 description 3
- 230000007246 mechanism Effects 0.000 description 3
- 229910052680 mordenite Inorganic materials 0.000 description 3
- 238000009832 plasma treatment Methods 0.000 description 3
- 239000011148 porous material Substances 0.000 description 3
- 229910052723 transition metal Inorganic materials 0.000 description 3
- 150000003624 transition metals Chemical class 0.000 description 3
- CSCPPACGZOOCGX-UHFFFAOYSA-N Acetone Chemical compound CC(C)=O CSCPPACGZOOCGX-UHFFFAOYSA-N 0.000 description 2
- VGGSQFUCUMXWEO-UHFFFAOYSA-N Ethene Chemical compound C=C VGGSQFUCUMXWEO-UHFFFAOYSA-N 0.000 description 2
- 239000005977 Ethylene Substances 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- 229910052786 argon Inorganic materials 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 238000004517 catalytic hydrocracking Methods 0.000 description 2
- 238000010531 catalytic reduction reaction Methods 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 150000002013 dioxins Chemical class 0.000 description 2
- 230000005284 excitation Effects 0.000 description 2
- 230000002349 favourable effect Effects 0.000 description 2
- 230000006698 induction Effects 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000002808 molecular sieve Substances 0.000 description 2
- 229910052759 nickel Inorganic materials 0.000 description 2
- 239000003208 petroleum Substances 0.000 description 2
- 229910052697 platinum Inorganic materials 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 239000001294 propane Substances 0.000 description 2
- 230000007420 reactivation Effects 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 238000007363 ring formation reaction Methods 0.000 description 2
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- OTMSDBZUPAUEDD-UHFFFAOYSA-N Ethane Chemical compound CC OTMSDBZUPAUEDD-UHFFFAOYSA-N 0.000 description 1
- BPQQTUXANYXVAA-UHFFFAOYSA-N Orthosilicate Chemical compound [O-][Si]([O-])([O-])[O-] BPQQTUXANYXVAA-UHFFFAOYSA-N 0.000 description 1
- CYTYCFOTNPOANT-UHFFFAOYSA-N Perchloroethylene Chemical group ClC(Cl)=C(Cl)Cl CYTYCFOTNPOANT-UHFFFAOYSA-N 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 229910002367 SrTiO Inorganic materials 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- XSTXAVWGXDQKEL-UHFFFAOYSA-N Trichloroethylene Chemical group ClC=C(Cl)Cl XSTXAVWGXDQKEL-UHFFFAOYSA-N 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 239000002156 adsorbate Substances 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 150000001338 aliphatic hydrocarbons Chemical class 0.000 description 1
- HSFWRNGVRCDJHI-UHFFFAOYSA-N alpha-acetylene Natural products C#C HSFWRNGVRCDJHI-UHFFFAOYSA-N 0.000 description 1
- JRPBQTZRNDNNOP-UHFFFAOYSA-N barium titanate Chemical compound [Ba+2].[Ba+2].[O-][Ti]([O-])([O-])[O-] JRPBQTZRNDNNOP-UHFFFAOYSA-N 0.000 description 1
- 229910002113 barium titanate Inorganic materials 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 239000012159 carrier gas Substances 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 239000003989 dielectric material Substances 0.000 description 1
- 238000010494 dissociation reaction Methods 0.000 description 1
- 230000005593 dissociations Effects 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 125000002534 ethynyl group Chemical group [H]C#C* 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000002290 gas chromatography-mass spectrometry Methods 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000005431 greenhouse gas Substances 0.000 description 1
- 239000010763 heavy fuel oil Substances 0.000 description 1
- 231100000171 higher toxicity Toxicity 0.000 description 1
- 238000007327 hydrogenolysis reaction Methods 0.000 description 1
- 238000003780 insertion Methods 0.000 description 1
- 230000037431 insertion Effects 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 229910052741 iridium Inorganic materials 0.000 description 1
- 239000003949 liquefied natural gas Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 229910052976 metal sulfide Inorganic materials 0.000 description 1
- 229910052750 molybdenum Inorganic materials 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 229910052763 palladium Inorganic materials 0.000 description 1
- 230000010363 phase shift Effects 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 230000010287 polarization Effects 0.000 description 1
- 239000012716 precipitator Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 229910052761 rare earth metal Inorganic materials 0.000 description 1
- 238000012958 reprocessing Methods 0.000 description 1
- 102200118166 rs16951438 Human genes 0.000 description 1
- 229910052707 ruthenium Inorganic materials 0.000 description 1
- 238000010517 secondary reaction Methods 0.000 description 1
- 238000007086 side reaction Methods 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 229910052665 sodalite Inorganic materials 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 229950011008 tetrachloroethylene Drugs 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 231100000167 toxic agent Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
- UBOXGVDOUJQMTN-UHFFFAOYSA-N trichloroethylene Natural products ClCC(Cl)Cl UBOXGVDOUJQMTN-UHFFFAOYSA-N 0.000 description 1
- 229910052721 tungsten Inorganic materials 0.000 description 1
- 239000011800 void material Substances 0.000 description 1
- 239000002699 waste material Substances 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
Landscapes
- Treating Waste Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、重質油(重油,廃
プラスチックの熱分解ワックスなどのC12+からなる
高級炭化水素)の軽質化(C1〜4:ガス成分,C5〜
11:ガソリン成分などの低級炭化水素化)、及びdeN
Ox,deCOx,VOCの分解除去などの排煙処理に関
する。The present invention relates to lightening of heavy oils (higher hydrocarbons composed of C12 + such as heavy oil and pyrolysis wax of waste plastics) (C1-4: gas components, C5-5).
11: lower hydrocarbons such as gasoline components) and deN
The present invention relates to flue gas treatment such as decomposition and removal of Ox, deCOx, and VOC.
【0002】[0002]
【従来の技術】(重質油の軽質化)炭素数1〜5程度の
ガス状炭化水素(CH4,C2H6,C3H8,C4H10,C
5H12など)は良好な還元剤であり、これらは脱硝反応
などにおけるアンモニア,尿素などの還元剤の代替とな
り得ることが知られている。具体的には、重油を燃料と
するディーゼル原動機設備の排煙脱硝などにおいて、燃
料重油の一部をガス化し、炭素数1〜5程度のガス状炭
化水素に効率よく軽質化できれば、それを還元剤として
活用することにより、アンモニア,尿素などの還元剤が
不要で、しかも安価な脱硝システムの構築が可能とな
る。BACKGROUND OF THE INVENTION (weight lightening of fuel oil) containing 1-5 about gaseous hydrocarbon carbon (CH 4, C 2 H 6 , C 3 H 8, C 4 H 10, C
Such as 5 H 12) is a good reducing agent, these are ammonia, be possible replacement of a reducing agent such as urea are known, such as in the denitration reaction. Specifically, in the flue gas denitrification of diesel motor equipment using heavy oil as fuel, a part of fuel heavy oil is gasified, and if it can be efficiently lightened to gaseous hydrocarbons having about 1 to 5 carbon atoms, it is reduced. Utilization as an agent makes it possible to construct an inexpensive denitration system that does not require a reducing agent such as ammonia or urea.
【0003】従来、ナフサ(重質ガソリン)などの炭素
数6〜10の炭化水素からCH4,C2H6などのガス状
低級炭化水素へ軽質化する方法としては、図10〜12
に示す「スチーム・リフォーミング法」がある。これ
は、ニッケル触媒などの存在下で高温(500〜900
℃),高圧(30〜50atm)中での水蒸気による重
質油の直接軽質化分解法であり、大量生産に適した手法
として確立されている。Conventionally, as a method for lightening a hydrocarbon having 6 to 10 carbon atoms such as naphtha (heavy gasoline) to a lower gaseous hydrocarbon such as CH 4 or C 2 H 6 , FIGS.
There is a “steam reforming method” shown in FIG. This is because of the high temperature (500-900
℃), high-pressure (30-50atm), direct lightening cracking of heavy oil by steam, which has been established as a method suitable for mass production.
【0004】また、触媒担持ゼオライトによる重質油の
軽質化は、現在、300〜400℃,10〜20atm
という条件下で広く行われている。[0004] Lightening of heavy oil with a catalyst-supporting zeolite is currently performed at 300 to 400 ° C and 10 to 20 atm.
It is widely performed under such conditions.
【0005】(deNOx及びdeCOx)石油,石
炭,LNGなどの化石燃料の燃焼時には、NOx,SO
x,COxなどといった有害ガスが発生するので、これ
らを無害化する必要がある。また、最近では地球環境保
護の観点から、無害であっても多量の排出に対する規制
が検討されているCO2をはじめとする温室効果ガスの
分解処理も必要とされてきている。[0005] (deNOx and deCOx) When burning fossil fuels such as petroleum, coal and LNG, NOx, SO
Since harmful gases such as x and COx are generated, it is necessary to make these harmless. In recent years, from the viewpoint of protection of the global environment, it has been required to decompose greenhouse gases such as CO 2 , for which regulations on large amounts of harmless emissions are being studied.
【0006】従来、deNOxに関しては、化石燃料燃
焼を伴う製鉄・鉄鋼,非鉄金属,紙・パルプ,窯業・セ
メント,電力,石油・化学,廃棄物焼却場,原動機な
ど、産業のあらゆる分野において、おもにアンモニア接
触還元法(SCR法〜350℃)が確立した手法として
適用されている。Conventionally, deNOx is mainly used in all fields of industry, such as iron and steel, non-ferrous metals, paper and pulp, ceramics and cement, electric power, petroleum and chemicals, waste incineration plants, and prime movers involving fossil fuel combustion. The ammonia catalytic reduction method (SCR method to 350 ° C.) has been applied as an established method.
【0007】SCR法は、高温(〜350℃)でアンモ
ニア,尿素などを還元剤として利用する直接接触還元法
である。The SCR method is a direct catalytic reduction method using ammonia, urea or the like as a reducing agent at a high temperature (up to 350 ° C.).
【0008】また、同じく高温領域において、金属Cu
を担持したZSM−5ゼオライト(Si/Al=31)
を用いた手法も自動車やディーゼル内燃機関などの排煙
処理技術として確立されている。In the same high temperature region, metal Cu
-5 zeolite carrying Si (Si / Al = 31)
Has been established as a technology for treating flue gas in automobiles and diesel internal combustion engines.
【0009】更に、プラズマによる脱硝技術についても
今日、種々研究されている。例えば、特開平6−269
635号公報には、プラズマを利用した排ガス処理装置
について記載されている。[0009] Further, various researches have been conducted on the denitration technology using plasma. For example, JP-A-6-269
No. 635 describes an exhaust gas treatment device using plasma.
【0010】deCOxに関しては、とくにCO2のメ
タノール化による燃料化が提唱され、各種の手法が検討
されている。メタノールへの再燃料化技術に関して言及
すれば、CO2のCO化、及び、CO+2H2→CH3O
H反応の達成が重要であり、とくに、CO+2H2→C
H3OH反応に関しては、工業生産レベルでは(CO+
2H2)なる水性ガスを、ZnO触媒中で高温(300
〜400℃),高圧(150〜200atm)で合成す
る。[0010] Regarding deCOx, in particular, the conversion of CO 2 into methanol has been proposed, and various methods have been studied. As for the refueling technology to methanol, CO 2 is converted into CO and CO + 2H 2 → CH 3 O
It is important to achieve the H reaction, especially CO + 2H 2 → C
Regarding the H 3 OH reaction, (CO +
2H 2 ) in a ZnO catalyst at a high temperature (300
~ 400 ° C) and high pressure (150 ~ 200atm).
【0011】その他、遷移金属触媒担持ゼオライトなど
による水素化反応としてのメタノール生成が行われてい
る。In addition, methanol is produced as a hydrogenation reaction using a zeolite supporting a transition metal catalyst.
【0012】 CO + 2H2 → CH3OH (発熱反応) 熱力学的及び化学量論的平衡条件からは、冷却,加圧に
よって反応は促進平衡する。CO + 2H 2 → CH 3 OH (exothermic reaction) From thermodynamic and stoichiometric equilibrium conditions, the reaction is accelerated by cooling and pressurizing.
【0013】また、CO2のCO化に関しては、プラズ
マ処理による還元が有望であり、種々研究されている。Regarding the conversion of CO 2 to CO, reduction by plasma treatment is promising, and various studies have been made.
【0014】(VOC(揮発性有機化合物)の分解)ベ
ンゼン,トリクロロエチレン,テトラクロロエチレン,
ダイオキシン類の4物質は、1997年4月からの大気
汚染防止法・改正で「排出または飛散を早急に抑制しな
ければならない」指定物質であり、対策がとくに必要で
ある。(Decomposition of VOC (Volatile Organic Compound)) Benzene, trichloroethylene, tetrachloroethylene,
The four dioxins are designated by the Air Pollution Control Law / Amendment from April 1997 as "designated emission or scattering must be suppressed immediately", and special measures are required.
【0015】VOCの発生は、化石燃料の燃焼時に排煙
中に含まれるNOx,SOx,COx,炭化水素,ハロ
ゲンガスなどが成分となって、350℃近傍の温度領域
において、おもにボイラ,電気集塵機電極などの金属を
触媒に合成される。The generation of VOCs is mainly caused by boilers and electric precipitators in a temperature range around 350 ° C., when NOx, SOx, COx, hydrocarbons, halogen gas and the like contained in flue gas when fossil fuels are combusted. It is synthesized using a metal such as an electrode as a catalyst.
【0016】したがって、とくに廃棄物焼却場排煙にお
いての対策が急務であり、その他、ガソリンの燃焼排煙
中にもベンゼンなどは含まれており、エンジン(原動
機)対策も重要視されている。Therefore, it is urgently necessary to take measures especially for smoke emission from a waste incineration plant, and in addition, benzene and the like are contained in gasoline combustion smoke, and measures for an engine (motor) are also regarded as important.
【0017】従来のVOC分解除去方法には、おもに燃
焼触媒法(>450℃)や活性炭吸着法などがある。The conventional VOC decomposition and removal methods mainly include a combustion catalyst method (> 450 ° C.) and an activated carbon adsorption method.
【0018】また、プラズマによるVOC分解技術につ
いては、種々の物質(ベンゼン,トリクロロエチレン,
テトラクロロエチレン,アセトン,フロン類,トルエ
ン,他)に関する研究が試みられ、それぞれの成果が得
られている。図13に ベッド・リアクター方式による
希薄ベンゼン(200ppm)の分解装置を、図14,
15にその結果を示す。本方式は、同軸円筒で電極を構
成し、電極間に誘電体粒(セラミック・ペレット)を充
填して高圧交番電圧を印加する。両電極に接触する誘電
体粒は帯電し、更に、誘電体粒同士の接触により隣接す
る誘電体粒が次々に帯電することによって、誘電体粒全
体が帯電して分極する。排煙ガスはこの誘電体粒中を通
過するように流され、その際各分極誘電体粒の保有する
分極電界によって電離,プラズマ化され、励起電子の運
動エネルギーはVOC分子と衝突し、分子中の2重結合
の乖離や水素ラジカルによるハロゲン結合の乖離,非環
化,低級炭化水素化などの分解を受ける。Regarding the VOC decomposition technology using plasma, various substances (benzene, trichloroethylene,
Research on tetrachloroethylene, acetone, chlorofluorocarbons, toluene, etc.) has been attempted, and each result has been obtained. FIG. 13 shows a device for decomposing dilute benzene (200 ppm) by the bed reactor method.
15 shows the results. In this method, electrodes are formed of coaxial cylinders, and dielectric particles (ceramic pellets) are filled between the electrodes to apply a high alternating voltage. The dielectric particles in contact with both electrodes are charged, and the adjacent dielectric particles are successively charged by the contact between the dielectric particles, so that the entire dielectric particles are charged and polarized. The flue gas is passed through the dielectric particles and is ionized and turned into plasma by the polarization electric field of each polarized dielectric particle. The kinetic energy of the excited electrons collides with the VOC molecules, and , And dissociation of halogen bonds due to hydrogen radicals, decyclization, lower hydrocarbon conversion, and the like.
【0019】[0019]
【発明が解決しようとする課題】上述したような従来の
技術では、次のような問題点がある。The above-mentioned prior art has the following problems.
【0020】(重質油の軽質化)従来の技術は、重質油
を燃料とする原動機などの機関における排煙処理に、還
元剤としてのガス状低級炭化水素を重質油燃料の軽質化
により直接得ようとするものであり、例えば、脱硝にお
けるNOx1000ppmに対応して1000ppmの
CH4+C2H6+C3H8+C4H10+C5H12の混合物炭
化水素を得るものである。その意味で軽質油を大量生産
する必要はなく、むしろ、大掛かりな装置(高温,高
圧,それに耐え得る触媒など)を必要とせず、比較的コ
ンパクトで安価な手法が必要とされる。(Lightening of Heavy Oil) The conventional technology is to use gaseous lower hydrocarbons as a reducing agent to lighten heavy oil fuel for exhaust gas treatment in engines such as motors using heavy oil as fuel. the is intended to be obtained directly, for example, thereby obtaining a mixture hydrocarbons corresponding to NOx1000ppm 1000 ppm of CH 4 + C 2 H 6 + C 3 H 8 + C 4 H 10 + C 5 H 12 in the denitration. In that sense, there is no need to mass-produce light oil, but rather a relatively compact and inexpensive method that does not require large-scale equipment (high temperature, high pressure, a catalyst that can withstand it, etc.).
【0021】また、触媒担持ゼオライトによる重質油の
軽質化は、上記のような利用目的から、更なる低温,低
圧化が望まれている。For the lightening of heavy oil by using a catalyst-supporting zeolite, further lowering the temperature and pressure is desired for the above-mentioned purpose of use.
【0022】(deNOx及びdeCOx)SCR法や
Cu−ZSM−5法などに代表される手法は、高温領域
で有効な手法である。しかし、高温領域技術に関して
は、高温排煙中(>300℃)で合成されるベンゼン,
ダイオキシン類など有害VOC(揮発性有機化合物)の
抑制対策上、今後、より低温化が検討される必要があ
る。(DeNOx and deCOx) Techniques such as the SCR method and the Cu-ZSM-5 method are effective in a high temperature region. However, with regard to high-temperature technology, benzene synthesized in high-temperature flue gas (> 300 ° C),
In order to control harmful VOCs (volatile organic compounds) such as dioxins, it is necessary to consider lowering the temperature in the future.
【0023】一方プラズマ法は、低温領域で有効な手法
であるが単独ではNO2などの有害物質を発生し、その
2次処理が必要となる。その意味でプラズマ法は、低温
化に対して有意であるが単独では有効でない。On the other hand, the plasma method is an effective method in a low temperature region, but generates harmful substances such as NO 2 by itself and requires a secondary treatment. In that sense, the plasma method is significant for lowering the temperature, but is not effective alone.
【0024】つまり、従来技術である特開平6−269
635号公報のようなプラズマを利用した排ガス処理装
置でのプロセスをNOxについて記述すれば、以下の通
りとなる。That is, Japanese Patent Application Laid-Open No. Hei 6-269
A process in an exhaust gas treatment apparatus using plasma as disclosed in Japanese Patent Application Laid-Open No. 635 is described below with respect to NOx.
【0025】 2NO + e → N2 + O2 + e 2e + 2NO2 → N2 + 2O2 + 2e 上記のプラズマ励起反応により、NOxはN2に還元さ
れるが、同時に発生するO2あるいはO3がN2を再酸化
し、一般的条件ではNOがNO2に酸化されて反応が終
了する。[0025] By 2NO + e → N 2 + O 2 + e 2e + 2NO 2 → N 2 + 2O 2 + 2e the plasma excitation reactions, NOx is reduced to N2, the O2 or O 3 generated at the same time N 2 is reoxidized, and under general conditions, NO is oxidized to NO 2 and the reaction is terminated.
【0026】この反応により生成されるNO2はNOよ
り毒性の高い有害物質である。したがって、このままで
の処理の終了は不可能であることから、一般に、従来技
術では吸着剤装置のようなNO2の後処理が必要とな
る。よって、NOxのプラズマ単独処理によるdeNO
xの課題は、同時に発生するO2,O3の除去にある。NO 2 generated by this reaction is a harmful substance having higher toxicity than NO. Therefore, since it is impossible to end the treatment as it is, generally, the prior art requires post-treatment of NO 2 as in an adsorbent device. Therefore, deNO by the plasma alone treatment of NOx
The problem of x lies in the removal of O 2 and O 3 that occur simultaneously.
【0027】また、deCOxにおけるCO2のCO化
に関しては、プラズマ処理による還元が有望であるが、 2e + 2CO2 → 2CO + O2 + 2e においてCO2はCOに還元されるが、同時に発生する
O2あるいはO3がCOを再酸化し、CO2が発生するこ
とからdeNOxと同様にdeCOxの課題は、同時に
発生するO2,O3の除去にある。With regard to the conversion of CO 2 into CO in deCOx, reduction by plasma treatment is promising, but CO 2 is reduced to CO in 2e + 2CO 2 → 2CO + O 2 + 2e, but it is generated simultaneously. Since O 2 or O 3 re-oxidizes CO to generate CO 2 , the problem of deCOx is removal of O 2 and O 3 which are generated at the same time as deNOx.
【0028】(VOC(揮発性有機化合物)の分解)V
OCの発生メカニズム,発生源などについては従来の技
術で述べたが、その除去方法はおもに、燃焼触媒法(>
450℃),活性炭吸着法などによる。しかし、いずれ
の手法においても、350℃領域でのVOCの再合成,
吸着物の脱着,再処理などの問題があり、必要十分では
ない。(Decomposition of VOC (Volatile Organic Compound))
Although the generation mechanism and source of OC have been described in the related art, the removal method is mainly the combustion catalyst method (>
450 ° C), by the activated carbon adsorption method. However, in either method, VOC resynthesis in the 350 ° C. region,
There is a problem such as desorption and reprocessing of the adsorbate, which is not necessary and sufficient.
【0029】また、ベッド・リアクター方式によるベン
ゼンの分解では、図17,18に示すようにC2H2(ア
セチレン)の他、NOx,O3などの副生成物を発生し
ている。NOx,O3はいずれも有害物質であり、無害
化処理が必要とされる。本方式の副生成物の発生は、ベ
ンゼン200ppmを除く多量の空気がプラズマにより
同時に分解を受け、N2がO2あるいはO3によって酸化
されNOxを生じている。したがって、deNOx,d
eCOxと同様にO2,O3の除去対策が必要となる。Further, in the degradation of benzene with bed reactor system, other C 2 H 2 (acetylene) as shown in FIGS. 17 and 18, are generated NOx, by-products such as O 3. Both NOx and O 3 are harmful substances and require detoxification treatment. In the generation of by-products in this method, a large amount of air excluding 200 ppm of benzene is simultaneously decomposed by plasma, and N 2 is oxidized by O 2 or O 3 to generate NOx. Therefore, deNOx, d
As with eCOx, it is necessary to take measures for removing O 2 and O 3 .
【0030】また、ハロゲン化VOCの場合は更に、分
離したハロゲンの金属触媒などによる選択的除去、具体
的には、例えば、ゼオライト活性点への吸着などによる
固定がO2,O3の除去と同様に必要となる。In the case of halogenated VOCs, selective removal of separated halogens with a metal catalyst or the like, for example, fixation by adsorption to active sites of zeolite, etc., means that O 2 and O 3 can be removed. Required as well.
【0031】この発明は、上記の3つの処理、すなわち
重質油の軽質化deNOx及びdeCOxVOC
の分解除去などの排煙処理を、プラズマと無機イオン交
換体の組み合わせで構成し、しかも無機イオン交換体に
担持する触媒を変化させるだけで全て同一の構成により
処理できる装置及びその方法の提供を目的とする。According to the present invention, the above-mentioned three treatments, that is, heavy oil lightening deNOx and deCOxVOC
The present invention provides an apparatus and a method thereof, wherein a flue gas treatment such as decomposition and removal of a gas is constituted by a combination of a plasma and an inorganic ion exchanger, and all the treatment can be carried out by the same constitution only by changing a catalyst carried on the inorganic ion exchanger. Aim.
【0032】[0032]
【課題を解決するための手段】(重質油の軽質化)この
発明は、少量のガス状低級炭化水素を大掛かりな装置に
よらず、比較的コンパクトで安価に得る装置及び方法で
ある。触媒担持ゼオライトによる重質油の軽質化は通
常、300〜400℃,10〜20atmにおいて広く
行われている手法である。本発明は、この手法をベース
に、反応をより低温(〜150℃),低圧(常圧)で実
行する手段として、プラズマ分解との組み合わせを採用
した。SUMMARY OF THE INVENTION (Lightening of Heavy Oil) The present invention is an apparatus and method for obtaining a small amount of gaseous lower hydrocarbons relatively inexpensively without using a large-scale apparatus. Lightening of heavy oil with a catalyst-supported zeolite is a widely practiced method usually at 300 to 400 ° C. and 10 to 20 atm. The present invention employs a combination with plasma decomposition as a means for executing the reaction at a lower temperature (up to 150 ° C.) and a lower pressure (normal pressure) based on this method.
【0033】本発明によれば、まずガス化された重質油
が処理装置(反応槽)中に導入される。反応槽内は、触
媒担持ゼオライト・ハニカムとそのハニカム中にほぼ上
下・左右、交互対称に配設された誘電体被覆管,正/負
線電極対とから構成され、電極間には高圧交番電圧が印
加される。According to the present invention, first, gasified heavy oil is introduced into a processing apparatus (reaction tank). The inside of the reaction tank is composed of a zeolite / catalyst carrying a catalyst, a dielectric coating tube and a positive / negative electrode pair arranged approximately symmetrically vertically and horizontally in the honeycomb, and a high-voltage alternating voltage is applied between the electrodes. Is applied.
【0034】誘電体被覆管は、高圧交番電圧によって帯
電・分極し、正/負極に対応してそれぞれ逆位相へ分極
し、両誘電体被覆管には常に交番高電界が発生する。The dielectric cladding is charged and polarized by the high alternating voltage, and is polarized in opposite phases corresponding to the positive / negative poles, and an alternating high electric field is always generated in both dielectric claddings.
【0035】交番高電界は、試料ガス(重質油ガス)を
課電(電荷を課すこと)し、試料ガス分子中の電子は電
界により加速,励起され、その運動エネルギーは周囲の
軽量分子(H2O,H2,O2,N2など)を加速,励起
し、やがて試料ガス分子の一部がイオン化,ラジカル化
(H+,0H-,N3+,02-など)して、他分子との酸
化,還元反応を行う。The alternating high electric field applies (charges) the sample gas (heavy oil gas), the electrons in the sample gas molecules are accelerated and excited by the electric field, and their kinetic energy is reduced by the surrounding light molecules ( H 2 O, H 2, O 2, etc. N 2) accelerated, excited, eventually partially ionized sample gas molecules, radicalization (H +, 0H -, N 3+, 0 2- , etc.) to Performs oxidation and reduction reactions with other molecules.
【0036】以上のメカニズムからなるプラズマ発生に
伴うラジカル種の化学作用により、試料ガス(重質油ガ
ス)は、低分子炭化水素への軽質化が実行されるが、同
時にO2ラジカルによる酸化反応(ケトン化,アルコー
ル化など)等のその他の副次反応も実行される。The sample gas (heavy oil gas) is lightened into low-molecular hydrocarbons by the chemical action of the radical species accompanying the plasma generation constituted by the above mechanism, but at the same time, the oxidation reaction by O 2 radicals is performed. Other side reactions such as (ketonization, alcoholization, etc.) are also performed.
【0037】したがって、より効率の良い軽質化反応を
実行,制御するには、同時進行する副次反応の内、おも
にO2ラジカルによる酸化反応の抑制が重要課題であ
り、その方法としては触媒によるゼオライトなどの活性
点へのO2吸着が有望である。Therefore, in order to execute and control a more efficient lightening reaction, it is important to suppress the oxidation reaction mainly by O 2 radicals among the secondary reactions which proceed simultaneously. O 2 adsorption on active sites, such as zeolite is promising.
【0038】なおかつ、ゼオライト活性点の異性化機
能,担持触媒の水素化機能は軽質化を促進し、併せて活
用することにより、より選択的に低分子軽質化が実行さ
れる。Furthermore, the isomerization function of the zeolite active site and the hydrogenation function of the supported catalyst promote lightening, and by utilizing them together, lightening of low molecular weight can be more selectively performed.
【0039】また、その他の軽質化過程で生成される一
部の高級炭化水素,ケトン類,アルコール類,炭素など
はゼオライト中の内部、あるいは表面近傍に分子篩効
果,選択的吸着効果などによって捕捉され、排出が抑制
される。In addition, some higher hydrocarbons, ketones, alcohols, carbon, etc. generated in other lightening processes are trapped inside or near the surface of the zeolite by a molecular sieve effect, a selective adsorption effect, and the like. , Emission is suppressed.
【0040】但し、これら捕獲された02,一部の高級
炭化水素,ケトン類,アルコール類,炭素などの増大
は、次第に内部、及び表面の活性点,選択的吸着点など
を占有し、新たな選択吸着,分子篩機能を低下させ、ま
た、本来の異性化,水素化機能をも低下させ軽質化を阻
害する。However, the increase of these trapped O 2 , some higher hydrocarbons, ketones, alcohols, carbon, etc., gradually occupies the active sites on the inside and on the surface, selective adsorption sites, etc. It reduces the selective adsorption and molecular sieving functions, and also lowers the original isomerization and hydrogenation functions, which hinders lightening.
【0041】したがって、これら内部、及び表面に捕獲
された副次生成物を定期的に分解,還元,炭化水素化な
どする目的で、反応槽内に水素を導入し、水素雰囲気中
での水素プラズマによる捕獲副次生成物の水素化分解を
行い、ゼオライト・ハニカム及び担持触媒のクリーニン
グ,再活性化を行う。Accordingly, hydrogen is introduced into the reaction tank for the purpose of periodically decomposing, reducing, or hydrocarbon-converting the by-products trapped inside and on the surface thereof, and the hydrogen plasma in a hydrogen atmosphere is introduced. Hydrodecomposition of trapped by-products is performed to clean and reactivate the zeolite honeycomb and the supported catalyst.
【0042】(deNOx及びdeCOx)deNOx
について本発明では、重質油の軽質化と同様にガス化さ
れた排煙が処理装置(反応槽)中に導入される。(DeNOx and deCOx) deNOx
In the present invention, gasified flue gas is introduced into a treatment device (reaction tank) in the same manner as lightening of heavy oil.
【0043】反応槽などの構成は、前記した重質油の軽
質化の場合と同じである。The configuration of the reaction tank and the like are the same as those for the lightening of the heavy oil described above.
【0044】すなわち、反応槽は触媒担持ゼオライト・
ハニカムと、そのハニカム中にほぼ上下・左右、交互対
称に配設された誘電体被覆管,正/負線電極対とから構
成され、電極間には高圧交番電圧が印加される。That is, the reaction vessel is a catalyst-supported zeolite.
It is composed of a honeycomb, a dielectric coating tube and a positive / negative wire electrode pair which are arranged substantially symmetrically in the honeycomb vertically and horizontally, and a high alternating voltage is applied between the electrodes.
【0045】誘電体被覆管は、高圧交番電圧によって帯
電・分極し、正/負極に対応してそれぞれ逆位相へ分極
し、両誘電体被覆管には常に交番高電界が発生する。The dielectric cladding is charged and polarized by the high alternating voltage, and is polarized in opposite phases corresponding to the positive / negative poles, and an alternating high electric field is always generated in both dielectric claddings.
【0046】交番高電界は、試料ガス(排煙ガス)を課
電し、試料ガス分子中の電子は電界により加速,励起さ
れ、その運動エネルギーは周囲の軽量分子(H2O,
H2,O2,N2など)を加速,励起し、やがて試料ガス
分子の一部がイオン化,ラジカル化(H+,0H-,
N3+,02-など)して、他分子との酸化,還元反応を行
う。The alternating high electric field impresses the sample gas (flue gas), the electrons in the sample gas molecules are accelerated and excited by the electric field, and their kinetic energy is reduced by the surrounding light molecules (H 2 O,
H 2 , O 2 , N 2, etc.) are accelerated and excited, and then some of the sample gas molecules are ionized and radicalized (H + , 0H − ,
N 3+ , O 2−, etc.) to perform oxidation and reduction reactions with other molecules.
【0047】このプロセスをNOxについて記述すれば
以下の通りとなる。This process is described below for NOx.
【0048】 2NO + e → N2 + O2 + e 2e + 2NO2 → N2 + 2O2 + 2e 上記のプラズマ励起反応により、NOxはN2に還元さ
れるが、同時に発生するO2あるいはO3がN2を再酸化
し、一般的条件ではNOがNO2に酸化されて反応が終
了する。2NO + e → N 2 + O 2 + e 2e + 2NO 2 → N 2 + 2O 2 + 2e By the above plasma excitation reaction, NOx is reduced to N 2 , but simultaneously generated O 2 or O 2 3 re-oxidizes N 2 , and under general conditions NO is oxidized to NO 2 and the reaction is terminated.
【0049】前述したように、この反応により生成され
るNO2はNOより毒性の高い有害物質であり、したが
ってこのままで処理を終了することは不可能であること
から、一般に、従来技術のようなNO2の後処理が必要
である。As described above, NO 2 generated by this reaction is a toxic substance that is more toxic than NO, and therefore, it is impossible to end the treatment as it is. Post treatment of NO 2 is required.
【0050】本発明では、ゼオライト・ハニカムに担持
した触媒の機能により、発生したO2,O3などを選択適
にゼオライト・ハニカム活性点に吸着・除去し、N2の
再酸化を防止する。In the present invention, the generated O 2 , O 3, etc. are selectively and appropriately adsorbed to and removed from the active sites of the zeolite honeycomb by the function of the catalyst supported on the zeolite honeycomb, thereby preventing the re-oxidation of N 2 .
【0051】NOxはN2に還元され、無害化されて放
出される一方、O2,O3などは担持触媒の還元性,ゼオ
ライト等無機イオン交換体の選択的イオン吸着性によ
り、ゼオライト内部、あるいは表面近傍の活性点に固着
される。NOx is reduced to N 2 and detoxified and released. On the other hand, O 2 , O 3 and the like are reduced in the zeolite due to the reducing property of the supported catalyst and the selective ion adsorption of inorganic ion exchangers such as zeolite. Alternatively, they are fixed to active points near the surface.
【0052】しかし、O2の吸着量の増大と共に、活性
点はO2に占有され、新たなO2の吸着能は低下し、した
がってN2のNO2への酸化反応が発生する。これらを防
止し内部及び表面に捕獲されたO2,O3などを定期的に
分解,還元(H2O化)する目的で反応槽内に水素を導
入し、水素雰囲気中での水素プラズマによる水素化分解
を行い、ゼオライト・ハニカム及び担持触媒のクリーニ
ング,再活性化を行う。However, as the amount of O 2 adsorbed increases, the active sites are occupied by O 2 , and the new O 2 adsorbing ability decreases, and thus the oxidation reaction of N 2 to NO 2 occurs. Hydrogen is introduced into the reactor for the purpose of preventing them and periodically decomposing and reducing (converting to H 2 O) O 2 , O 3, etc. trapped inside and on the surface, and using hydrogen plasma in a hydrogen atmosphere. Hydrocracking is performed to clean and reactivate the zeolite honeycomb and the supported catalyst.
【0053】deCOxのメカニズムについても同様で
あり、まずCOx中のCO2のCOへの還元を行い、次
にCOの水素化反応によるメタノール化を行う。The same applies to the mechanism of deCOx. First, CO 2 in COx is reduced to CO, and then methanolization is performed by hydrogenation of CO.
【0054】CO2のCO化に関しては、プラズマ処理
による還元を行い、 2e + 2CO2 → 2CO + O2 + 2e 上記反応においてCO2はCOに還元されるが、同時に
発生するO2あるいはO3がCOを再酸化し、CO2が発
生する。Regarding the conversion of CO 2 into CO, reduction by plasma treatment is performed, and 2e + 2CO 2 → 2CO + O 2 + 2e In the above reaction, CO 2 is reduced to CO, but O 2 or O 3 generated simultaneously Reoxidizes CO to generate CO 2 .
【0055】したがって、この際もdeNOx同様、触
媒担持ゼオライト・ハニカムに担持した触媒の機能によ
り、発生したO2,O3などを選択適にゼオライト・ハニ
カム活性点に吸着・除去し、COの再酸化を防止する。Therefore, in this case, as in the case of deNOx, the generated O 2 , O 3, etc. are selectively adsorbed and removed to the active sites of the zeolite honeycomb by the function of the catalyst supported on the zeolite honeycomb supporting the catalyst, and the CO is regenerated. Prevent oxidation.
【0056】CO2はCOに還元され、水素化反応によ
るメタノール化を行う一方、O2,O3などは担持触媒の
還元性,ゼオライト等無機イオン交換体の選択的イオン
吸着性により、ゼオライト内部、あるいは表面近傍の活
性点に固着される。CO 2 is reduced to CO and is converted to methanol by a hydrogenation reaction. On the other hand, O 2 , O 3 and the like are reduced in the zeolite due to the reducing property of the supported catalyst and the selective ion adsorption of an inorganic ion exchanger such as zeolite. Alternatively, they are fixed to active points near the surface.
【0057】次に、COのH2による水素化反応として
のメタノール生成が行われる。Next, methanol is produced as a hydrogenation reaction of CO with H 2 .
【0058】 CO + 2H2 → CH3OH (発熱反応) 熱力学的及び化学量論的平衡条件からは、冷却,加圧に
よって反応は促進平衡する。CO + 2H 2 → CH 3 OH (exothermic reaction) From thermodynamic and stoichiometric equilibrium conditions, the reaction is accelerated by cooling and pressurizing.
【0059】プラズマ過程における、上記混合ガス中で
の高圧課電により、水素は容易に電離し、水素イオンラ
ジカルの生成による水素化反応を促進する。一方、
O2,O3選択吸着触媒,ゼオライト活性点機能などはこ
れらCO,H2などをもよく選択吸着し、水素化反応を
促進するのに有効となる。In the plasma process, hydrogen is easily ionized by applying a high voltage in the above-mentioned mixed gas, thereby promoting a hydrogenation reaction by generation of hydrogen ion radicals. on the other hand,
The O 2 and O 3 selective adsorption catalyst, zeolite active site function and the like are also effective for selectively adsorbing these CO and H 2, etc., and promoting the hydrogenation reaction.
【0060】そして適時、反応槽内に水素を導入し、水
素雰囲気中での水素プラズマによる水素化分解を行い、
ゼオライト・ハニカム及び担持触媒のクリーニング,再
活性化を行う。Then, when appropriate, hydrogen is introduced into the reaction tank, and hydrogenolysis is performed by hydrogen plasma in a hydrogen atmosphere.
Cleaning and reactivation of zeolite honeycomb and supported catalyst.
【0061】(VOC(揮発性有機化合物)の分解)V
OCの分解過程におけるプラズマの機能は、ガス分子中
の電子が電界により加速,励起され、その運動エネルギ
ーは周囲の軽量分子(H2O,H2,O2,N2など)を
加速,励起し、やがてガス分子の一部がイオン化、ラジ
カル化(H+,0H-,N3+,02-など)して、他分子
との酸化,還元反応を行うことによる分解作用、とくに
脱ハロゲン化,非環化がその目的となる。(Decomposition of VOC (volatile organic compound))
The function of the plasma in the process of decomposing OC is that electrons in gas molecules are accelerated and excited by an electric field, and the kinetic energy accelerates and excites surrounding light molecules (H 2 O, H 2 , O 2 , N 2, etc.). Eventually, some of the gas molecules are ionized or radicalized (H + , 0H − , N 3+ , O 2−, etc.) and decomposed by performing oxidation and reduction reactions with other molecules, especially dehalogenation. Cyclization and decyclization are the objectives.
【0062】但し、プラズマ単独処理においては、分解
生成物中に含まれるのハロゲンガス,NOx,O3その
他中間有害化合物などの発生と、その無害化処理を検討
する必要があり、本発明で使用する触媒担持ゼオライト
・ハニカムはその目的のためのものとなる。However, in the case of the plasma alone treatment, it is necessary to consider the generation of halogen gas, NOx, O 3 and other intermediate harmful compounds contained in the decomposition product, and the detoxification treatment thereof. The resulting catalyst-supported zeolite honeycomb is for that purpose.
【0063】遷移金属触媒によるゼオライト活性点への
ハロゲン吸着,O2,O3の選択吸着によるNOx発生の
防止、ゼオライト活性点の異性化,水素化,分子篩など
の機能による中間有害化合物の更なる低分子化,炭化水
素化,内部保留の促進などが想定され、分解VOCの分
子構造にあわせた担持触媒種,ゼオライト種などの選
択、組み合わせが有効となる。Halogen adsorption to zeolite active sites by transition metal catalysts, prevention of NOx generation by selective adsorption of O 2 and O 3 , further conversion of intermediate harmful compounds by functions such as zeolite active site isomerization, hydrogenation and molecular sieve It is assumed that the molecular weight is reduced, the hydrocarbon is converted, and the internal retention is promoted, and selection and combination of a supported catalyst type, a zeolite type, and the like according to the molecular structure of the cracked VOC are effective.
【0064】また、補集したハロゲンガス,O2,O3中
間有害化合物などの活性点への吸着量の増大は、新たな
吸着を阻害し、無害化処理を不完全なものとする。した
がって、定期的に、これら内部、及び表面に捕獲された
副次生成物を分解,還元、更なる炭化水素化などをする
目的で、反応槽内に水素を導入し、水素雰囲気中での水
素プラズマによる捕集副次生成物の水素化分解を行い、
ゼオライト・ハニカム及び担持触媒のクリーニング,再
活性化を行う。Further, an increase in the amount of adsorbed halogen gas, O 2 , O 3 intermediate harmful compounds and the like at active sites inhibits new adsorption and makes the detoxification process incomplete. Therefore, hydrogen is periodically introduced into the reaction tank for the purpose of decomposing, reducing, and further converting hydrocarbons to the by-products trapped inside and on the surface thereof. Hydrocracking of by-products collected by plasma is performed,
Cleaning and reactivation of zeolite honeycomb and supported catalyst.
【0065】(重質油のプラズマによる軽質化実験)図
7に示す通り、誘電体球ペレット(BaTiO3:チタ
ン酸バリウム、誘電率=4500)中にA重油を含浸さ
せて円筒ガラス管(直径30φ)中に充填し、上端及び
下端を円盤状の金属(SUS)で封印する。誘電体球ペ
レットはの円盤によって加圧・圧縮されて相互接触し、
かつ上端及び下端のペレットは円盤に接している。(Lightening Experiment by Plasma of Heavy Oil) As shown in FIG. 7, a dielectric spherical pellet (BaTiO 3 : barium titanate, dielectric constant = 4500) was impregnated with heavy oil A to form a cylindrical glass tube (diameter). 30φ), and the upper and lower ends are sealed with a disk-shaped metal (SUS). The dielectric sphere pellets are pressurized and compressed by a disk and come into contact with each other,
The upper and lower pellets are in contact with the disk.
【0066】円盤は電極を兼ねており、両端に商用周波
(50Hz),15kVの高圧交番電圧が印加される。
また反応槽内にはアルゴンガスをキャリアガスとして流
し、O2,N2パージを行い、かつプラズマ発生に伴う発
熱冷却も併せて行う。The disk also serves as an electrode, and a high-frequency alternating voltage of 15 kV with a commercial frequency (50 Hz) is applied to both ends.
Also, argon gas is flowed into the reaction tank as a carrier gas, O 2 and N 2 are purged, and the heat generated by plasma generation is also cooled.
【0067】誘電体球ペレットは高圧交番電圧によって
課電されて、分極し、交番電界を発生する。さらに電界
はセル内部のガスを課電し、セル中にはアルゴンガス及
び誘電体ペレットから気化したA重油ガスが充満してお
り、これらのガスは電界によって課電され、加速励起さ
れた電子などの運動エネルギーを受けた周囲の軽量分子
(H2O,H2,O2,N2など)は加速,励起し、やがて
ガス分子の一部がイオン化,ラジカル化(H+,0H-,
N3+,02-など)して、他分子との酸化,還元反応を行
う。The dielectric sphere pellet is charged by the high alternating voltage, polarizes and generates an alternating electric field. In addition, the electric field charges the gas inside the cell, and the cell is filled with argon gas and A heavy oil gas vaporized from the dielectric pellets. These gases are charged by the electric field and accelerated excited electrons, etc. Surrounding light molecules (H 2 O, H 2 , O 2 , N 2, etc.) that have received the kinetic energy of are accelerated and excited, and then some of the gas molecules are ionized and radicalized (H + , 0H − ,
N 3+ , O 2−, etc.) to perform oxidation and reduction reactions with other molecules.
【0068】図8に交番高電圧を印加した場合の発生ガ
ス成分を捕集し、成分分析した結果を示す。FIG. 8 shows the results of collecting and analyzing the generated gas components when an alternating high voltage is applied.
【0069】この結果によれば、分解ガス成分は、C2
H4(エチレン),CH4(メタン)、C3H8(プロパ
ン),C2H6(エタン),その他などであり、その内エ
チレンが発生ガス量の60vol%程度を占める。According to the result, the decomposition gas component was C 2
Examples include H 4 (ethylene), CH 4 (methane), C 3 H 8 (propane), C 2 H 6 (ethane), and others, of which ethylene accounts for about 60 vol% of the generated gas amount.
【0070】また、発生ガス量の増加時間は本装置では
2min程度であり、それ以降の電圧印加に対しての分
解ガスの発生は認められず、この事より、誘電体球ペレ
ット中に含浸したA重油は2min程度で、ある部分が
分解され、それ以降の分解はそれ以上進行しない状況に
あるものと思われる。The increase time of the amount of generated gas was about 2 minutes in the present apparatus, and no generation of decomposition gas was observed when the voltage was applied after that. Therefore, it was impregnated into the dielectric sphere pellet. It is considered that heavy fuel oil A was decomposed in about 2 minutes, and a certain portion was decomposed, and the subsequent decomposition did not proceed any more.
【0071】反応の律速要因については、 全ての誘電体球ペレットが誘電分極した状態ではな
く、円盤電極に接する近傍のペレ ットのみから分解
ガスが発生し、その他のペレットは反応に寄与していな
い。Regarding the rate-determining factors of the reaction, not all the dielectric sphere pellets are in a dielectrically polarized state, but a decomposition gas is generated only from the pellet near the disk electrode, and the other pellets contribute to the reaction. Absent.
【0072】分解反応に関与したペレットについて
は、その表面に炭素数6〜12程度の液状炭化 水素
(ガソリン質)が付着し誘電体活性が低下した。With respect to the pellets involved in the decomposition reaction, liquid hydrocarbons (gasoline) having about 6 to 12 carbon atoms adhered to the surfaces thereof, and the dielectric activity was reduced.
【0073】などの可能性があり、反応槽としてのこれ
らへの改善が必要となる。[0073] There is a possibility of such a problem, and it is necessary to improve these as a reaction tank.
【0074】図9は、発生ガス成分のGC−MSによる
詳細分析結果を示す。この結果によれば、炭素数1〜5
程度の炭化水素,アルコール,ケトン類の生成が見ら
れ、とくにC3H8(プロパン)の生成が顕著である。FIG. 9 shows a detailed analysis result of the generated gas component by GC-MS. According to this result, carbon number 1-5
Production of hydrocarbons, alcohols and ketones to some extent is observed, and production of C 3 H 8 (propane) is particularly remarkable.
【0075】これら個々の発生物質に関する生成条件と
制御方法に関する情報は別途把握するとして、プラズマ
による重質油の軽質化により、脱硝などでのアンモニ
ア,尿素に代替する還元剤としての炭素数1〜5程度の
炭化水素(混合物)がの入手が可能であることが改めて
確認された。It is assumed that information on the generation conditions and the control method for each of these generated substances is separately grasped, and that the heavy oil is lightened by plasma to reduce the carbon number of 1 to 1 as a reducing agent in place of ammonia and urea in denitration and the like. It was again confirmed that about 5 hydrocarbons (mixtures) were available.
【0076】(触媒を担持していない無機イオン交換体
とプラズマを併用した脱硝実験)本実験は、無機イオン
交換体としてZSM−5,NaYのゼオライトを用い
た。但し、ゼオライト中への酸化,還元などの触媒は担
持されていない物を用いた。また、線電極は裸線の状態
(誘電体被覆をしていない)でハニカム(5mmメッシ
ュ)中にアース極(●),高圧極(○)を左右・上下ほ
ぼ対称(千鳥格子状)に配列し、ハニカム中に試料ガス
(ディーゼルエンジンの排気ガス:NOx濃度=150
〜200ppm)を流し、両電極管に高電圧パルスを印
加する。(Denitration experiment using plasma together with an inorganic ion exchanger not carrying a catalyst) In this experiment, ZSM-5 and NaY zeolite were used as the inorganic ion exchanger. However, a catalyst such as oxidation and reduction into zeolite which is not supported was used. The wire electrodes are bare wires (not covered with a dielectric material) and the ground electrode (●) and high-voltage electrode (○) are almost symmetrical in the left-right and up-down directions (in a staggered pattern) in a honeycomb (5 mm mesh). The sample gas (exhaust gas of diesel engine: NOx concentration = 150) was arranged in the honeycomb.
200200 ppm) and apply a high voltage pulse to both electrode tubes.
【0077】高電圧パルスによって、試料ガス中の電子
は励起され、運動エネルギーを近傍分子に与え、その内
の軽量分子(H2O,H2,O2,N2など)は加速,励起
し、やがてガス分子の一部がイオン化,ラジカル化(H
+,0H-,N3+,02-など)して、他分子との酸化,還
元反応を行う。Electrons in the sample gas are excited by the high voltage pulse, giving kinetic energy to nearby molecules, and light-weight molecules (H 2 O, H 2 , O 2 , N 2, etc.) are accelerated and excited. Eventually, some of the gas molecules are ionized and radicalized (H
+ , 0H − , N 3+ , 0 2−, etc.) to perform oxidation and reduction reactions with other molecules.
【0078】ゼオライトは無機イオン交換体であり、S
i/Al比においてNaY=1.0,ZSM−5=31
で、その活性点数は NaY>>ZSM−5 であることより、耐絶縁性に関してはNaY<<ZSM
−5となり、誘電体被覆なしでの高電圧印加において
は、NaYでは電圧上昇時(15kVまで)にしばしば
絶縁破壊が発生し、十分な昇圧が行われず、したがって
プラズマ発生が不十分となり、データの取得が不可能と
なった。よって、活性点数の少ないZSM−5について
のみ特性評価を行った。Zeolite is an inorganic ion exchanger,
NaY = 1.0, ZSM-5 = 31 in i / Al ratio
Since the number of active points is NaY >> ZSM-5, the insulation resistance is NaY << ZSM
−5, when applying a high voltage without a dielectric coating, dielectric breakdown often occurs with NaY when the voltage rises (up to 15 kV), and sufficient boosting is not performed. Therefore, plasma generation becomes insufficient, and data Acquisition became impossible. Therefore, characteristic evaluation was performed only on ZSM-5 having a small number of active points.
【0079】このことから、活性点数の多いNaY,モ
ルデナイト,ZK−5などによる特性評価を実施するに
は、線電極を誘電体被覆管で被覆し、高圧交番電圧印加
によるプラズマ発生方式の採用が好ましいことが判明し
た。From the above, in order to evaluate the characteristics using NaY, mordenite, ZK-5, etc. having a large number of active points, it is necessary to cover the wire electrodes with a dielectric coating tube and adopt a plasma generation method by applying a high alternating voltage. It turned out to be favorable.
【0080】触媒無担持ZSM−5中、裸線電極挿入/
高圧パルス電圧印加プラズマ発生方式におけるNOxの
分解結果を図6に示す。実験結果によれば、投入電力
(watt)に対するNOxの除去率は単調増加の関係
にあるが、1/m(m=正数)乗の関係で除去率は低減
することが分かる。この際の分解反応は通常、 NO→NO2 への酸化反応が中心となるが、本実験においてはNOの
約30%が NO→N2O なる形で、還元反応が実行された。Insertion of bare wire electrode in ZSM-5 without catalyst
FIG. 6 shows the result of decomposition of NOx in the high-pressure pulse voltage applied plasma generation system. According to the experimental results, the removal rate of NOx with respect to the input power (watt) has a monotonically increasing relationship, but the removal rate decreases with the power of 1 / m (m = positive number). Usually, the decomposition reaction at this time mainly involves an oxidation reaction from NO to NO 2 , but in this experiment, a reduction reaction was performed in a form in which about 30% of NO was changed from NO to N 2 O.
【0081】この還元反応の実行要因は、ゼオライト活
性点へのO2の吸着によるものと思われ、ゼオライトに
よる還元効果が想定される。The cause of the reduction reaction is considered to be the adsorption of O 2 to the active site of zeolite, and the reduction effect of zeolite is assumed.
【0082】したがって、還元効果をより顕著に増大さ
せる方策として、より活性点の多いNaY,モルデナイ
ト,ZK−5系ゼオライトにO2吸着促進触媒を担持す
ることが好ましく、かつ、プラズマ発生の観点から、誘
電体への高圧交番電圧課電方式による発生方法の採用が
好ましいことが判明した。Therefore, as a measure to remarkably increase the reduction effect, it is preferable to carry an O 2 adsorption promoting catalyst on NaY, mordenite, or ZK-5 zeolite having more active sites, and from the viewpoint of plasma generation. It has been found that it is preferable to employ a method of generating a high voltage alternating voltage on the dielectric.
【0083】また、図6によれば、酸化,還元反応は1
20〜150℃温度レベルにおいて達成され、上記還元
効果増大化策の実行により低温領域(120〜150
℃)での脱硝が実現される。According to FIG. 6, the oxidation and reduction reactions are 1
Achieved at a temperature level of 20 to 150 ° C., and by implementing the above-described measures for increasing the reduction effect, a low-temperature region (120 to 150
C) is realized.
【0084】(重質油の軽質化・排煙処理装置)処理対
象ガスが流通する配管内に反応槽を配置し、前記反応槽
内に無機イオン交換体から成るハニカムを設置し、処理
対象ガスと前記ハニカムとを接触させるように構成した
重質油の軽質化・排煙処理装置において、前記ハニカム
の各空孔部に誘電体被覆管により被覆された線電極を正
極・負極一対になる位置関係でそれぞれ挿入配置し、前
記線電極間には高圧交番電圧を印加することによってプ
ラズマを発生させ、前記ハニカムには触媒を担持したこ
とを特徴とするものである。(Heavy oil lightening and flue gas treatment apparatus) A reaction tank is disposed in a pipe through which a gas to be treated flows, and a honeycomb made of an inorganic ion exchanger is installed in the reaction tank. In the heavy oil lightening and flue gas treatment apparatus configured to contact the honeycomb with the honeycomb, a position in which each of the pores of the honeycomb is covered with a dielectric coating tube to form a pair of a positive electrode and a negative electrode. Plasma is generated by applying a high alternating voltage between the line electrodes, and a catalyst is carried on the honeycomb.
【0085】(重質油の軽質化方法)プラズマによる重
質油の直接軽質化分解と、無機イオン交換体の活性点に
おける異性化機能および担持触媒の水素化機能による軽
質化反応を相補的に組み合わせることを特徴とする。(Method of Lightening Heavy Oil) The direct lightening decomposition of heavy oil by plasma and the lightening reaction by the isomerization function at the active site of the inorganic ion exchanger and the hydrogenation function of the supported catalyst are complemented. It is characterized by being combined.
【0086】(deNOx方法)プラズマによるNOx
の直接N2還元と、前記N2還元の際に発生するO2を担
持触媒による無機イオン交換体の活性点に吸着,除去
し、N2の再酸化を防止してdeNOxを行うことを特
徴とする。(DeNOx method) NOx by plasma
Direct NO 2 reduction and O 2 generated during the N 2 reduction are adsorbed and removed at the active sites of the inorganic ion exchanger by a supported catalyst, and deNOx is performed while preventing re-oxidation of N 2. And
【0087】(deCOx方法)プラズマによるCOx
+H2ガスでの直接メタノール生成と、前記メタノール
生成の再に発生するO2を担持触媒による無機イオン交
換体の活性点に吸着,除去し、COの再酸化を防止して
deCOxを行うことを特徴とする。(DeCOx Method) COx by Plasma
Direct methanol generation with + H 2 gas and O 2 generated at the re-generation of methanol are adsorbed and removed at the active sites of the inorganic ion exchanger by the supported catalyst, and deCOx is performed while preventing re-oxidation of CO. Features.
【0088】(VOCの分解方法)プラズマによるVO
Cの直接反応を無機イオン交換体の活性点における異性
化機能と担持触媒による脱水素化機能,ハロゲン吸着機
能を組み合わせて分解することを特徴とする。(Method of Decomposing VOC) VO by Plasma
It is characterized in that the direct reaction of C is decomposed by combining the isomerization function at the active site of the inorganic ion exchanger, the dehydrogenation function using a supported catalyst, and the halogen adsorption function.
【0089】[0089]
【発明の実施の形態】以下、本発明の実施の形態を図面
に基づいて説明する。図1は、本発明の実施の形態を示
す重質油の軽質化・排煙処理装置の無機イオン交換体と
プラズマ発生部の概略構成図で、図2はその側面図であ
る。1は無機イオン交換体であるゼオライト・ハニカム
で、反応を促進するための触媒2が選択的に担持されて
いる。ゼオライト・ハニカム1のメッシュ状の空孔部1
aには、誘電体被覆管4により被覆された線電極3a,
3bが正極・負極一対で左右・上下対称に(千鳥格子
状)挿入配置され、誘電体支持部材5によって固定され
ている。6は交流電源であり、配電線3から線電極3
a,3bへとつながっている。この線電極3a,3b間
に電源6からの高圧交番電圧を印加することによって、
プラズマを発生させるように構成されている。Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a schematic configuration diagram of an inorganic ion exchanger and a plasma generator of a heavy oil lightening and flue gas treatment apparatus according to an embodiment of the present invention, and FIG. 2 is a side view thereof. Reference numeral 1 denotes a zeolite honeycomb, which is an inorganic ion exchanger, on which a catalyst 2 for promoting the reaction is selectively supported. Mesh-shaped voids 1 of zeolite honeycomb 1
a includes line electrodes 3a covered with a dielectric coating tube 4;
A pair of positive and negative electrodes 3 b are inserted and arranged symmetrically in a left-right and up-down direction (in a zigzag pattern) and fixed by a dielectric support member 5. Reference numeral 6 denotes an AC power supply,
a, 3b. By applying a high alternating voltage from the power supply 6 between the line electrodes 3a and 3b,
It is configured to generate plasma.
【0090】なお、線電極3a,3bは正極・負極一対
で左右・上下対称に(千鳥格子状)配置するのが望まし
いが、発生する電界の不均一などの諸条件から、ほぼ左
右・上下対称に(千鳥格子状)配置すればよい。また、
誘電体支持部材4は、ゼオライト・ハニカム1の空孔部
1aに導入される処理対象ガスの導入の妨げにならない
程度に、その形状を考慮して小片化される必要がある。It is desirable that the line electrodes 3a and 3b are arranged in a pair of positive and negative electrodes symmetrically in the left-right and up-down directions (in a staggered pattern). What is necessary is just to arrange symmetrically (houndstooth check). Also,
The dielectric support member 4 needs to be formed into small pieces in consideration of its shape so as not to hinder the introduction of the gas to be treated introduced into the pores 1 a of the zeolite honeycomb 1.
【0091】ゼオライト・ハニカム1のゼオライト種別
については、活性点の密度(Si/Al比)から、Na
A,LiA,ソーダライト(1.0),ZK−5(2.
2),Y(2.6),モルデナイト(5.0),ZSM
−5(31),ZSM−11(40)などがあり、更
に、それらをベースとしてAlイオンと置換する種々の
触媒2としては、触媒活性金属イオン,金属酸化物,金
属硫化物などがあり、それらの組み合わせによって目的
とする反応を達成する。Regarding the zeolite type of the zeolite honeycomb 1, the density of active sites (Si / Al ratio)
A, LiA, sodalite (1.0), ZK-5 (2.
2), Y (2.6), mordenite (5.0), ZSM
-5 (31), ZSM-11 (40) and the like, and various catalysts 2 based on them for replacing with Al ions include catalytically active metal ions, metal oxides and metal sulfides. The desired reaction is achieved by their combination.
【0092】ゼオライト・ハニカム1のゼオライト種別
と担持する触媒2の具体例を以下に示す。Specific examples of the zeolite type of the zeolite honeycomb 1 and the catalyst 2 to be supported are shown below.
【0093】重質油の軽質化、芳香族の脂肪族炭化水
素化 (水素化反応) a.Fe(8〜10族遷移金属)イオン含有Yゼオライ
ト b.(Pt,Ni,Co,Mo,W)硫化物Yゼオライ
ト c.希土類金属イオン含有Yゼオライト(REYゼオラ
イト) d.Cu/ZnO,CrO Yゼオライト 脱硝(deNOx),deCOx,メタノール化 a.Cuイオン交換ZSM−5(deNOx) b.Ceイオン交換ZSM−5(deNOx) c.(Fe,Co,Ni,Ru)シリケートZSM−5
(deCOx) d.(Pt,Pd,Ir)イオン交換ZSM−5(メタ
ノール) 脱ハロゲン化 a.Cuイオン交換ZSM−5 b.Niイオン交換ZSM−5 処理対象ガスは、ハニカム・ゼオライト1の空孔部1a
に導入され、プラズマラジカルによって軽質化分解,還
元,脱ハロゲン化,非環化(脂肪族炭化水素化),メタ
ノール化などの処理を施される。Lightening of heavy oil, conversion of aromatic aliphatic hydrocarbon (hydrogenation reaction) a. Y zeolite containing Fe (Group 8-10 transition metal) ion b. (Pt, Ni, Co, Mo, W) sulfide Y zeolite c. Rare earth metal ion-containing Y zeolite (REY zeolite) d. Cu / ZnO, CrO Y zeolite denitration (deNOx), deCOx, methanolization a. Cu ion exchange ZSM-5 (deNOx) b. Ce ion exchange ZSM-5 (deNOx) c. (Fe, Co, Ni, Ru) silicate ZSM-5
(DeCOx) d. (Pt, Pd, Ir) ion exchange ZSM-5 (methanol) dehalogenation a. Cu ion exchange ZSM-5 b. Ni ion exchange ZSM-5 The gas to be treated is the pore 1a of the honeycomb zeolite 1.
And subjected to treatments such as lightening decomposition, reduction, dehalogenation, non-cyclization (aliphatic hydrocarbon conversion), and methanolization by plasma radicals.
【0094】一般に直流またはパルス高電圧によるプラ
ズマ発生方式は、電極間での相対距離やミクロな表面形
状などの物理的条件の微妙な差異によって、往々にして
電極表面全面による均一なプラズマ発生は達成されな
い。したがって、本実施の形態のように誘電体被覆管4
に高圧交番電圧を印加することによって誘電体被覆管4
を分極させ、交番高電界を発生させる方式を採用する方
が、電極表面全面による均一なプラズマ発生上望まし
い。In general, a plasma generation method using a direct current or a pulsed high voltage often achieves uniform plasma generation over the entire electrode surface due to a slight difference in physical conditions such as a relative distance between electrodes and a microscopic surface shape. Not done. Therefore, as in the present embodiment, the dielectric coating tube 4
The high voltage alternating voltage is applied to the
It is more desirable to employ a method of generating an alternating high electric field by polarizing the electrode in order to generate a uniform plasma over the entire electrode surface.
【0095】また、ゼオライト・ハニカム1との反応の
相補的促進効果の組み合わせを主眼とした本発明におい
て、ゼオライトは無機イオン交換体でイオン導電性を有
することから、高電圧を直接印加出来ない性状からも、
本実施の形態のように誘電体課電方式を採用する方が望
ましい。In the present invention, which mainly focuses on the combination of the effect of complementarily promoting the reaction with the zeolite honeycomb 1, the zeolite is an inorganic ion exchanger and has ionic conductivity, so that a high voltage cannot be directly applied. From
It is desirable to adopt a dielectric charging method as in this embodiment.
【0096】更に、誘電体被覆管4の物性については比
誘電率によって規定され、商用周波においてはε=40
00〜5000程度が望ましく、それより小さな比誘電
率においては電力効率が低下する。また、交番周波数依
存性は高周波電力の場合、無効電力分が増加するのでこ
の場合も電力効率が低下する。材料としては、BaTi
O3,CaTiO3,SrTiO3,石英ガラスなどが望
ましい。Further, the physical properties of the dielectric coating tube 4 are defined by the relative permittivity, and ε = 40 at the commercial frequency.
It is desirable to be about 00 to 5000, and the power efficiency is reduced when the relative dielectric constant is smaller than about 5000. In addition, in the case of high frequency power, the alternation frequency dependency increases the reactive power, so that the power efficiency also decreases in this case. The material is BaTi
O 3 , CaTiO 3 , SrTiO 3 , quartz glass and the like are desirable.
【0097】線電極3a,3bの配置に関しては、図1
に示すように交番電極の双方を(●,○)で表示したよ
うに配置している。したがって線電極3a,3bは、そ
の位相が180゜ずれることにより、両電極間には常に
100%の電圧が印加され、それに伴う電界が発生し、
かつ左右・上下において対局に位置することにより、プ
ラズマの発生はハニカム・ゼオライト1の全域に及び良
好な反応場が形成される。The arrangement of the line electrodes 3a and 3b is shown in FIG.
As shown in the figure, both of the alternating electrodes are arranged as indicated by (●, ○). Therefore, the line electrodes 3a and 3b are always applied with a voltage of 100% between the two electrodes due to a phase shift of 180 °, and an electric field is generated accordingly.
In addition, by being located on the opposite sides in the left, right, up and down directions, the generation of plasma extends over the entire area of the honeycomb zeolite 1 and a favorable reaction field is formed.
【0098】以上の構成を基本として、ガスの流量(N
m3/hr),要求処理速度,圧力損失,電力効率,処
置装置形状などの諸条件を勘案して、ハニカムメッシュ
形状・寸法,ハニカム縦・横・長さ寸法,印加電圧,電
流,周波数,電源容量などを設計する。Based on the above configuration, the gas flow rate (N
m3 / hr), taking into account various conditions such as required processing speed, pressure loss, power efficiency, treatment device shape, etc., the honeycomb mesh shape / dimension, honeycomb length / width / length dimension, applied voltage, current, frequency, power supply Design capacity etc.
【0099】図3に反応槽10の中に設置された触媒2
を担持したゼオライト・ハニカム1の構成例を示す。触
媒2を担持したゼオライト・ハニカム1は、反応槽10
の中に固定・設置される。処理対象ガスは、反応槽10
に取り付けられた誘導ダクト11に誘導されて反応槽1
0内へ送り込まれる。この誘導ダクト11は、処理対象
ガスを誘導すると同時に、反応槽10内のクリーニン
グ,ゼオライト・ハニカムの再活性化を行うにための、
水素プラズマ発生用水素ガスの導入用ダクトとしても機
能する。FIG. 3 shows the catalyst 2 installed in the reaction tank 10.
1 shows an example of the configuration of a zeolite honeycomb 1 that carries. The zeolite honeycomb 1 supporting the catalyst 2 is supplied to the reaction vessel 10
It is fixed and installed inside. The gas to be treated is the reactor 10
The reaction tank 1 is guided by the induction duct 11 attached to the
It is sent into 0. The guide duct 11 is used for cleaning the inside of the reaction tank 10 and reactivating the zeolite honeycomb at the same time as guiding the gas to be treated.
It also functions as a duct for introducing hydrogen gas for generating hydrogen plasma.
【0100】誘導ダクト11の入口部11a,出口部1
1bは、電磁バルブ13,14などで流入,流出ガス量
の流量調整を行うと同時に、流入,流出ガス種の切り替
え調節も併せて行う。The entrance 11a and the exit 1 of the guide duct 11
1b adjusts the flow rate of the inflow and outflow gas amounts by the electromagnetic valves 13 and 14, etc., and also adjusts the switching of the inflow and outflow gas types.
【0101】図4にプラズマ発生用の線電極3a,3b
及び誘電体被覆管4,電磁バルブ13,14,高圧交番
電圧・電流発生電源6,ガス流量調節部7,制御部8な
どから構成される「触媒担持 ゼオライト・ハニカム構
造体中 誘電体課電プラズマ発生 重畳方式−重質油軽
質化/排煙種理装置システム」を示す。本システムは、
ガス流量,圧力,温度,電圧,電流,流入ガス性状,流
出ガス性状,添加ガス性状などをモニターして最適制御
が実行される。FIG. 4 shows line electrodes 3a and 3b for plasma generation.
And a dielectric coating tube 4, electromagnetic valves 13 and 14, a high-voltage alternating voltage / current generating power supply 6, a gas flow control unit 7, a control unit 8, etc. Generation superposition method-heavy oil lightening / smoke flue speculation system ". This system is
Optimal control is executed by monitoring the gas flow rate, pressure, temperature, voltage, current, inflow gas property, outflow gas property, added gas property, and the like.
【0102】[0102]
【発明の効果】以上述べたように、本発明によれば、
重質油の軽質化deNOx及びdeCOxVOCの
分解除去などの排煙処理を、プラズマ+無機イオン交換
体で行い、無機イオン交換体に担持する触媒を適当なも
のに変えるだけで全て同一の装置により処理できる。As described above, according to the present invention,
The flue gas treatment such as the lightening of heavy oil deNOx and deCOxVOC is carried out by plasma + inorganic ion exchanger, and all are treated by the same equipment just by changing the catalyst carried on the inorganic ion exchanger to an appropriate one. it can.
【図面の簡単な説明】[Brief description of the drawings]
【図1】本発明の実施の形態を示す触媒担持ゼオライト
・ハニカムとプラズマ発生部の概略構成の正面図。FIG. 1 is a front view of a schematic configuration of a catalyst-carrying zeolite honeycomb and a plasma generating unit according to an embodiment of the present invention.
【図2】本発明の実施の形態を示す触媒担持ゼオライト
・ハニカムとプラズマ発生部の概略構成の側面図。FIG. 2 is a side view showing a schematic configuration of a catalyst-carrying zeolite honeycomb and a plasma generating unit according to the embodiment of the present invention.
【図3】本発明の実施の形態を示す反応槽構成図。FIG. 3 is a configuration diagram of a reaction tank showing an embodiment of the present invention.
【図4】本発明の実施の形態を示すシステム構成図。FIG. 4 is a system configuration diagram showing an embodiment of the present invention.
【図5】触媒を担持していない無機イオン交換体とプラ
ズマを併用した脱硝実験の概略構成図。FIG. 5 is a schematic configuration diagram of a denitration experiment using a plasma in combination with an inorganic ion exchanger not carrying a catalyst.
【図6】触媒を担持していない無機イオン交換体とプラ
ズマを併用した脱硝実験の実験結果を表す図。FIG. 6 is a diagram showing experimental results of a denitration experiment in which a plasma is used in combination with an inorganic ion exchanger not carrying a catalyst.
【図7】重質油のプラズマによる軽質化実験の概略構成
図。FIG. 7 is a schematic configuration diagram of a lightening experiment using heavy oil plasma.
【図8】重質油のプラズマによる軽質化実験の生成ガス
特性図。FIG. 8 is a characteristic diagram of generated gas in a lightening experiment using heavy oil plasma.
【図9】重質油のプラズマによる軽質化実験によって生
成されたガスの分析図。FIG. 9 is an analysis diagram of a gas generated in a lightening experiment using heavy oil plasma.
【図10】スチーム・リフォーミング法を述べるための
図。FIG. 10 is a diagram for describing a steam reforming method.
【図11】スチーム・リフォーミング法を述べるための
特性図。FIG. 11 is a characteristic diagram for describing a steam reforming method.
【図12】スチーム・リフォーミング法を述べるための
特性図。FIG. 12 is a characteristic diagram for describing a steam reforming method.
【図13】ベッド・リアクター方式による分解装置の概
略構成図。FIG. 13 is a schematic configuration diagram of a decomposition apparatus using a bed reactor system.
【図14】ベッド・リアクター方式による希薄ベンゼン
の分解特性。FIG. 14 shows decomposition characteristics of dilute benzene by a bed reactor system.
【図15】ベッド・リアクター方式による希薄ベンゼン
の分解特性。FIG. 15 shows decomposition characteristics of dilute benzene by a bed reactor system.
1…ゼオライト・ハニカム 1a…空孔部 2…触媒 3…配電線 3a,3b…線電極 4…誘電体被覆管 5…誘電体支持部材 6…交流電源 7…流量調節部 8…制御部 10…反応槽 11…誘導ダクト 11a…入口部 11b…出口部 12,13…電磁バルブ DESCRIPTION OF SYMBOLS 1 ... Zeolite honeycomb 1a ... Void part 2 ... Catalyst 3 ... Distribution line 3a, 3b ... Wire electrode 4 ... Dielectric coating tube 5 ... Dielectric support member 6 ... AC power supply 7 ... Flow control part 8 ... Control part 10 ... Reaction tank 11 ... Induction duct 11a ... Inlet 11b ... Outlet 12,13 ... Electromagnetic valve
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI C10G 49/04 B01D 53/36 101Z ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification code FI C10G 49/04 B01D 53/36 101Z
Claims (5)
を配置し、前記反応槽内に無機イオン交換体から成るハ
ニカムを設置し、処理対象ガスと前記ハニカムとを接触
させるように構成した重質油の軽質化・排煙処理装置に
おいて、 前記ハニカムの各空孔部に誘電体被覆管により被覆され
た線電極を正極・負極一対になる位置関係でそれぞれ挿
入配置し、前記線電極間には高圧交番電圧を印加するこ
とによってプラズマを発生させ、前記ハニカムには触媒
を担持したことを特徴とする重質油の軽質化・排煙処理
装置。1. A reaction vessel is arranged in a pipe through which a gas to be treated flows, a honeycomb made of an inorganic ion exchanger is installed in the reaction vessel, and the honeycomb is made to contact the gas to be treated with the honeycomb. In the heavy oil lightening and flue gas treatment apparatus, wire electrodes covered with a dielectric coating tube are inserted and arranged in each of the holes of the honeycomb in a positional relationship of a positive electrode and a negative electrode, and A plasma is generated by applying a high alternating voltage to the honeycomb, and a catalyst is supported on the honeycomb.
と、無機イオン交換体の活性点における異性化機能およ
び担持触媒の水素化機能による軽質化反応を相補的に組
み合わせることを特徴とする重質油の軽質化方法。2. A heavy-duty fuel characterized in that the direct light-weight cracking of heavy oil by plasma and the lightening reaction by the isomerization function at the active site of the inorganic ion exchanger and the hydrogenation function of the supported catalyst are complementarily combined. Lightening method of high quality oil.
と、前記N2還元の際に発生するO2を担持触媒による無
機イオン交換体の活性点に吸着,除去し、N2の再酸化
を防止してdeNOxを行うことを特徴とする排煙処理
方法。3. A direct N 2 reduction of NOx by the plasma, the N 2 adsorption of O 2 generated during the reduction in active sites of inorganic ion exchangers according to the supported catalyst, is removed, to prevent re-oxidation of N2 And performing deNOx by using a smoke exhaust treatment method.
接メタノール生成と、前記メタノール生成の再に発生す
るO2を担持触媒による無機イオン交換体の活性点に吸
着,除去し、COの再酸化を防止してdeCOxを行う
ことを特徴とする排煙処理方法。Prevention 4. A direct methanol production in COx + H 2 gas plasma, adsorption of O 2 occurring again in the methanol generated active sites of the inorganic ion exchanger by supported catalyst, removed, re-oxidation of the CO And performing deCOx.
イオン交換体の活性点における異性化機能と担持触媒に
よる脱水素化機能,ハロゲン吸着機能を組み合わせて分
解することを特徴とする排煙処理方法。5. A method for treating flue gas, comprising decomposing a direct reaction of VOC by plasma by a combination of an isomerization function at an active site of an inorganic ion exchanger, a dehydrogenation function using a supported catalyst, and a halogen adsorption function.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10090485A JPH11285616A (en) | 1998-04-02 | 1998-04-02 | Heavy oil lightening/flue gas treating device and method therefor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10090485A JPH11285616A (en) | 1998-04-02 | 1998-04-02 | Heavy oil lightening/flue gas treating device and method therefor |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH11285616A true JPH11285616A (en) | 1999-10-19 |
Family
ID=13999862
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP10090485A Pending JPH11285616A (en) | 1998-04-02 | 1998-04-02 | Heavy oil lightening/flue gas treating device and method therefor |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH11285616A (en) |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20020003890A (en) * | 2000-06-21 | 2002-01-16 | 황해웅 | Method for treating toxic compounds by using rare earth ion-exchanged catalyst in non-thermal plasma |
| KR20020005185A (en) * | 2000-06-21 | 2002-01-17 | 황해웅 | Method for treating toxic compounds by using alkali ion-exchanged catalyst in non-thermal plasma |
| KR20020023727A (en) * | 2001-12-12 | 2002-03-29 | 김기호 | the manufacturing method of the plasma occurrence unit. |
| KR20020023728A (en) * | 2001-12-12 | 2002-03-29 | 김기호 | the manufacturing method of the plasma occurrence unit. |
| KR20030065067A (en) * | 2002-01-29 | 2003-08-06 | 사단법인 고등기술연구원 연구조합 | A Plasma Reactor for Purifying Poisonous Gas with Dielectric Barrier Structure |
| KR100472751B1 (en) * | 2002-01-29 | 2005-03-08 | 고등기술연구원연구조합 | Mixture and one-body type purification apparatus with dielectric barrier structure |
| KR100543529B1 (en) * | 2003-04-29 | 2006-01-31 | 국방과학연구소 | Air Purification System and Purification Method |
| CN119386640A (en) * | 2025-01-02 | 2025-02-07 | 信昌科技股份有限公司 | A low concentration oil and gas tail gas treatment device |
-
1998
- 1998-04-02 JP JP10090485A patent/JPH11285616A/en active Pending
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20020003890A (en) * | 2000-06-21 | 2002-01-16 | 황해웅 | Method for treating toxic compounds by using rare earth ion-exchanged catalyst in non-thermal plasma |
| KR20020005185A (en) * | 2000-06-21 | 2002-01-17 | 황해웅 | Method for treating toxic compounds by using alkali ion-exchanged catalyst in non-thermal plasma |
| KR20020023727A (en) * | 2001-12-12 | 2002-03-29 | 김기호 | the manufacturing method of the plasma occurrence unit. |
| KR20020023728A (en) * | 2001-12-12 | 2002-03-29 | 김기호 | the manufacturing method of the plasma occurrence unit. |
| KR20030065067A (en) * | 2002-01-29 | 2003-08-06 | 사단법인 고등기술연구원 연구조합 | A Plasma Reactor for Purifying Poisonous Gas with Dielectric Barrier Structure |
| KR100472751B1 (en) * | 2002-01-29 | 2005-03-08 | 고등기술연구원연구조합 | Mixture and one-body type purification apparatus with dielectric barrier structure |
| KR100543529B1 (en) * | 2003-04-29 | 2006-01-31 | 국방과학연구소 | Air Purification System and Purification Method |
| CN119386640A (en) * | 2025-01-02 | 2025-02-07 | 信昌科技股份有限公司 | A low concentration oil and gas tail gas treatment device |
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