CN108003920A - 一种用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法 - Google Patents
一种用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法 Download PDFInfo
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- CN108003920A CN108003920A CN201711133814.2A CN201711133814A CN108003920A CN 108003920 A CN108003920 A CN 108003920A CN 201711133814 A CN201711133814 A CN 201711133814A CN 108003920 A CN108003920 A CN 108003920A
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- Prior art keywords
- metal oxide
- desulfurizing agent
- cuo
- zno
- function catalyzing
- Prior art date
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- 239000003795 chemical substances by application Substances 0.000 title claims abstract description 104
- 230000003009 desulfurizing effect Effects 0.000 title claims abstract description 100
- 238000001179 sorption measurement Methods 0.000 title claims abstract description 99
- 229910044991 metal oxide Inorganic materials 0.000 title claims abstract description 70
- 150000004706 metal oxides Chemical class 0.000 title claims abstract description 70
- 238000000034 method Methods 0.000 title claims abstract description 52
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 title claims abstract description 26
- 229910052717 sulfur Inorganic materials 0.000 title claims abstract description 20
- 239000011593 sulfur Substances 0.000 title claims abstract description 20
- 239000000446 fuel Substances 0.000 claims abstract description 60
- 238000006477 desulfuration reaction Methods 0.000 claims abstract description 48
- 230000023556 desulfurization Effects 0.000 claims abstract description 44
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 claims abstract description 39
- 150000001451 organic peroxides Chemical class 0.000 claims abstract description 28
- JKQOBWVOAYFWKG-UHFFFAOYSA-N molybdenum trioxide Inorganic materials O=[Mo](=O)=O JKQOBWVOAYFWKG-UHFFFAOYSA-N 0.000 claims abstract description 26
- WGLPBDUCMAPZCE-UHFFFAOYSA-N Trioxochromium Chemical compound O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 claims abstract description 24
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 claims abstract description 24
- 125000001741 organic sulfur group Chemical group 0.000 claims abstract description 22
- 238000010521 absorption reaction Methods 0.000 claims abstract description 18
- 230000003647 oxidation Effects 0.000 claims abstract description 14
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 14
- 238000006555 catalytic reaction Methods 0.000 claims abstract description 13
- 238000005859 coupling reaction Methods 0.000 claims abstract description 10
- 230000008929 regeneration Effects 0.000 claims abstract description 9
- 238000011069 regeneration method Methods 0.000 claims abstract description 9
- 239000000463 material Substances 0.000 claims description 28
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 24
- 239000003921 oil Substances 0.000 claims description 15
- ONDPHDOFVYQSGI-UHFFFAOYSA-N zinc nitrate Chemical compound [Zn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ONDPHDOFVYQSGI-UHFFFAOYSA-N 0.000 claims description 13
- 229910052757 nitrogen Inorganic materials 0.000 claims description 12
- 238000004064 recycling Methods 0.000 claims description 12
- 238000006243 chemical reaction Methods 0.000 claims description 11
- 238000013329 compounding Methods 0.000 claims description 11
- 238000010438 heat treatment Methods 0.000 claims description 11
- 230000008569 process Effects 0.000 claims description 11
- 238000007664 blowing Methods 0.000 claims description 10
- 239000000203 mixture Substances 0.000 claims description 10
- 238000002360 preparation method Methods 0.000 claims description 10
- 238000011084 recovery Methods 0.000 claims description 10
- 239000002808 molecular sieve Substances 0.000 claims description 9
- 239000011148 porous material Substances 0.000 claims description 9
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims description 9
- 238000001354 calcination Methods 0.000 claims description 7
- XTVVROIMIGLXTD-UHFFFAOYSA-N copper(II) nitrate Chemical compound [Cu+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O XTVVROIMIGLXTD-UHFFFAOYSA-N 0.000 claims description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 7
- PNEYBMLMFCGWSK-UHFFFAOYSA-N Alumina Chemical compound [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 6
- DKGAVHZHDRPRBM-UHFFFAOYSA-N Tert-Butanol Chemical compound CC(C)(C)O DKGAVHZHDRPRBM-UHFFFAOYSA-N 0.000 claims description 6
- 239000012876 carrier material Substances 0.000 claims description 6
- 229910052751 metal Inorganic materials 0.000 claims description 6
- 239000002184 metal Substances 0.000 claims description 6
- HSJPMRKMPBAUAU-UHFFFAOYSA-N cerium(3+);trinitrate Chemical compound [Ce+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O HSJPMRKMPBAUAU-UHFFFAOYSA-N 0.000 claims description 5
- 150000002978 peroxides Chemical class 0.000 claims description 5
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 4
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 claims description 4
- 229910002796 Si–Al Inorganic materials 0.000 claims description 4
- 238000002156 mixing Methods 0.000 claims description 4
- XCRBXWCUXJNEFX-UHFFFAOYSA-N peroxybenzoic acid Chemical compound OOC(=O)C1=CC=CC=C1 XCRBXWCUXJNEFX-UHFFFAOYSA-N 0.000 claims description 4
- 229910052710 silicon Inorganic materials 0.000 claims description 4
- 239000010703 silicon Substances 0.000 claims description 4
- APUPEJJSWDHEBO-UHFFFAOYSA-P ammonium molybdate Chemical compound [NH4+].[NH4+].[O-][Mo]([O-])(=O)=O APUPEJJSWDHEBO-UHFFFAOYSA-P 0.000 claims description 3
- 229940010552 ammonium molybdate Drugs 0.000 claims description 3
- 235000018660 ammonium molybdate Nutrition 0.000 claims description 3
- 239000011609 ammonium molybdate Substances 0.000 claims description 3
- 238000009388 chemical precipitation Methods 0.000 claims description 3
- 238000005137 deposition process Methods 0.000 claims description 3
- 238000001802 infusion Methods 0.000 claims description 3
- 239000000741 silica gel Substances 0.000 claims description 3
- 229910002027 silica gel Inorganic materials 0.000 claims description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 claims description 2
- 229910021555 Chromium Chloride Inorganic materials 0.000 claims description 2
- 229910002651 NO3 Inorganic materials 0.000 claims description 2
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 claims description 2
- QSWDMMVNRMROPK-UHFFFAOYSA-K chromium(3+) trichloride Chemical compound [Cl-].[Cl-].[Cl-].[Cr+3] QSWDMMVNRMROPK-UHFFFAOYSA-K 0.000 claims description 2
- FEOIEZBSUVRDJZ-UHFFFAOYSA-N chromium;nitric acid Chemical compound [Cr].O[N+]([O-])=O FEOIEZBSUVRDJZ-UHFFFAOYSA-N 0.000 claims description 2
- 150000001875 compounds Chemical class 0.000 claims description 2
- ORTQZVOHEJQUHG-UHFFFAOYSA-L copper(II) chloride Chemical compound Cl[Cu]Cl ORTQZVOHEJQUHG-UHFFFAOYSA-L 0.000 claims description 2
- MRIZMKJLUDDMHF-UHFFFAOYSA-N cumene;hydrogen peroxide Chemical group OO.CC(C)C1=CC=CC=C1 MRIZMKJLUDDMHF-UHFFFAOYSA-N 0.000 claims description 2
- 239000007789 gas Substances 0.000 claims description 2
- 238000010792 warming Methods 0.000 claims description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims 1
- 239000001301 oxygen Substances 0.000 claims 1
- 229910052760 oxygen Inorganic materials 0.000 claims 1
- 230000003197 catalytic effect Effects 0.000 description 22
- 239000002283 diesel fuel Substances 0.000 description 14
- QDOXWKRWXJOMAK-UHFFFAOYSA-N chromium(III) oxide Inorganic materials O=[Cr]O[Cr]=O QDOXWKRWXJOMAK-UHFFFAOYSA-N 0.000 description 13
- 230000000694 effects Effects 0.000 description 11
- 239000003502 gasoline Substances 0.000 description 9
- 230000000052 comparative effect Effects 0.000 description 7
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- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- YQHLDYVWEZKEOX-UHFFFAOYSA-N cumene hydroperoxide Chemical compound OOC(C)(C)C1=CC=CC=C1 YQHLDYVWEZKEOX-UHFFFAOYSA-N 0.000 description 4
- 239000003463 adsorbent Substances 0.000 description 3
- 239000008367 deionised water Substances 0.000 description 3
- 229910021641 deionized water Inorganic materials 0.000 description 3
- 238000005265 energy consumption Methods 0.000 description 3
- 239000001257 hydrogen Substances 0.000 description 3
- 229910052739 hydrogen Inorganic materials 0.000 description 3
- 150000002431 hydrogen Chemical class 0.000 description 3
- -1 organic sulfur sulfone Chemical class 0.000 description 3
- FCEHBMOGCRZNNI-UHFFFAOYSA-N 1-benzothiophene Chemical compound C1=CC=C2SC=CC2=C1 FCEHBMOGCRZNNI-UHFFFAOYSA-N 0.000 description 2
- NIPNSKYNPDTRPC-UHFFFAOYSA-N N-[2-oxo-2-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethyl]-2-[[3-(trifluoromethoxy)phenyl]methylamino]pyrimidine-5-carboxamide Chemical compound O=C(CNC(=O)C=1C=NC(=NC=1)NCC1=CC(=CC=C1)OC(F)(F)F)N1CC2=C(CC1)NN=N2 NIPNSKYNPDTRPC-UHFFFAOYSA-N 0.000 description 2
- 230000000274 adsorptive effect Effects 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 238000001514 detection method Methods 0.000 description 2
- IYYZUPMFVPLQIF-UHFFFAOYSA-N dibenzothiophene Chemical compound C1=CC=C2C3=CC=CC=C3SC2=C1 IYYZUPMFVPLQIF-UHFFFAOYSA-N 0.000 description 2
- 238000009826 distribution Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 239000007800 oxidant agent Substances 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- 229910052573 porcelain Inorganic materials 0.000 description 2
- 230000009257 reactivity Effects 0.000 description 2
- 229960001866 silicon dioxide Drugs 0.000 description 2
- 238000005303 weighing Methods 0.000 description 2
- AXDZBUZLJGBONR-UHFFFAOYSA-N 1,2-dimethyldibenzothiophene Chemical class C1=CC=C2C3=C(C)C(C)=CC=C3SC2=C1 AXDZBUZLJGBONR-UHFFFAOYSA-N 0.000 description 1
- MYAQZIAVOLKEGW-UHFFFAOYSA-N DMDBT Natural products S1C2=C(C)C=CC=C2C2=C1C(C)=CC=C2 MYAQZIAVOLKEGW-UHFFFAOYSA-N 0.000 description 1
- 229910018557 Si O Inorganic materials 0.000 description 1
- XOLBLPGZBRYERU-UHFFFAOYSA-N SnO2 Inorganic materials O=[Sn]=O XOLBLPGZBRYERU-UHFFFAOYSA-N 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- PFRUBEOIWWEFOL-UHFFFAOYSA-N [N].[S] Chemical compound [N].[S] PFRUBEOIWWEFOL-UHFFFAOYSA-N 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- PHFQLYPOURZARY-UHFFFAOYSA-N chromium trinitrate Chemical compound [Cr+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O PHFQLYPOURZARY-UHFFFAOYSA-N 0.000 description 1
- 230000002860 competitive effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910017464 nitrogen compound Inorganic materials 0.000 description 1
- 150000002830 nitrogen compounds Chemical class 0.000 description 1
- 150000002927 oxygen compounds Chemical class 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 239000013618 particulate matter Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- LIVNPJMFVYWSIS-UHFFFAOYSA-N silicon monoxide Inorganic materials [Si-]#[O+] LIVNPJMFVYWSIS-UHFFFAOYSA-N 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 230000003335 steric effect Effects 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- 238000002604 ultrasonography Methods 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
Classifications
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- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G45/00—Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds
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- B01J37/34—Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation
- B01J37/341—Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation
- B01J37/343—Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation of ultrasonic wave energy
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G25/00—Refining of hydrocarbon oils in the absence of hydrogen, with solid sorbents
- C10G25/003—Specific sorbent material, not covered by C10G25/02 or C10G25/03
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Abstract
本发明提供一种用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法。其特征在于,所述燃料氧化脱硫方法是将有机过氧化物加入含有机硫的燃料中混合,得到含有机过氧化物的燃料;将所述含有机过氧化物的燃料通过负载型金属氧化物双功能催化吸附脱硫剂的固定床床层,室温下进行催化氧化吸附耦合反应0.5~2 h,实现燃料的反应性深度吸附脱硫;所述脱硫剂包括载体以及负载在载体上的金属氧化物,所述金属氧化物为ZnO、CuO、CeO2、CrO3、MoO3中的一种或多种,所述脱硫剂中金属氧化物的质量百分数为5~15 wt.%。脱硫剂同时具备催化和吸附两个功能,且再生利用率高。
Description
技术领域
本发明属于燃料脱硫领域,具体涉及一种用负载型金属氧化物双功能催化吸附脱硫剂 的燃料氧化脱硫方法。
背景技术
含硫燃料在燃烧过程向环境排放大量的污染物,如SO2,NOx以及颗粒物PM2.5的排放 等,对环境造成严重污染。因此,世界各国相继颁布了严格的燃料含硫标准,如何有效的生 产清洁燃料已成为全球石化企业研究的一个重要课题。
当前,炼油厂主要使用的燃料脱硫技术是加氢脱硫,其存在的主要问题是:需要在较 高的反应温度(300-400℃)和压力(3-6MPa)下进行,需大量消耗氢气,而且难脱除燃料中有 空间位阻效应的硫化物,如四六二甲基二苯并噻吩(4,6-DMDBT)等[1]([1]Song,C.S.An Overview of New Approaches to Deep Desulfurization for Ultra-cleanGasoline,Diesel Fuel and Jet Fuel.Catal.Today 2003,86,211-263.),因而用于超清洁燃料(<1ppmw-S)的生产效率低 且能耗大。因此,研发低能耗高选择性的超深度脱硫技术具有重大的国家需求和现实意义。
吸附脱硫因不消耗氢气、可在常温常压条件下,将硫化物吸附在固体多孔吸附剂表面从 而获得清洁燃料,是一种极具应用前景的燃料脱硫技术([2]Xiao,J.;Li,Z.;Liu,B.;Xia,Q.B.; Yu,M.X.Adsorption of Benzothiophene and Dibenzothiophene on Ion-impregnated Activated Carbons and Ion-Exchanged Y Zeolites.EnergyFuels 2008,22,3858-3863.)。然而,当前的吸附 脱硫技术应用于燃料超深度脱硫所面临的瓶颈问题之一是:由于燃料中其他组分的竞争吸附, 导致吸附脱硫的选择性低[3]([3]Xiao,J.;Song,C.S.;Ma,X.L.;Li,Z.Effects of Aromatics, Diesel Additives,Nitrogen Compounds,and Moisture on Adsorptive Desulfurization of Diesel Fuel over ActivatedCarbon.Ind.Eng.Chem.Res.2012,51,3436-3443.),从而导致深度脱硫困难,因 而吸附剂的脱硫吸附量很低。因而急需开发高吸附选择性和高吸附容量的新型燃料脱硫吸附 材料,和基于该材料的低能耗可循环的新型脱硫工艺。
CN102059094A公开了CuO和CrO3用于活性炭吸附脱硫中的应用,CN103540342A公开了一种用于吸附脱硫的流化床反应器极其应用,所采用的吸附脱硫催化剂是采用ZnO和Ni/Co的复配,其应用原理同样知识吸附。CN10363879A公开了一种船用柴油机脱硫填料塔,填料层表面负载有CrO3-SnO2催化剂,其所针对的是SOX气体。
发明内容
为了克服现有技术的缺点与不足,本发明的首要目的在于发明一种用负载型金属氧化物 双功能催化吸附脱硫剂的燃料氧化脱硫方法。该技术操作简单,可在常温常压下进行,不需 消耗氢气,可应用于燃料深度脱硫获超清洁燃料(<10或<1ppmw-S),材料的脱硫效率高且 可再生循环使用。
本发明的目的至少通过如下技术方案之一实现。
一种用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,所述燃料氧化 脱硫方法是将有机过氧化物加入含有机硫的燃料中混合,得到含有机过氧化物的燃料;将 所述含有机过氧化物的燃料通过负载型金属氧化物双功能催化吸附脱硫剂的固定床床层, 室温下进行催化氧化吸附耦合反应0.5~2h,实现燃料的反应性深度吸附脱硫;
所述脱硫剂包括载体以及负载在载体上的金属氧化物,所述脱硫剂中金属氧化物为 ZnO、CuO、MoO3、CeO2、CrO3中的一种或多种,所述脱硫剂中金属氧化物的质量百分数 为5~15wt.%。
优选的,所述含有机硫的燃料为柴油或汽油;所述有机过氧化物为过氧化氢异丙苯或 过氧苯甲酸或过氧化氢叔丁醇;所述有机过氧化物、燃料中有机硫的摩尔比为5~18:1。
优选的,所述负载型金属氧化物双功能催化吸附脱硫剂的比表面积在100~800m2/g范 围,孔径尺寸在1.5~10nm范围,孔容在0.2~0.8cm3/g范围。
优选的,所述负载型金属氧化物双功能催化吸附脱硫剂的制备方法是将金属氧化物的 前驱体负载在载体材料上,再将前驱体和载体的混合物通过煅烧得到所述的负载型金属氧 化物双功能催化吸附脱硫剂,所述前驱体负载在载体材料上的方法包括浸渍法、机械混合 法、溶胶凝胶法、气相沉积法、化学沉淀法;所述煅烧的方法是在空气氛围中以1-5℃/min 升温速率升温至380-450℃,煅烧时间为3.5-5.5h。
优选的,所述金属氧化物为ZnO和CuO两种复配,所述ZnO和CuO的质量比为:ZnO:CuO=5-15:1-5。
优选的,所述金属氧化物为ZnO、CuO和CeO2三种复配,所述ZnO、CuO和CeO2的 质量比为:ZnO:CuO:CeO2=5-15:1-5:1-5。
优选的,所述金属氧化物为ZnO、CuO、CeO2和CrO3四种复配,或ZnO、CuO、MoO3和CrO3四种复配,所述ZnO、CuO、CeO2和CrO3的质量比为:CrO3:MnO:ZnO:CeO2= 5-15:1-5:1-5:1-5;或ZnO、CuO、MoO3和CrO3的质量比为:ZnO:CuO:MoO3:CrO3=5-15:1-5:1-5:1-5。
优选的,所述ZnO的前驱体为硝酸锌;所述CuO的前驱体为硝酸铜或氯化铜;所述MoO3的前驱体为钼酸铵;所述CeO2的前驱体为硝酸铈、硝酸铈铵;所述CrO3的前驱体为 硝酸铬或氯化铬。
所述所述载体材料为硅胶、硅铝分子筛、纯硅分子筛或氧化铝。
优选的,将已经吸附脱硫反应后的负载型金属氧化物双功能催化吸附脱硫剂固定床床 层先通氮气热处理进行油品回收,后通空气对所述脱硫剂固定床床层进行热再生,脱硫剂 固定床床层即可循环使用;所述热再生温度为300~650℃;再生时间为2~6h。
本发明的有益效果:
(1)负载型金属氧化物双功能催化吸附脱硫剂同时具备催化和吸附两个功能。以燃料中 添加的有机过氧化物为氧化剂,在常温常压下,可在负载型金属氧化物双功能催化吸附脱硫 剂表面将燃料中的有机硫转化成极性较强的有机硫砜,脱硫剂中的金属氧化物可催化氧化反 应;与此同时,所产生的有机硫砜会在负载型金属氧化物双功能催化吸附脱硫剂表面发生较 强的吸附,从而实现燃料高效深度脱硫。
(2)该脱硫方法采用负载型金属氧化物为双功能催化吸附材料,添加有机过氧化物为氧 化剂,脱硫成本低。
(3)本发明一步法催化和吸附耦合脱硫技术,工艺简单,可在常温常压下操作,能耗低。
(4)本发明中的负载型金属氧化物双功能催化吸附材料可再生循环使用。
(5)本发明中过氧化物和燃料中有机硫以及负载型金属氧化物双功能催化吸附脱硫剂 合适的配比可以使燃料中的有机硫脱除效率更高,因为脱硫剂过少,脱硫剂催化氧化和吸 附会饱和而达不到有效脱除燃料中有机硫的目的,如果脱硫剂或者过氧化物过多,不能有 效发挥脱硫剂和过氧化物的作用,增加脱硫成本。
(6)本发明的负载型金属氧化物双功能催化吸附脱硫剂的比表面积、孔径尺寸、孔容 等性能参数优越,更利于催化氧化吸附脱硫。
(7)本发明在研究负载型金属氧化物双功能催化吸附脱硫剂的基础上还研究了不同金 属氧化物的复配对于燃料中的应用效果具有优越的效果。
具体实施方式
下面对本发明的具体实施方式作进一步说明:
(1)负载型金属氧化物双功能催化吸附脱硫剂。负载型金属氧化物双功能催化吸附脱硫 剂的制备方法是将金属氧化物的前驱体负载在载体材料上,再将前驱体和载体的混合物通过 煅烧得到所述的负载型金属氧化物双功能催化吸附脱硫剂,所述前驱体负载在载体材料上的 方法包括浸渍法、机械混合法、溶胶凝胶法、气相沉积法、化学沉淀法。
(2)负载型金属氧化物双功能催化吸附脱硫剂的燃料脱硫方法。将有机过氧化物加入含 有机硫的燃料中混合,得到含有机过氧化物的燃料;将上述燃料通过负载型金属氧化物双功 能催化吸附脱硫剂固定床床层,进行室温下的催化氧化吸附耦合反应,从而实现燃料的反应 性深度吸附脱硫;先通氮气热处理进行油品回收,后通空气对负载型金属氧化物双功能催化 吸附脱硫剂固定床床层进行热再生,催化吸附脱硫剂固定床床层即可循环使用。
实施例1
(1)负载型ZnO双功能催化吸附脱硫剂的制备:
按ZnO/载体质量比为10wt.%的比例称取0.204g Zn(NO3)2.6H2O溶于0.375mL的去离子 水中;称取0.5g活化后的工业级MCM-41分子筛,在超声氛围下充分搅拌并逐滴滴加Zn(NO3)2溶液,滴加结束后继续超声45min;将混合物放入100℃烘箱干燥2h;干燥后收集 粉末于坩埚中,在马弗炉中以1.5℃/min的升温速率升至400℃时煅烧4h,自然降温至室温 制得负载型ZnO双功能催化吸附脱硫剂。
(2)负载型ZnO双功能催化吸附脱硫剂的燃料脱硫方法:
按有机过氧化物和有机硫的摩尔比为6的比例将过氧化氢异丙苯加入柴油中混合,得 到含有机过氧化物的柴油;将上述柴油通过负载型ZnO双功能催化吸附脱硫剂固定床床层, 进行室温下的催化氧化吸附耦合反应0.5h,从而实现燃料的反应性深度吸附脱硫;将热氮 气通过反应后的负载型ZnO双功能催化吸附脱硫剂固定床床层进行油品回收,后通空气对 负载型ZnO双功能催化吸附脱硫剂固定床床层在500℃下进行热再生4h,催化吸附材料固 定床床层即可循环使用。该工艺可将50ppmw-S的国IV柴油处理到9ppmw-S获国V超清 洁柴油,处理量为80L/kg-催化吸附脱硫剂。
实施例2
(1)负载型CuO双功能催化吸附脱硫剂的制备:
将CuO的前驱体为硝酸铜1.0g前驱体溶于去离子水,按CuO/载体质量比为10wt.%的比例将CuO的前驱体溶液均匀负载到硅胶载体材料上,超声浸渍,充分混合;将混合物 放入烘箱干燥,研磨,在空气的氛围中以1.5℃/min的升温速率至400℃下煅烧4h,便制 得负载型CuO双功能催化吸附脱硫剂。
(2)负载型CuO双功能催化吸附脱硫剂的燃料脱硫新工艺:
按有机过氧化物和有机硫的摩尔比为16的比例将过氧苯甲酸加入柴油中混合,得到含 有机过氧化物的柴油;将上述柴油通过负载型CuO双功能催化吸附脱硫剂固定床床层,进 行室温下的催化氧化吸附耦合反应1h,从而实现燃料的反应性深度吸附脱硫;将热氮气通 过反应后的负载型CuO双功能催化吸附脱硫剂固定床床层进行油品回收,后通空气对负载 型CuO双功能催化吸附脱硫剂固定床床层在400℃下进行热再生4h,催化吸附材料固定床 床层即可循环使用。该工艺可将10ppmw-S的国V柴油处理到1ppmw-S获零硫柴油,处理量为120L/kg-催化吸附脱硫剂。
实施例3
(1)负载型ZnO/CuO双功能催化吸附脱硫剂的制备:
将ZnO前驱体硝酸锌和CuO前驱体硝酸铜按质量比为5:1混合,共计2.0g溶于去离子水中,按(ZnO和CuO)/载体质量比为15wt.%的比例将ZnO和CuO的前驱体溶液均匀 负载到硅铝分子筛载体材料上,超声浸渍,充分混合;将混合物放入烘箱干燥,研磨,在 空气的氛围中以1.5℃/min的升温速率升至400℃下煅烧5h,便制得负载型ZnO/CuO双功 能催化吸附脱硫剂。
(2)负载型ZnO/CuO双功能催化吸附脱硫剂的燃料脱硫新工艺:
按有机过氧化物和有机硫的摩尔比为8的比例将过氧化氢异丙苯加入汽油中混合,得 到含有机过氧化物的汽油;将上述汽油通过负载型ZnO和CuO双功能催化吸附脱硫剂固定 床床层,进行室温下的催化氧化吸附耦合反应1.5h,从而实现燃料的反应性深度吸附脱硫; 将热氮气通过反应后的负载型ZnO/CuO双功能催化吸附脱硫剂固定床床层进行油品回收, 后通空气对负载型ZnO/CuO双功能催化吸附脱硫剂固定床床层在500℃下进行热再生3h, 催化吸附材料固定床床层即可循环使用。该工艺可将50ppmw-S的国IV汽油处理到10ppmw-S获国V超清洁汽油,处理量为50L/kg-催化吸附材料。
实施例4
(1)负载型ZnO/CuO/CeO2复配双功能催化吸附脱硫剂的制备:
按金属氧化物/载体质量比为15wt.%的比例称取0.09g ZnO/CuO/CeO2的前驱体硝酸锌、 硝酸铜、硝酸铈,其中ZnO:CuO:CeO2=5:1:1,以及0.5g纯硅分子筛分别置于两个瓷舟 中,并暴露在50℃氮气氛围中吹扫30min;在管式炉中控制氮气流速为50mL/min,以 2℃/min的升温速率加热两个瓷舟,待其升到400℃维持4h后降温得到负载型ZnO/CuO/CeO2复配双功能催化吸附脱硫剂。
(2)负载型ZnO/CuO/CeO2复配双功能催化吸附脱硫剂的燃料脱硫新工艺:
按有机过氧化物和有机硫的摩尔比为10的比例将过氧苯甲酸加入汽油中混合,得到含 有机过氧化物的汽油;将上述汽油通过负载型ZnO/CuO/CeO2复配双功能催化吸附脱硫剂固 定床床层,进行室温下的催化氧化吸附耦合反应2h,从而实现燃料的反应性深度吸附脱硫; 将热氮气通过反应后的负载型ZnO/CuO/CeO2双功能催化吸附脱硫剂固定床床层进行油品 回收,后通空气对负载型ZnO/CuO/CeO2复配双功能催化吸附脱硫剂固定床床层在500℃下 进行热再生6h,催化吸附材料固定床床层即可循环使用。该工艺可将10ppmw-S的国V汽 油处理到1ppmw-S获国零硫汽油,处理量为30L/kg-催化吸附材料。
实施例5
(1)负载型ZnO/CuO/CeO2/Cr2O3双功能催化吸附脱硫剂的制备:
将ZnO/CuO/CeO2/Cr2O3的前驱体硝酸锌、硝酸铜、硝酸铈、硝酸铬前驱体1.0g溶于去离子水中,其中ZnO:CuO:CeO2:Cr2O3=5:1:1:1,按(ZnO/CuO/CeO2/Cr2O3)/载 体质量比为12wt.%的比例将ZnO/CuO/CeO2/Cr2O3的前驱体溶液均匀负载到纯硅分子筛载 体材料上,超声浸渍,充分混合;将混合物放入烘箱干燥,研磨,在空气的氛围中以1.5℃/min 的升温速率升至400℃下煅烧2h,便制得负载型ZnO/CuO/CeO2/Cr2O3双功能催化吸附脱 硫剂。
(2)负载型ZnO/CuO/CeO2/Cr2O3双功能催化吸附脱硫剂的燃料脱硫新工艺:
按有机过氧化物和有机硫的摩尔比为15的比例将过氧化氢异丙苯加入柴油中混合,得 到含有机过氧化物的柴油;将上述柴油通过负载型ZnO/CuO/CeO2/Cr2O3双功能催化吸附脱 硫剂固定床床层,进行室温下的催化氧化吸附耦合反应1h,从而实现燃料的反应性深度吸 附脱硫;将热氮气通过反应后的负载型ZnO/CuO/CeO2/Cr2O3双功能催化吸附脱硫剂固定床 床层进行油品回收,后通空气对负载型ZnO/CuO/CeO2/Cr2O3双功能催化吸附脱硫剂固定床 床层在400℃下进行热再生2h,催化吸附材料固定床床层即可循环使用。该工艺可将10 ppmw-S的国V柴油处理到1ppmw-S获零硫柴油,处理量为130L/kg-催化吸附材料。
实施例6
(1)负载型ZnO/CuO/CeO2/MoO3双功能催化吸附脱硫剂的制备:
将ZnO/CuO/CeO2/MoO3的前驱体硝酸锌、硝酸铜、硝酸铈、钼酸铵前驱体1.0g溶于去离子水中,其中ZnO:CuO:CeO2:MoO3=5:1:1:2,按(ZnO/CuO/CeO2/MoO3)/载 体质量比为12wt.%的比例将ZnO/CuO/CeO2/Cr2O3的前驱体溶液均匀负载到硅铝分子筛载 体材料上,超声浸渍,充分混合;将混合物放入烘箱干燥,研磨,在空气的氛围中以1.5℃/min 的升温速率升至400℃下煅烧2h,便制得负载型ZnO/CuO/CeO2/MoO3双功能催化吸附脱 硫剂。
(2)负载型ZnO/CuO/CeO2/MoO3双功能催化吸附脱硫剂的燃料脱硫新工艺:
按有机过氧化物和有机硫的摩尔比为9的比例将过氧化氢异丙苯加入柴油中混合,得 到含有机过氧化物的柴油;将上述柴油通过负载型ZnO/CuO/CeO2/MoO3双功能催化吸附脱 硫剂固定床床层,进行室温下的催化氧化吸附耦合反应1h,从而实现燃料的反应性深度吸 附脱硫;将热氮气通过反应后的负载型ZnO/CuO/CeO2/MoO3双功能催化吸附脱硫剂固定床 床层进行油品回收,后通空气对负载型ZnO/CuO/CeO2/MoO3双功能催化吸附脱硫剂固定床 床层在400℃下进行热再生2h,催化吸附材料固定床床层即可循环使用。该工艺可将50 ppmw-S的国V柴油处理到5ppmw-S获零硫柴油,处理量为50L/kg-催化吸附材料。
实施例7
本发明提出一种负载型金属氧化物双功能催化吸附脱硫的燃料脱硫方法,其孔隙结构、 燃油脱硫性能和再生性能如下:
(1)孔隙结构
采用美国Micromeritics ASAP 2010型比表面积和孔隙分布测试仪测试了本发明制备的 系列负载型金属氧化物双功能催化吸附脱硫的比表面积(SBET)、孔径分布(Poresize)和孔 容(VTotal),结果如表1所示。表1示出,其中实施例1-5负载型金属氧化物双功能催化吸 附材料的比表面积在100~800m2/g范围,孔径尺寸在1.5~10nm范围,孔容在0.2~0.8cm3/g 范围,其中对比例1-11是调整了样品中相应的变量对比,检测孔结构数据。
表1 本发明不同金属/Si摩尔比的金属-Si-O双功能催化吸附剂的孔结构参数
从上述表1的结果得知,实施例1和2和对比例1-3表明,采用本发明中金属氧化物和 载体的质量配比得到孔结构参数更优异;从实施例3-5与实施例1-2对比可以看出,采用本 发明的多元复配比的效果比单元要好;从实施例3-5与对比例4-11可以看出,采用多元复 配时,每种金属氧化物在本发明的合理配比下效果更优。
(2)燃油脱硫性能(超低硫燃油产率)的测定
应用ANTEK 9000系列硫氮元素分析仪检测燃油中总硫含量,仪器测量误差为<0.5ppmw-S,超 低硫燃油产率(L/kg-催化吸附材料)为负载型金属氧化物双功能催化吸附脱硫剂在1 ppmw-S时的透过吸附量。表2示出实施例应用负载型金属氧化物双功能催化吸附脱硫剂进 行反应性催化吸附耦合脱硫的吸附透过曲线。它显示,表2实施例1-5和对比例1-11的超 低硫燃油(<1ppmw-S)产率分别为L/kg-催化吸附材料。其中表3中是调整了有机过氧化 物与燃料中有机硫的比例以及脱硫剂与有机硫的比例,用以研究最有效率的脱硫参数。
表2
从上述表2可以看出,实施例1-6的脱硫吸附产率明显高于对比例1-3,从实施例3-6 与对比例4-13可以看出,采用多元复配时,每种金属氧化物在本发明的合理配比下效果脱 硫吸附产率更好。
表3
从表3结果可得知,从实施例1-6与对比例14-31可以看出,有机过氧化物与燃料中有 机硫的比例以及脱硫剂与有机硫的比例在本发明的合理配比下效果脱硫吸附产率更好。
(3)负载型金属氧化物双功能催化吸附脱硫剂循环再生性能的测定
将热氮气通过反应后的负载型金属氧化物双功能催化吸附脱硫剂床层进行油品回收, 后通空气对负载型金属氧化物双功能催化吸附脱硫剂床层在一定温度下进行热再生,催化 吸附材料床层即可循环使用。表4示出实施例1-6应用负载型金属氧化物双功能催化吸附脱 硫剂三次循环使用的超低硫燃油产率,效果见表4。它显示,负载型金属氧化物双功能催化 吸附脱硫剂可经过热空气氧化的方法完全再生循环使用。
表4
产率L/kg-催化吸附材料 | 再生后产率L/kg-催化吸附材料 | |
实施例1 | 80 | 79 |
实施例2 | 120 | 118 |
实施例3 | 150 | 150 |
实施例4 | 30 | 30 |
实施例5 | 130 | 128 |
实施例6 | 50 | 50 |
从表4结果可以看出,本发明制备的负载型金属氧化物双功能催化吸附脱硫剂在燃料 中脱硫方法中可以再生利用,再生后的效果几乎与原生相同,再生利用率达到98%以上。
根据上述说明书的揭示和教导,本发明所属领域的技术人员还可以对上述实施方式进 行变更和修改。因此,本发明并不局限于上面揭示和描述的具体实施方式,对发明的一些 修改和变更也应当落入本发明的权利要求的保护范围内。此外,尽管本说明书中使用了一 些特定的术语,但这些术语只是为了方便说明,并不对本发明构成任何限制。
Claims (9)
1.一种用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,将有机过氧化物加入含有机硫的燃料中混合,得到含有机过氧化物的燃料;将所述含有机过氧化物的燃料通过负载型金属氧化物双功能催化吸附脱硫剂的固定床床层,室温下进行催化氧化吸附耦合反应0.5~2 h,实现燃料的反应性深度吸附脱硫;
所述脱硫剂包括载体以及负载在载体上的金属氧化物,所述金属氧化物为ZnO、CuO、MoO3、CeO2、CrO3中的一种以上,所述脱硫剂中金属氧化物的质量百分数为5~15 wt.%。
2.根据权利要求1所述的用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,所述含有机硫的燃料为柴油或汽油;所述有机过氧化物为过氧化氢异丙苯、过氧苯甲酸或过氧化氢叔丁醇;所述有机过氧化物与燃料中有机硫的摩尔比为5~18:1。
3.根据权利要求1所述的用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,所述负载型金属氧化物双功能催化吸附脱硫剂的比表面积在100~800m2/g范围,孔径尺寸在1.5~10 nm范围,孔容在0.2~0.8 cm3/g范围。
4.根据权利要求1所述的用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,所述负载型金属氧化物双功能催化吸附脱硫剂的制备方法是将金属氧化物的前驱体负载在载体材料上,再将前驱体和载体的混合物通过煅烧得到所述的负载型金属氧化物双功能催化吸附脱硫剂,所述前驱体负载在载体材料上的方法包括浸渍法、机械混合法、溶胶凝胶法、气相沉积法、化学沉淀法;所述煅烧的方法是在空气氛围中以1-5℃/min升温速率升温至380-450℃,煅烧时间为3.5-5.5h。
5.根据权利要求4所述的用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,所述金属氧化物为ZnO和CuO两种复配,所述ZnO和CuO的质量比为:ZnO:CuO = 5-15:1-5。
6.根据权利要求4所述的用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,所述金属氧化物为ZnO、CuO和CeO2三种复配,所述ZnO、CuO和CeO2的质量比为:ZnO:CuO:CeO2 = 5-15:1-5:1-5。
7.根据权利要求4所述的用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,所述金属氧化物为ZnO、CuO、CeO2和CrO3四种复配,或ZnO、CuO、MoO3和CrO3四种复配,所述ZnO、CuO、CeO2和CrO3的质量比为:CrO3:MnO:ZnO:CeO2 = 5-15:1-5:1-5:1-5;或ZnO、CuO、MoO3和CrO3的质量比为:ZnO:CuO:MoO3:CrO3 = 5-15:1-5:1-5:1-5。
8.根据权利要求4所述的用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,所述ZnO的前驱体为硝酸锌;所述CuO的前驱体为硝酸铜或氯化铜;所述MoO3的前驱体为钼酸铵;所述CeO2的前驱体为硝酸铈、硝酸铈铵;所述CrO3的前驱体为硝酸铬或氯化铬;
所述载体材料为硅胶、硅铝分子筛、纯硅分子筛或氧化铝。
9.根据权利要求1所述的用负载型金属氧化物双功能催化吸附脱硫剂的燃料氧化脱硫方法,其特征在于,将已经吸附脱硫反应后的负载型金属氧化物双功能催化吸附脱硫剂固定床床层先通氮气热处理进行油品回收,后通空气对所述脱硫剂固定床床层进行热再生,脱硫剂固定床床层即可循环使用;所述热再生温度为300~650 ℃;再生时间为2~6 h。
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