CN108246298A - A kind of method of nano lamellar solid base removing carbonyl sulfur - Google Patents
A kind of method of nano lamellar solid base removing carbonyl sulfur Download PDFInfo
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- CN108246298A CN108246298A CN201810147532.6A CN201810147532A CN108246298A CN 108246298 A CN108246298 A CN 108246298A CN 201810147532 A CN201810147532 A CN 201810147532A CN 108246298 A CN108246298 A CN 108246298A
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- JJWKPURADFRFRB-UHFFFAOYSA-N carbonyl sulfide Chemical compound O=C=S JJWKPURADFRFRB-UHFFFAOYSA-N 0.000 title claims abstract description 63
- 239000007787 solid Substances 0.000 title claims abstract description 54
- 238000000034 method Methods 0.000 title claims abstract description 41
- 239000002585 base Substances 0.000 claims abstract description 46
- 239000007789 gas Substances 0.000 claims abstract description 31
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 22
- 238000006460 hydrolysis reaction Methods 0.000 claims abstract description 20
- 230000007062 hydrolysis Effects 0.000 claims abstract description 19
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims abstract description 16
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 9
- 238000011069 regeneration method Methods 0.000 claims abstract description 9
- 230000008929 regeneration Effects 0.000 claims abstract description 7
- 239000003513 alkali Substances 0.000 claims abstract description 6
- 230000003647 oxidation Effects 0.000 claims abstract description 6
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 claims abstract description 5
- 238000002360 preparation method Methods 0.000 claims abstract description 5
- 238000005406 washing Methods 0.000 claims abstract description 5
- 238000001035 drying Methods 0.000 claims abstract description 4
- 230000000694 effects Effects 0.000 claims abstract description 4
- 239000000126 substance Substances 0.000 claims abstract description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 3
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 3
- 239000001301 oxygen Substances 0.000 claims abstract description 3
- 239000005864 Sulphur Substances 0.000 claims abstract 5
- 230000002779 inactivation Effects 0.000 claims abstract 3
- 239000003317 industrial substance Substances 0.000 claims abstract 2
- 239000000463 material Substances 0.000 claims abstract 2
- 239000003054 catalyst Substances 0.000 claims description 23
- GDVKFRBCXAPAQJ-UHFFFAOYSA-A dialuminum;hexamagnesium;carbonate;hexadecahydroxide Chemical compound [OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[Mg+2].[Mg+2].[Mg+2].[Mg+2].[Mg+2].[Mg+2].[Al+3].[Al+3].[O-]C([O-])=O GDVKFRBCXAPAQJ-UHFFFAOYSA-A 0.000 claims description 18
- 229960001545 hydrotalcite Drugs 0.000 claims description 18
- 229910001701 hydrotalcite Inorganic materials 0.000 claims description 18
- 239000000243 solution Substances 0.000 claims description 17
- 239000008367 deionised water Substances 0.000 claims description 13
- 229910021641 deionized water Inorganic materials 0.000 claims description 13
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 10
- 239000002184 metal Substances 0.000 claims description 10
- 229910052751 metal Inorganic materials 0.000 claims description 9
- 239000011259 mixed solution Substances 0.000 claims description 9
- 239000012265 solid product Substances 0.000 claims description 6
- 238000003756 stirring Methods 0.000 claims description 5
- 230000015572 biosynthetic process Effects 0.000 claims description 4
- 238000005119 centrifugation Methods 0.000 claims description 4
- 229910044991 metal oxide Inorganic materials 0.000 claims description 4
- 150000004706 metal oxides Chemical class 0.000 claims description 4
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 claims description 4
- 238000003786 synthesis reaction Methods 0.000 claims description 4
- 238000002425 crystallisation Methods 0.000 claims description 3
- 238000001027 hydrothermal synthesis Methods 0.000 claims description 3
- 229910052802 copper Inorganic materials 0.000 claims description 2
- 229910052748 manganese Inorganic materials 0.000 claims description 2
- 229910052759 nickel Inorganic materials 0.000 claims description 2
- 229910000027 potassium carbonate Inorganic materials 0.000 claims description 2
- 229910052725 zinc Inorganic materials 0.000 claims description 2
- 239000002904 solvent Substances 0.000 claims 3
- 150000002739 metals Chemical class 0.000 claims 2
- 235000019441 ethanol Nutrition 0.000 claims 1
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 claims 1
- 229910052737 gold Inorganic materials 0.000 claims 1
- 239000010931 gold Substances 0.000 claims 1
- VCJMYUPGQJHHFU-UHFFFAOYSA-N iron(III) nitrate Inorganic materials [Fe+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O VCJMYUPGQJHHFU-UHFFFAOYSA-N 0.000 claims 1
- 229910052717 sulfur Inorganic materials 0.000 abstract description 12
- 239000011593 sulfur Substances 0.000 abstract description 12
- 239000006185 dispersion Substances 0.000 abstract description 3
- 239000013078 crystal Substances 0.000 abstract description 2
- 238000009826 distribution Methods 0.000 abstract description 2
- -1 Carbonyl sulfur Chemical compound 0.000 abstract 1
- 238000006243 chemical reaction Methods 0.000 description 12
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 7
- 239000002356 single layer Substances 0.000 description 7
- 238000006477 desulfuration reaction Methods 0.000 description 6
- 230000023556 desulfurization Effects 0.000 description 6
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- 125000001741 organic sulfur group Chemical group 0.000 description 6
- 238000010521 absorption reaction Methods 0.000 description 4
- 239000010949 copper Substances 0.000 description 4
- 239000011701 zinc Substances 0.000 description 4
- 239000013064 chemical raw material Substances 0.000 description 3
- 238000011156 evaluation Methods 0.000 description 3
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical class S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 2
- 229910016870 Fe(NO3)3-9H2O Inorganic materials 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 229910019427 Mg(NO3)2-6H2O Inorganic materials 0.000 description 2
- YTPLMLYBLZKORZ-UHFFFAOYSA-N Thiophene Chemical compound C=1C=CSC=1 YTPLMLYBLZKORZ-UHFFFAOYSA-N 0.000 description 2
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 description 2
- 230000008025 crystallization Effects 0.000 description 2
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 description 2
- 230000008676 import Effects 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- 229910002554 Fe(NO3)3·9H2O Inorganic materials 0.000 description 1
- 229910018590 Ni(NO3)2-6H2O Inorganic materials 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- 229910010413 TiO 2 Inorganic materials 0.000 description 1
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 229910000287 alkaline earth metal oxide Inorganic materials 0.000 description 1
- 150000001342 alkaline earth metals Chemical class 0.000 description 1
- 239000012670 alkaline solution Substances 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- QGJOPFRUJISHPQ-NJFSPNSNSA-N carbon disulfide-14c Chemical compound S=[14C]=S QGJOPFRUJISHPQ-NJFSPNSNSA-N 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 238000000975 co-precipitation Methods 0.000 description 1
- 239000003034 coal gas Substances 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 238000007598 dipping method Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 238000005470 impregnation Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000002052 molecular layer Substances 0.000 description 1
- 239000002808 molecular sieve Substances 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- PXHVJJICTQNCMI-UHFFFAOYSA-N nickel Substances [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 1
- 229910052755 nonmetal Inorganic materials 0.000 description 1
- 239000003209 petroleum derivative Substances 0.000 description 1
- 238000006552 photochemical reaction Methods 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 235000015320 potassium carbonate Nutrition 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 229910001404 rare earth metal oxide Inorganic materials 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000007086 side reaction Methods 0.000 description 1
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 1
- 239000011343 solid material Substances 0.000 description 1
- 230000019635 sulfation Effects 0.000 description 1
- 238000005670 sulfation reaction Methods 0.000 description 1
- 150000004763 sulfides Chemical class 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 229930192474 thiophene Natural products 0.000 description 1
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 description 1
- 239000011787 zinc oxide Substances 0.000 description 1
- 229910006299 γ-FeOOH Inorganic materials 0.000 description 1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/002—Mixed oxides other than spinels, e.g. perovskite
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8668—Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/76—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/78—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with alkali- or alkaline earth metals
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/76—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/80—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with zinc, cadmium or mercury
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/30—Sulfur compounds
- B01D2257/308—Carbonoxysulfide COS
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2523/00—Constitutive chemical elements of heterogeneous catalysts
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Abstract
Description
技术领域technical field
本发明涉及化工原料气或硫磺尾气脱除有机硫领域,具体涉及一种纳米层状固体碱脱除气体中羰基硫的方法。The invention relates to the field of removing organic sulfur from chemical raw material gas or sulfur tail gas, in particular to a method for removing carbonyl sulfide in gas with a nano-layered solid base.
背景技术Background technique
随着经济的快速发展,能源供需矛盾日益突出,科学合理利用高含硫能源受到了广泛的关注。在以煤、石油和天然气为原料制备的化工原料气和后续脱硫工序中硫磺尾气中含有大量的硫化物,主要分为有机硫和无机硫两大类,有机硫包含羰基硫、二硫化碳、噻吩、硫醇等,无机硫则主要是指硫化氢。其中羰基硫占有机硫总量的80-90%,它的存在不仅容易引起原料气体管道的腐烛,降低设备的使用寿命,而且还容易造成下游催化剂的中毒,增加生产的成本因此,羰基硫的脱除是原料气深度净化过程中要解决的主要问题此外,作为工业气体中的一种主要的有机硫,排入到大气中的羰基硫在经过一系列化学、光化学反应后会生成,造成环境污染,威胁人类的健康和福利。因此,羰基硫的脱除研究具有重要的环保意义。With the rapid development of the economy, the contradiction between energy supply and demand has become increasingly prominent, and the scientific and rational use of high-sulfur energy has received extensive attention. In the chemical raw material gas prepared from coal, petroleum and natural gas and in the subsequent desulfurization process, sulfur tail gas contains a large amount of sulfide, which is mainly divided into two categories: organic sulfur and inorganic sulfur. Organic sulfur includes carbonyl sulfide, carbon disulfide, thiophene, Mercaptans, etc., inorganic sulfur mainly refers to hydrogen sulfide. Among them, carbonyl sulfide accounts for 80-90% of the total organic sulfur. Its existence not only easily causes the corrosion of raw gas pipelines, reduces the service life of equipment, but also easily causes poisoning of downstream catalysts, increasing production costs. Therefore, carbonyl sulfide The removal of carbonyl sulfide is the main problem to be solved in the process of deep purification of raw material gas. In addition, as a major organic sulfur in industrial gases, carbonyl sulfide discharged into the atmosphere will be generated after a series of chemical and photochemical reactions, resulting in Environmental pollution threatens human health and welfare. Therefore, the research on the removal of carbonyl sulfide has important environmental significance.
目前常用的COS脱除方法包括还原法、水解法、吸收法、吸附法和氧化法等。还原法是用H2将COS还原成H2S,该法转化率高,但成本高并存在一定的副反应。吸收法是利用碱性的有机胺溶液吸收酸性的COS气体,该法吸收速度快、成本低廉,但脱硫选择性差、能耗高,主要适用于粗脱。吸附法是利用多孔性固体材料吸附低浓度COS,使其在固体表面富集而与其它组分分离的过程。常用的吸附剂包括活性炭、分子筛、氧化锌、氧化铁和氧化锰等。该法脱硫深度高、处理量大、但需频繁再生且再生条件较为苛刻。氧化法是将COS氧化生成其他易除去的硫化物再设法除去,流程较为复杂。The commonly used COS removal methods include reduction method, hydrolysis method, absorption method, adsorption method and oxidation method. The reduction method uses H 2 to reduce COS to H 2 S. This method has a high conversion rate, but the cost is high and there are certain side reactions. The absorption method is to use alkaline organic amine solution to absorb acidic COS gas. This method has fast absorption speed and low cost, but has poor desulfurization selectivity and high energy consumption, and is mainly suitable for coarse desulfurization. Adsorption method is the process of using porous solid material to adsorb low concentration COS, enriching it on the solid surface and separating it from other components. Commonly used adsorbents include activated carbon, molecular sieves, zinc oxide, iron oxide, and manganese oxide. This method has high desulfurization depth and large treatment capacity, but requires frequent regeneration and the regeneration conditions are relatively harsh. The oxidation method is to oxidize COS to generate other easily removable sulfides and then try to remove them. The process is relatively complicated.
水解法是先使COS与H2O反应,再设法脱除产生的H2S的技术。常用的COS水解催化剂包括以γ-Al2O3和TiO2为代表的金属氧化物基载体和以活性炭为代表的非金属氧化物基载体,具有常温活性高、使用温域宽、抗中毒性强、转化吸收有机硫效率高和节约能耗等优点。公开号为106031868 A的中国发明专利申请,该专利申请公开了一种用于羰基硫水解的催化剂及其制备方法及其应用,通过浸渍法制备出以活性氧化铝或氧化钛为载体,以碱金属、碱土金属或稀土金属氧化物为活性组分的羰基硫水解催化剂,该催化剂具有良好的气源适用性,抗硫酸盐化能力强,脱除效果好,但不适用于COS浓度较低的情况。公开号为101703928 A的中国发明专利申请,该专利申请公开了一种低温水解羰基硫炭基催化剂的制备方法,该法以活性炭为载体,经碱液处理及活化后,可脱除COS及其水解后产生的H2S,成本低廉,但仅适用于COS浓度较大的情况。公告号为104667926 B的中国发明专利,该专利公开了一种以改性γ-FeOOH为活性组分的低温羰基硫水解催化剂的制备方法,该催化剂通过共沉淀法制备得到,可适用于CO2浓度较高的情况,但催化活性还有待提高。The hydrolysis method is a technology that first reacts COS with H 2 O, and then tries to remove the generated H 2 S. Commonly used COS hydrolysis catalysts include metal oxide-based supports represented by γ-Al 2 O 3 and TiO 2 and non-metal oxide-based supports represented by activated carbon, which have high activity at room temperature, wide use temperature range, and anti-toxicity. Strong, high conversion and absorption efficiency of organic sulfur and energy saving. The Chinese invention patent application with publication number 106031868 A discloses a catalyst for the hydrolysis of carbonyl sulfide and its preparation method and application. It uses activated alumina or titanium oxide as a carrier and base Carbonyl sulfide hydrolysis catalyst with metal, alkaline earth metal or rare earth metal oxide as the active component. The catalyst has good gas source applicability, strong resistance to sulfation, and good removal effect, but it is not suitable for low COS concentration Happening. The Chinese invention patent application with the publication number 101703928 A discloses a method for preparing a carbon-based catalyst for low-temperature hydrolysis of carbonyl sulfide. This method uses activated carbon as a carrier, and after being treated with lye and activated, COS and its The H 2 S produced after hydrolysis is low in cost, but it is only applicable to the case of high COS concentration. The Chinese invention patent with the notification number 104667926 B discloses a method for preparing a low-temperature carbonyl sulfide hydrolysis catalyst with modified γ-FeOOH as the active component. The catalyst is prepared by co-precipitation and is applicable to CO 2 In the case of higher concentration, the catalytic activity still needs to be improved.
一般认为羰基硫水解反应的实质是碱催化反应,催化剂表面的碱性中心是COS水解活性中心。但以往的水解法很难做到精脱硫且工艺流程复杂。It is generally believed that the essence of the carbonyl sulfide hydrolysis reaction is a base-catalyzed reaction, and the basic center on the surface of the catalyst is the active center of COS hydrolysis. However, the previous hydrolysis method is difficult to achieve fine desulfurization and the process is complicated.
发明内容Contents of the invention
本发明的目的是提供一种纳米层状固体碱脱除气体中羰基硫的方法,这种纳米层状固体碱脱除气体中羰基硫的方法用于解决现有的水解法脱除COS的方法很难做到精脱硫,且工艺流程复杂的问题。The purpose of the present invention is to provide a method for removing carbonyl sulfide in gas with a nano-layered solid base, which is used to solve the existing method for removing COS by hydrolysis It is difficult to achieve fine desulfurization, and the process is complicated.
本发明解决其技术问题所采用的技术方案是:这种纳米层状固体碱脱除气体中羰基硫的方法:The technical solution adopted by the present invention to solve its technical problems is: the method for removing carbonyl sulfide in gas by this nano-layered solid base:
化工原料或硫磺尾气中羰基硫在纳米层状固体碱催化作用下,在温度为40oC-80oC、水和羰基硫摩尔比为1.1:1-2:1、含有COS的化工原料气空速为1.0-4000h-1的条件下,发生水解和氧化反应,COS水解后经水中溶解氧的氧化作用转化为硫单质和硫酸盐,实现COS的脱除,羰基硫脱除率达99.5%以上;失活后的纳米层状固体碱经碱液浸渍、洗涤、干燥和焙烧后再生,再生后的固体碱循环使用;Carbonyl sulfide in chemical raw materials or sulfur tail gas is catalyzed by nano-layered solid base, at a temperature of 40 o C-80 o C, the molar ratio of water and carbonyl sulfide is 1.1:1-2:1, and the chemical raw material gas containing COS Under the condition of space velocity of 1.0-4000h -1 , hydrolysis and oxidation reactions occur. After COS is hydrolyzed, it is converted into sulfur element and sulfate through the oxidation of dissolved oxygen in water, and the removal of COS is realized. The removal rate of carbonyl sulfide reaches 99.5%. Above; the deactivated nano-layered solid alkali is regenerated after lye impregnation, washing, drying and roasting, and the regenerated solid alkali is recycled;
纳米层状金属氧化物固体碱的制备方法为:配制Mg(NO3)2和Fe(NO3)3溶液,Mg(NO3)2和Fe(NO3)3溶液浓度为0.01mol/L-2.0mol/L,且Mg/Fe摩尔比为1:4-6:1,同时添加M(NO3)2进行金属掺杂,M为掺杂金属,M/Mg摩尔比为1:10-5:1,形成水滑石合成溶液,调整该溶液pH值至碱性,搅拌均匀后进行水热合成,得到的固体产物经洗涤、干燥后得到纳米级金属掺杂的MgFe单层状水滑石,焙烧后得到纳米层状固体碱。The preparation method of the nano-layered metal oxide solid base is: prepare Mg(NO 3 ) 2 and Fe(NO 3 ) 3 solutions, the concentration of Mg(NO 3 ) 2 and Fe(NO 3 ) 3 solutions is 0.01mol/L- 2.0mol/L, and Mg/Fe molar ratio is 1:4-6:1, at the same time add M(NO 3 ) 2 for metal doping, M is doping metal, M/Mg molar ratio is 1:10-5 : 1, forming a hydrotalcite synthetic solution, adjusting the pH value of the solution to alkalescence, carrying out hydrothermal synthesis after stirring, the obtained solid product is washed and dried to obtain nanoscale metal-doped MgFe monolayer hydrotalcite, roasting Afterwards, a nano-layered solid base is obtained.
上述方案中纳米级金属掺杂的MgFe单层状水滑石合成条件为:在100oC-280oC下晶化10h-36h,离心分离得到的固体产物用去离子水和乙醇洗涤3-5次,80oC-120 oC下干燥6h-24h,得到纳米级金属掺杂的MgFe单层状水滑石。The synthesis conditions of the nanoscale metal-doped MgFe single-layer hydrotalcite in the above scheme are: crystallization at 100 o C-280 o C for 10h-36h, and the solid product obtained by centrifugation is washed with deionized water and ethanol for 3-5 Once, dry at 80 o C-120 o C for 6h-24h to obtain nano-scale metal-doped MgFe single-layer hydrotalcite.
上述方案中掺杂金属M为Zn、Cu、Ni和Mn中的任意一种。In the above solution, the doping metal M is any one of Zn, Cu, Ni and Mn.
上述方案中纳米级金属掺杂的MgFe单层状水滑石在300oC-450oC焙烧3 h-12h得到纳米层状固体碱。In the above scheme, the nanoscale metal-doped MgFe single-layer hydrotalcite is calcined at 300 o C-450 o C for 3 h-12 h to obtain a nano-layered solid base.
上述方案中调整水滑石合成溶液pH值至碱性的方法为:采用0.1 mol/L-2 mol/LKOH溶液逐滴加入至水滑石合成溶液pH值为8.0-13.0。The method for adjusting the pH value of the hydrotalcite synthesis solution to alkaline in the above scheme is: add 0.1 mol/L-2 mol/L KOH solution dropwise until the pH value of the hydrotalcite synthesis solution is 8.0-13.0.
上述方案中纳米层状固体碱的再生方法为:将失活的纳米层状固体碱催化剂采用K2CO3,KOH中的一种或二者混合溶液在20oC-80 oC浸渍1h-24,经去离子水洗涤3-5次至中性,在120 oC干燥1h-24h,然后在300oC-450oC焙烧3h-12h,实现固体碱催化剂的再生,再生后的纳米层状固体碱循环使用。The regeneration method of the nano-layered solid base in the above scheme is: soak the deactivated nano-layered solid base catalyst in K 2 CO 3 , KOH or a mixed solution of the two at 20 o C-80 o C for 1h- 24. Wash with deionized water for 3-5 times until neutral, dry at 120 o C for 1h-24h, and then bake at 300oC - 450oC for 3h-12h to realize the regeneration of the solid alkali catalyst, and the regenerated nano-layer The solid base can be recycled.
本发明具有以下有益效果:The present invention has the following beneficial effects:
1、本发明采用水热合成法制备出金属掺杂MgFe纳米层状水滑石,焙烧后得到纳米层状氧化物固体碱,其晶体尺寸分布范围较窄,比表面积大,分散度高,制备过程简单,成本低廉。1. The present invention adopts hydrothermal synthesis to prepare metal-doped MgFe nano-layered hydrotalcite, and obtains nano-layered oxide solid base after roasting. The crystal size distribution range is narrow, the specific surface area is large, and the dispersion degree is high. The preparation process Simple and low cost.
2、本发明通过COS的水解和进一步氧化的协同作用,最终将COS转化为单质硫和硫酸盐而除去,具有较高的COS脱除率。2. The present invention finally converts COS into elemental sulfur and sulfate through the synergistic effect of COS hydrolysis and further oxidation, and has a high COS removal rate.
3、本发明由于硫单质和硫酸盐在催化剂表面的覆盖导致其失活,通过碱性溶液浸渍、洗涤、烘干和焙烧即可实现催化剂的再生,再生后的催化剂可循环使用。3. In the present invention, the surface of the catalyst is deactivated due to the coverage of the sulfur element and sulfate on the surface. The catalyst can be regenerated by dipping in alkaline solution, washing, drying and roasting, and the regenerated catalyst can be recycled.
4、本发明制备得到纳米层状固体碱,该固体碱具有较大的比表面积、分散度和碱性,将其用于催化COS水解,适用温度低,具有广阔的应用前景,拓展了COS水解催化剂范围。4. The present invention prepares a nano-layered solid base. The solid base has a large specific surface area, dispersion and alkalinity. It is used to catalyze the hydrolysis of COS. The applicable temperature is low and has broad application prospects. It expands the hydrolysis of COS catalyst range.
附图说明Description of drawings
图1为NiMgFe氧化物固体碱对COS脱除的评价结果;Fig. 1 is the evaluation result of COS removal by NiMgFe oxide solid base;
图2为ZnMgFe氧化物固体碱对COS脱除的评价结果;Fig. 2 is the evaluation result of COS removal by ZnMgFe oxide solid base;
图3为CuMgFe氧化物固体碱对COS脱除的评价结果。Figure 3 is the evaluation result of COS removal by CuMgFe oxide solid base.
具体实施方式Detailed ways
下面结合附图对本发明作进一步的说明:Below in conjunction with accompanying drawing, the present invention will be further described:
实施例1Example 1
称取4.096g Mg(NO3)2·6H2O、2.020g Fe(NO3)3·9H2O和1.163 g Ni(NO3)2·6H2O溶解于50 mL去离子水中并搅拌均匀,该混合溶液中nNi:nMg:nFe=4:16:5;逐滴加入1.0 mol/LKOH至溶液pH值为11,将搅拌均匀的混合溶液转移至反应釜中在150oC下晶化24h,反应结束后将离心分离得到的固体产物用去离子水和乙醇分别洗涤5次,在110oC下干燥12h,得到纳米级金属掺杂的NiMgFe单层状水滑石(其中Ni掺杂质量分数为26.1%)。将制得的水滑石在400 oC下焙烧8h得到纳米层状NiMgFe固体碱。Weigh 4.096g Mg(NO 3 ) 2 6H 2 O, 2.020g Fe(NO 3 ) 3 9H 2 O and 1.163 g Ni(NO 3 ) 2 6H 2 O in 50 mL deionized water and stir well , n Ni : n Mg : n Fe =4:16:5 in the mixed solution; 1.0 mol/L KOH was added dropwise until the pH value of the solution was 11, and the evenly stirred mixed solution was transferred to a reaction kettle at 150 o C After crystallization for 24 h, the centrifuged solid product was washed 5 times with deionized water and ethanol respectively, and dried at 110 o C for 12 h to obtain nanoscale metal-doped NiMgFe single-layer hydrotalcite (wherein Ni-doped The impurity mass fraction is 26.1%). The prepared hydrotalcite was calcined at 400 o C for 8 hours to obtain a nano-layered NiMgFe solid base.
在反应温度为50oC、水和羰基硫摩尔比为1.5:1、含284μg/g羰基硫的硫磺尾气的空速为1000 h-1的条件下进行反应,经检测进出口COS和H2S浓度COS脱除率见图1。The reaction was carried out under the conditions that the reaction temperature was 50 o C, the molar ratio of water and carbonyl sulfide was 1.5:1, and the space velocity of the sulfur tail gas containing 284 μg/g carbonyl sulfide was 1000 h -1 . The COS removal rate of S concentration is shown in Figure 1.
将失活的纳米层状NiMgFe固体碱催化剂在45oC下、在1 mol/L的KOH中的浸渍6h,经去离子水洗涤5次至中性后,在120oC干燥6h,然后在350oC下焙烧8h,固体碱催化剂即可得到再生。The deactivated nano-layered NiMgFe solid base catalyst was impregnated in 1 mol/L KOH at 45 o C for 6 h, washed 5 times with deionized water to neutrality, dried at 120 o C for 6 h, and then placed in After calcination at 350 o C for 8 hours, the solid base catalyst can be regenerated.
实施例2Example 2
称取10.24g Mg(NO3)2·6H2O、4.85g Fe(NO3)3·9H2O和2.38 g Zn(NO3)2·6H2O溶解于50 mL去离子水中并搅拌均匀,该混合溶液中nZn:nMg:nFe=2:10:3;逐滴加入0.5 mol/L KOH至溶液pH值为10.5,将搅拌均匀的混合溶液转移至反应釜中在180oC下晶化18h,反应结束后将离心分离得到的固体产物用去离子水和乙醇分别洗涤3次,在110oC下干燥24h,得到纳米级金属掺杂的ZnMgFe单层状水滑石(其中Zn的掺杂质量分数为24.2%)。将制得的水滑石在400oC下焙烧12 h得到纳米层状ZnMgFe固体碱。Weigh 10.24g Mg(NO 3 ) 2 6H 2 O, 4.85g Fe(NO 3 ) 3 9H 2 O and 2.38 g Zn(NO 3 ) 2 6H 2 O in 50 mL deionized water and stir well , n Zn : n Mg : n Fe =2:10:3 in the mixed solution; 0.5 mol/L KOH was added dropwise until the pH value of the solution was 10.5, and the evenly stirred mixed solution was transferred to a reaction kettle at 180 o C After the reaction was finished, the solid product obtained by centrifugation was washed three times with deionized water and ethanol, and dried at 110 o C for 24 hours to obtain nanoscale metal-doped ZnMgFe single-layer hydrotalcite (where Zn The doping mass fraction is 24.2%). The prepared hydrotalcite was calcined at 400 o C for 12 h to obtain a nano-layered ZnMgFe solid base.
在反应温度为45oC、水和羰基硫摩尔比为1.4:1、含284μg/g羰基硫的硫磺尾气在空速为2400h-1的条件下进行反应,经检测进出口COS和H2S浓度计算出COS脱除率见图2。The reaction temperature is 45 o C, the molar ratio of water and carbonyl sulfide is 1.4:1, and the sulfur tail gas containing 284 μg/g carbonyl sulfide is reacted under the condition of space velocity of 2400h -1 . The COS and H 2 S at the import and export The COS removal rate calculated from the concentration is shown in Figure 2.
将失活的纳米层状ZnMgFe氧化物固体碱催化剂在30oC下、在1mol/L的K2CO3中浸渍6h,经去离子水洗涤5次至中性后,在120oC干燥12h,然后在400oC下焙烧12h,固体碱催化剂得到再生。Immerse the deactivated nano-layered ZnMgFe oxide solid base catalyst in 1mol/L K2CO3 at 30 o C for 6 hours, wash it with deionized water for 5 times to neutrality, and dry it at 120 o C for 12 hours , and then roasted at 400 o C for 12h, the solid base catalyst was regenerated.
实施例3Example 3
称取20.48gMg(NO3)2·6H2O、12.12gFe(NO3)3·9H2O和2.416g Cu(NO3)2·3H2O溶解于100 mL去离子水中并搅拌均匀,该混合溶液中nCu:nMg:nFe=1:8:3;逐滴加入1 mol/L KOH和K2CO3混合溶液(其中KOH质量分数为50%)至溶液pH值为11,将搅拌均匀的混合溶液转移至反应釜中在220oC下晶化16h,反应结束后将离心分离得到的固体产物用去离子水和乙醇分别洗涤5次,在80oC下干燥24h,得到纳米级金属掺杂的CuMgFe单层状水滑石(其中Cu掺杂质量分数为15.1%)。将制得的水滑石在380oC下焙烧6h得到纳米层状CuMgFe固体碱。Weigh 20.48g of Mg(NO 3 ) 2 ·6H 2 O, 12.12g of Fe(NO 3 ) 3 ·9H 2 O and 2.416g of Cu(NO 3 ) 2 ·3H 2 O in 100 mL of deionized water and stir evenly. In the mixed solution, n Cu : n Mg : n Fe =1:8:3; add 1 mol/L KOH and K 2 CO 3 mixed solution (wherein the mass fraction of KOH is 50%) dropwise until the pH value of the solution is 11, and the The uniformly stirred mixed solution was transferred to a reaction kettle and crystallized at 220 o C for 16 h. After the reaction, the solid product obtained by centrifugation was washed with deionized water and ethanol for 5 times, and dried at 80 o C for 24 h to obtain nano Metal-doped CuMgFe single-layer hydrotalcite (in which Cu doping mass fraction is 15.1%). The prepared hydrotalcite was calcined at 380 o C for 6h to obtain a nano-layered CuMgFe solid base.
在反应温度为60oC、水和羰基硫摩尔比为1.2:1,含284μg/g羰基硫的硫磺尾气在空速为3200h-1的条件下进行反应,经检测进出口COS和H2S浓度计算出COS脱除率见图3。The reaction temperature is 60 o C, the molar ratio of water and carbonyl sulfide is 1.2:1, and the sulfur tail gas containing 284 μg/g carbonyl sulfide is reacted under the condition of space velocity of 3200h -1 . After testing the COS and H 2 S at the import and export The COS removal rate calculated from the concentration is shown in Figure 3.
将失活的纳米层状CuMgFe固体碱催化剂在50oC下、在2 mol/L的KOH中的浸渍12h,经去离子水洗涤5次至中性后,在120oC干燥12h,然后在400oC下焙烧6h,固体碱催化剂得到再生。The deactivated nano-layered CuMgFe solid base catalyst was impregnated in 2 mol/L KOH at 50 o C for 12 h, washed 5 times with deionized water to neutrality, dried at 120 o C for 12 h, and then placed in Calcined at 400 o C for 6h, the solid base catalyst was regenerated.
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