CN114950088B - A device, usage method and application of electrochemical reduction technology coupled with gas-liquid separation membrane technology for resource-based treatment of nitrogen oxide waste gas - Google Patents
A device, usage method and application of electrochemical reduction technology coupled with gas-liquid separation membrane technology for resource-based treatment of nitrogen oxide waste gas Download PDFInfo
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- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims abstract description 246
- 239000012528 membrane Substances 0.000 title claims abstract description 70
- 239000007788 liquid Substances 0.000 title claims abstract description 55
- 238000005516 engineering process Methods 0.000 title claims abstract description 50
- 230000009467 reduction Effects 0.000 title claims abstract description 31
- 238000000926 separation method Methods 0.000 title claims abstract description 25
- 239000002912 waste gas Substances 0.000 title claims abstract description 23
- 238000000034 method Methods 0.000 title claims abstract description 18
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 234
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 118
- 239000007789 gas Substances 0.000 claims abstract description 104
- 238000009792 diffusion process Methods 0.000 claims abstract description 67
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- 238000004064 recycling Methods 0.000 claims abstract description 19
- 239000003011 anion exchange membrane Substances 0.000 claims abstract description 10
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 21
- 239000003546 flue gas Substances 0.000 claims description 21
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 claims description 14
- 239000010936 titanium Substances 0.000 claims description 14
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- 239000010949 copper Substances 0.000 claims description 9
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- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims description 8
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims description 8
- 230000002209 hydrophobic effect Effects 0.000 claims description 7
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 claims description 6
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical group [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 6
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 6
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- CJTCBBYSPFAVFL-UHFFFAOYSA-N iridium ruthenium Chemical compound [Ru].[Ir] CJTCBBYSPFAVFL-UHFFFAOYSA-N 0.000 claims description 5
- OTYBMLCTZGSZBG-UHFFFAOYSA-L potassium sulfate Chemical compound [K+].[K+].[O-]S([O-])(=O)=O OTYBMLCTZGSZBG-UHFFFAOYSA-L 0.000 claims description 5
- 229910052939 potassium sulfate Inorganic materials 0.000 claims description 5
- 235000011151 potassium sulphates Nutrition 0.000 claims description 5
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 4
- ZOKXTWBITQBERF-UHFFFAOYSA-N Molybdenum Chemical compound [Mo] ZOKXTWBITQBERF-UHFFFAOYSA-N 0.000 claims description 4
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 claims description 4
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 claims description 4
- 229910017052 cobalt Inorganic materials 0.000 claims description 4
- 239000010941 cobalt Substances 0.000 claims description 4
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims description 4
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 claims description 4
- 229910052737 gold Inorganic materials 0.000 claims description 4
- 239000010931 gold Substances 0.000 claims description 4
- 229910052741 iridium Inorganic materials 0.000 claims description 4
- GKOZUEZYRPOHIO-UHFFFAOYSA-N iridium atom Chemical compound [Ir] GKOZUEZYRPOHIO-UHFFFAOYSA-N 0.000 claims description 4
- 229910052742 iron Inorganic materials 0.000 claims description 4
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 claims description 4
- 229910052750 molybdenum Inorganic materials 0.000 claims description 4
- 239000011733 molybdenum Substances 0.000 claims description 4
- 229910052759 nickel Inorganic materials 0.000 claims description 4
- 229910052762 osmium Inorganic materials 0.000 claims description 4
- SYQBFIAQOQZEGI-UHFFFAOYSA-N osmium atom Chemical compound [Os] SYQBFIAQOQZEGI-UHFFFAOYSA-N 0.000 claims description 4
- 229910052763 palladium Inorganic materials 0.000 claims description 4
- 229910052697 platinum Inorganic materials 0.000 claims description 4
- 229910052703 rhodium Inorganic materials 0.000 claims description 4
- 239000010948 rhodium Substances 0.000 claims description 4
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims description 4
- 229910052707 ruthenium Inorganic materials 0.000 claims description 4
- 229910052709 silver Inorganic materials 0.000 claims description 4
- 239000004332 silver Substances 0.000 claims description 4
- 229910052723 transition metal Inorganic materials 0.000 claims description 4
- 150000003624 transition metals Chemical class 0.000 claims description 4
- 239000004743 Polypropylene Substances 0.000 claims description 3
- 229920001155 polypropylene Polymers 0.000 claims description 3
- 239000004810 polytetrafluoroethylene Substances 0.000 claims description 3
- 229920001343 polytetrafluoroethylene Polymers 0.000 claims description 3
- 239000004800 polyvinyl chloride Substances 0.000 claims description 3
- 229920000915 polyvinyl chloride Polymers 0.000 claims description 3
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 2
- 239000011248 coating agent Substances 0.000 claims description 2
- 238000000576 coating method Methods 0.000 claims description 2
- 229910017604 nitric acid Inorganic materials 0.000 claims description 2
- 239000011148 porous material Substances 0.000 claims description 2
- 229910052938 sodium sulfate Inorganic materials 0.000 claims description 2
- 235000011152 sodium sulphate Nutrition 0.000 claims description 2
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims 1
- 239000011734 sodium Substances 0.000 claims 1
- 125000000391 vinyl group Chemical group [H]C([*])=C([H])[H] 0.000 claims 1
- 229920002554 vinyl polymer Polymers 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 7
- 238000005265 energy consumption Methods 0.000 abstract description 6
- 238000006722 reduction reaction Methods 0.000 description 19
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 13
- 239000003344 environmental pollutant Substances 0.000 description 12
- 231100000719 pollutant Toxicity 0.000 description 12
- 238000006243 chemical reaction Methods 0.000 description 10
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 8
- 238000010586 diagram Methods 0.000 description 6
- 238000004519 manufacturing process Methods 0.000 description 6
- 229910052751 metal Inorganic materials 0.000 description 6
- 239000002184 metal Substances 0.000 description 6
- 229910052757 nitrogen Inorganic materials 0.000 description 6
- 230000003197 catalytic effect Effects 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
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- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 2
- 238000003917 TEM image Methods 0.000 description 2
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- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 238000003916 acid precipitation Methods 0.000 description 1
- 239000004480 active ingredient Substances 0.000 description 1
- 239000013543 active substance Substances 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 238000010531 catalytic reduction reaction Methods 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 230000008094 contradictory effect Effects 0.000 description 1
- ORTQZVOHEJQUHG-UHFFFAOYSA-L copper(II) chloride Chemical compound Cl[Cu]Cl ORTQZVOHEJQUHG-UHFFFAOYSA-L 0.000 description 1
- YDRFJPRPCBJKCM-UHFFFAOYSA-L dichlorocopper ethanol Chemical compound C(C)O.[Cu](Cl)Cl YDRFJPRPCBJKCM-UHFFFAOYSA-L 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- 239000011810 insulating material Substances 0.000 description 1
- 238000004172 nitrogen cycle Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 235000011118 potassium hydroxide Nutrition 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
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- 235000011121 sodium hydroxide Nutrition 0.000 description 1
- 229910001415 sodium ion Inorganic materials 0.000 description 1
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Classifications
-
- 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
- B01D53/32—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 by electrical effects other than those provided for in group B01D61/00
- B01D53/326—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 by electrical effects other than those provided for in group B01D61/00 in electrochemical cells
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/40—Nitrogen compounds
- B01D2257/402—Dinitrogen oxide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/40—Nitrogen compounds
- B01D2257/404—Nitrogen oxides other than dinitrogen oxide
-
- 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
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- Chemical & Material Sciences (AREA)
- Electrochemistry (AREA)
- Engineering & Computer Science (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
- Treating Waste Gases (AREA)
Abstract
Description
技术领域Technical field
本发明涉及一种废气处理装置,具体涉及一种电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置、使用方法和应用。The present invention relates to an exhaust gas treatment device, and specifically relates to a device, usage method and application for recycling nitrogen oxide exhaust gas using electrochemical reduction technology coupled with gas-liquid separation membrane technology.
背景技术Background technique
在中国,氮氧化物污染物主要来源于有色冶炼和火电行业的烟气排放,是引起光化学烟雾、酸雨和温室效应等环境问题的重要前体物之一,其大量排放已经严重威胁到自然界氮循环和人类生命安全。目前,传统选择性催化还原技术能实现氮氧化物到氮气的无害化处理,但存在能耗巨大和次生污染等问题,应用范围受到限制。更为重要的是,从自然界氮循环角度而言,烟气中氮氧化物也是一种氮资源。相比于将氮氧化物转化为氮气的策略,氮氧化物到高附加值氨的选择性转化以及氨回收的策略更符合国家“废物资源化”战略需求,在实际应用中有着重要意义。In China, nitrogen oxide pollutants mainly come from flue gas emissions from non-ferrous smelting and thermal power industries. They are one of the important precursors that cause environmental problems such as photochemical smog, acid rain and greenhouse effects. Their large emissions have seriously threatened natural nitrogen. Circulation and safety of human life. At present, traditional selective catalytic reduction technology can realize the harmless treatment of nitrogen oxides to nitrogen, but it has problems such as huge energy consumption and secondary pollution, and its application scope is limited. More importantly, from the perspective of natural nitrogen cycle, nitrogen oxides in flue gas are also a nitrogen resource. Compared with the strategy of converting nitrogen oxides into nitrogen gas, the selective conversion of nitrogen oxides into high value-added ammonia and the strategy of ammonia recovery are more in line with the national "waste resource utilization" strategic needs and are of great significance in practical applications.
相比于传统方法,电化学还原技术具有操作简单、可控性强、经济适用、反应条件温和等优势,有望实现氮氧化物到氨的选择性转化。然而,电化学还原技术面临着电极活性和选择性低的难题,应用范围暂时受到限制。另外,将氮氧化物转化的氨富集和回收是氮氧化物资源化的重要环节。在实际的电化学还原氮氧化物过程中,溶液共存阴/阳离子(氯离子、硫酸根离子和钠离子)会干扰氨的选择性回收。目前工业上的蒸氨-吹脱法存在能耗大,溶液中的氨不能完全释放,氨回收率较低(<60%)等问题。Compared with traditional methods, electrochemical reduction technology has the advantages of simple operation, strong controllability, economical applicability, and mild reaction conditions, and is expected to realize the selective conversion of nitrogen oxides to ammonia. However, electrochemical reduction technology faces the problem of low electrode activity and selectivity, and its application scope is temporarily limited. In addition, the enrichment and recovery of ammonia converted from nitrogen oxides is an important link in the resource utilization of nitrogen oxides. In the actual electrochemical reduction of nitrogen oxides, the coexistence of anions/cations (chloride ions, sulfate ions, and sodium ions) in the solution will interfere with the selective recovery of ammonia. The current industrial ammonia steaming-stripping method has problems such as high energy consumption, incomplete release of ammonia in the solution, and low ammonia recovery rate (<60%).
发明内容Contents of the invention
本发明的目的就是为了解决上述问题至少其一而提供一种电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置、使用方法和应用,实现了有效处理氮氧化物污染物,同时实现氮氧化物的资源化利用。The purpose of the present invention is to solve at least one of the above problems and provide an electrochemical reduction technology coupled with gas-liquid separation membrane technology resource-based treatment of nitrogen oxide exhaust gas device, use method and application, achieving effective treatment of nitrogen oxide pollutants , while realizing resource utilization of nitrogen oxides.
本发明的目的通过以下技术方案实现:The object of the present invention is achieved through the following technical solutions:
本发明第一方面公开了一种电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置,包括由阴极气室、气体扩散阴极、阴极液室、阴离子交换膜、气体扩散阳极以及阳极液室依次贴合而成的电化学反应器和与阴极液室通过输送管道相连通的氨回收装置;The first aspect of the present invention discloses a device for resource-based treatment of nitrogen oxide waste gas using electrochemical reduction technology coupled with gas-liquid separation membrane technology, including a cathode gas chamber, a gas diffusion cathode, a cathode liquid chamber, an anion exchange membrane, and a gas diffusion anode. and an electrochemical reactor formed by sequentially fitting the anolyte chambers and an ammonia recovery device connected to the catholyte chamber through a transportation pipeline;
所述的电化学反应器还包括与阴极气室相连通的进气系统、与阳极液室相连通的电解液进液系统以及分别与气体扩散阴极和气体扩散阳极相连接的电源;The electrochemical reactor also includes an air inlet system connected to the cathode gas chamber, an electrolyte inlet system connected to the anolyte chamber, and a power supply connected to the gas diffusion cathode and the gas diffusion anode respectively;
所述的氨回收装置内设有中空纤维膜,所述的中空纤维膜一侧通过由阴极液室输入的电解液,另一侧通过吸收液;The ammonia recovery device is provided with a hollow fiber membrane, one side of the hollow fiber membrane passes the electrolyte input from the catholyte chamber, and the other side passes the absorption liquid;
所述的电化学反应器将烟气中的氮氧化物转化为氨,氨随阴极液室的电解液经输送管道输入氨回收装置内部,并透过中空纤维膜进入吸收液后随吸收液离开氨回收装置,剩余的电解液输回阴极液室。The electrochemical reactor converts nitrogen oxides in the flue gas into ammonia. The ammonia is input into the ammonia recovery device along with the electrolyte in the catholyte chamber through the transportation pipeline, and enters the absorption liquid through the hollow fiber membrane and then leaves with the absorption liquid. Ammonia recovery device, the remaining electrolyte is returned to the catholyte chamber.
优选地,所述的气体扩散阴极以泡沫钛为基底,表面负载过渡金属单原子或纳米团簇活性物质;所述的气体扩散阴极的孔径为50-100μm。Preferably, the gas diffusion cathode is based on titanium foam, and the surface is loaded with transition metal single atoms or nanocluster active materials; the pore diameter of the gas diffusion cathode is 50-100 μm.
优选地,所述的过渡金属单原子或纳米团簇活性物质包括锰、铁、钴、镍、铜、钼、钌、铑、钯、银、锇、铱、铂和金中的一种或多种,质量负载量为0.01-20%。Preferably, the transition metal single atom or nanocluster active material includes one or more of manganese, iron, cobalt, nickel, copper, molybdenum, ruthenium, rhodium, palladium, silver, osmium, iridium, platinum and gold. species, the mass loading is 0.01-20%.
优选地,所述的电解液为氢氧化钠、氢氧化钾、硫酸钠和硫酸钾中的一种或多种,浓度为0.1-5mol/L;所述的吸收液为硫酸、硝酸和盐酸中的一种或多种,浓度为0.1-5mol/L。Preferably, the electrolyte is one or more of sodium hydroxide, potassium hydroxide, sodium sulfate and potassium sulfate, with a concentration of 0.1-5mol/L; the absorption solution is sulfuric acid, nitric acid and hydrochloric acid. One or more, the concentration is 0.1-5mol/L.
优选地,所述的气体扩散阳极为钌铱涂层钛电极,涂层厚度为8-15μm。Preferably, the gas diffusion anode is a ruthenium-iridium coated titanium electrode, and the coating thickness is 8-15 μm.
优选地,所述的中空纤维膜为疏水性多孔膜,膜管内径为100μm-1mm,膜管厚度为100μm-1mm。Preferably, the hollow fiber membrane is a hydrophobic porous membrane, the inner diameter of the membrane tube is 100 μm-1mm, and the thickness of the membrane tube is 100 μm-1mm.
优选地,所述的中空纤维膜包括聚丙烯纤维膜、聚四氟乙烯纤维膜或聚氯乙烯中空纤维膜。Preferably, the hollow fiber membrane includes polypropylene fiber membrane, polytetrafluoroethylene fiber membrane or polyvinyl chloride hollow fiber membrane.
优选地,所述的电化学反应器和氨回收装置串联工作,实现氮氧化物选择性电化学转化为氨和氨同步回收;所述的阳极液室和阴极液室均为绝缘材料构成,与电极和阴离子交换膜紧密贴合,确保装置密封效果无泄漏;所述的自动电解液进液系统和进气系统由增压控制器和流量控制器构成,稳定控制废气和电解液进入和排出的流速。Preferably, the electrochemical reactor and the ammonia recovery device work in series to achieve selective electrochemical conversion of nitrogen oxides into ammonia and simultaneous recovery of ammonia; the anolyte chamber and the catholyte chamber are both made of insulating materials, and are The electrodes and the anion exchange membrane are closely fitted to ensure that the sealing effect of the device is leak-free; the automatic electrolyte liquid inlet system and the air inlet system are composed of a booster controller and a flow controller to stably control the entry and discharge of waste gas and electrolyte. flow rate.
本发明第二方面公开了一种如上任一所述的电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置的使用方法,在电化学反应器的气体扩散阴极和气体扩散阳极间施加电压,由进气系统进入的烟气经电化学还原形成氨,氨随阴极液室内的电解液流入氨回收装置的中空纤维膜,并透过中空纤维膜随吸收液流出氨回收装置,剩余的电解液流回阴极液室。The second aspect of the present invention discloses a method of using a device for recycling nitrogen oxide waste gas using electrochemical reduction technology coupled with gas-liquid separation membrane technology as described in any one of the above, in the gas diffusion cathode and gas diffusion of the electrochemical reactor A voltage is applied between the anodes, and the flue gas entering from the air intake system is electrochemically reduced to form ammonia. The ammonia flows into the hollow fiber membrane of the ammonia recovery device with the electrolyte in the catholyte chamber, and flows out of the ammonia recovery device through the hollow fiber membrane along with the absorption liquid. , the remaining electrolyte flows back to the catholyte chamber.
优选地,所述的电压为0.5-36V的直流电压;所述的烟气的流速为0.001-10m/s;所述的电解液的流速为1-500mL/min;所述的吸收液的流速为1-500mL/min。Preferably, the voltage is a DC voltage of 0.5-36V; the flow rate of the flue gas is 0.001-10m/s; the flow rate of the electrolyte is 1-500mL/min; the flow rate of the absorption liquid is 1-500mL/min.
本发明第三方面公开了一种如上任一所述的电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置在氮氧化物废气处理上的应用。The third aspect of the present invention discloses the application of a device for recycling nitrogen oxide exhaust gas using electrochemical reduction technology coupled with gas-liquid separation membrane technology as described in any one of the above in the treatment of nitrogen oxide exhaust gas.
与现有技术相比,本发明具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:
1、本发明的技术方案,由于阴极采用负载金属单原子或纳米团簇的多孔气体扩散电极,能够在气液固三相界面处将氮氧化物选择性还原为氨,氨随阴极电解液进入氨回收装置中的中空纤维膜组件,随后利用中空纤维膜两侧的氨蒸发压差实现电解液中氨的高效分离,最终氨被氨回收装置中的酸液吸收。故,本发明中电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置能够实现氮氧化物到氨的选择性转化和氨同步回收,有利于实现氮氧化物污染物控制和资源化利用。并且泡沫钛基金属单原子或纳米团簇电极的活性较高,稳定性较好,有助于氮氧化物污染物转化为氨选择性的提高。并且疏水性中空纤维膜氨回收选择性较高,有助于氨回收率的提高。1. The technical solution of the present invention, because the cathode adopts a porous gas diffusion electrode loaded with metal single atoms or nanoclusters, can selectively reduce nitrogen oxides to ammonia at the gas-liquid-solid three-phase interface, and ammonia enters with the catholyte. The hollow fiber membrane module in the ammonia recovery device then uses the ammonia evaporation pressure difference on both sides of the hollow fiber membrane to achieve efficient separation of ammonia in the electrolyte. Finally, the ammonia is absorbed by the acid liquid in the ammonia recovery device. Therefore, the device of the present invention that uses electrochemical reduction technology coupled with gas-liquid separation membrane technology to resource-process nitrogen oxide waste gas can realize the selective conversion of nitrogen oxides into ammonia and the simultaneous recovery of ammonia, which is beneficial to the control and control of nitrogen oxide pollutants. Resource utilization. Moreover, foam titanium-based metal single atom or nanocluster electrodes have higher activity and better stability, which helps to improve the selectivity of converting nitrogen oxide pollutants into ammonia. Moreover, the hydrophobic hollow fiber membrane has high ammonia recovery selectivity, which helps to increase the ammonia recovery rate.
2、本发明提供的装置,能有效降低处理工业烟气中氮氧化物的能耗,而且电极性能高,可高效、高选择性转化氮氧化物为氨以及高效回收氮氧化物选择性转化所得氨,对于当今环境保护和废气资源化利用具有重要的意义,也具有重大的市场应用前景。2. The device provided by the present invention can effectively reduce the energy consumption of processing nitrogen oxides in industrial flue gas, and has high electrode performance. It can efficiently and highly selectively convert nitrogen oxides into ammonia and efficiently recover the proceeds from the selective conversion of nitrogen oxides. Ammonia is of great significance for today's environmental protection and waste gas resource utilization, and also has great market application prospects.
3、本发明利用电化学还原技术在气体扩散阴极三相界面处选择性转化氮氧化物为氨,随后氨随阴极电解液泵入氨回收装置并透过中空纤维膜被吸收液回收。利用本发明中的装置处理含氮氧化物废气,不仅能耗低,而且电极活性和选择性高,氮氧化物资源化处理效率高,无二次污染,适合工业化推广。3. The present invention uses electrochemical reduction technology to selectively convert nitrogen oxides into ammonia at the three-phase interface of the gas diffusion cathode. Then the ammonia is pumped into the ammonia recovery device with the catholyte and passes through the hollow fiber membrane to be recovered by the absorption liquid. The device in the present invention is used to treat waste gas containing nitrogen oxides, which not only has low energy consumption, but also has high electrode activity and selectivity, high nitrogen oxide resource treatment efficiency, no secondary pollution, and is suitable for industrial promotion.
附图说明Description of the drawings
图1为本发明的装置的结构示意图;Figure 1 is a schematic structural diagram of the device of the present invention;
图2为负载铜单原子的泡沫钛气体扩散电极实物图;Figure 2 is a physical diagram of a titanium foam gas diffusion electrode loaded with copper single atoms;
图3为负载铜单原子的泡沫钛气体扩散电极AC-TEM图像;Figure 3 is an AC-TEM image of a titanium foam gas diffusion electrode loaded with copper single atoms;
图4为负载铜单原子的泡沫钛气体扩散电极处理含氮氧化物模拟烟气的氨选择性和产氨速率图;Figure 4 shows the ammonia selectivity and ammonia production rate of the titanium foam gas diffusion electrode loaded with copper single atoms in the treatment of simulated flue gas containing nitrogen oxides;
图5为本发明的装置的回收氨选择性和效率图;Figure 5 is a diagram of ammonia recovery selectivity and efficiency of the device of the present invention;
图6为本发明的装置处理含不同氮氧化物浓度的模拟烟气的氨选择性和产氨速率图;Figure 6 is a diagram of the ammonia selectivity and ammonia production rate of the device of the present invention for processing simulated flue gas containing different nitrogen oxide concentrations;
图7为本发明的装置处理含5%二氧化硫和20%氮氧化物的模拟烟气的氨选择性和产氨速率图;Figure 7 is a diagram of the ammonia selectivity and ammonia production rate of the device of the present invention for processing simulated flue gas containing 5% sulfur dioxide and 20% nitrogen oxides;
图8为本发明的装置处理含5%二氧化硫和20%氮氧化物的模拟烟气的回收氨选择性和效率图;Figure 8 is a diagram showing the ammonia recovery selectivity and efficiency of the device of the present invention for processing simulated flue gas containing 5% sulfur dioxide and 20% nitrogen oxides;
图中:1-阴极气室;2-气体扩散阴极;3-阴极液室;4-阴离子交换膜;5-气体扩散阳极;6-阳极液室;7-氨回收装置;8-输送设备。In the picture: 1-cathode gas chamber; 2-gas diffusion cathode; 3-cathode liquid chamber; 4-anion exchange membrane; 5-gas diffusion anode; 6-anolyte liquid chamber; 7-ammonia recovery device; 8-transport equipment.
具体实施方式Detailed ways
下面结合附图和具体实施例对本发明进行详细说明。显然,所描述的实施例仅仅是本发明的一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The present invention will be described in detail below with reference to the accompanying drawings and specific embodiments. Obviously, the described embodiments are only some of the embodiments of the present invention, but not all of the embodiments. Based on the embodiments of the present invention, all other embodiments obtained by those of ordinary skill in the art without creative efforts fall within the scope of protection of the present invention.
另外,各个实施例之间的技术方案可以相互结合,但是必须是以本领域普通技术人员能够实现为基础,当技术方案的结合出现相互矛盾或无法实现时应当认为这种技术方案的结合不存在,也不在本发明要求的保护范围之内。In addition, the technical solutions in various embodiments can be combined with each other, but it must be based on the realization by those of ordinary skill in the art. When the combination of technical solutions is contradictory or cannot be realized, it should be considered that such a combination of technical solutions does not exist. , nor within the protection scope required by the present invention.
本发明一方面提供了一种电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置,用于氮氧化物污染物到氨的选择性转化和氨的同步回收,实现氮氧化物污染物的资源化利用。On the one hand, the present invention provides a device for recycling nitrogen oxide waste gas using electrochemical reduction technology coupled with gas-liquid separation membrane technology, which is used for the selective conversion of nitrogen oxide pollutants into ammonia and the simultaneous recovery of ammonia to achieve nitrogen oxidation. Resource utilization of chemical pollutants.
请参阅图1,在本发明电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置一实例中,氮氧化物污染物到氨的选择性转化和氨同步回收的串联装置包括电化学反应器和氨回收装置7,电化学反应器包括电源、阴极气室1、气体扩散阴极2、阴极液室3、阴离子交换膜4、气体扩散阳极5以及阳极液室6,气体扩散阴极2为负载活性物质的多孔泡沫钛电极,阴离子交换膜4设于阴极液室3和气体扩散阳极5之间,气体扩散阳极5为钌铱涂层钛电极,氨回收装置7为中空纤维膜组件。Please refer to Figure 1. In an example of a device for recycling nitrogen oxide waste gas using electrochemical reduction technology coupled with gas-liquid separation membrane technology according to the present invention, a series device for selective conversion of nitrogen oxide pollutants into ammonia and simultaneous recovery of ammonia includes Electrochemical reactor and ammonia recovery device 7. The electrochemical reactor includes a power supply, a cathode gas chamber 1, a gas diffusion cathode 2, a catholyte chamber 3, an anion exchange membrane 4, a gas diffusion anode 5 and an anolyte chamber 6. The gas diffusion cathode 2 is a porous titanium foam electrode loaded with active material. The anion exchange membrane 4 is located between the catholyte chamber 3 and the gas diffusion anode 5. The gas diffusion anode 5 is a ruthenium-iridium coated titanium electrode, and the ammonia recovery device 7 is a hollow fiber membrane module. .
本发明中电源采用直流电源,以负载金属单原子或纳米团簇的泡沫钛气体扩散电极为气体扩散阴极2,以钌铱涂层电极为气体扩散阳极5,阴极液室3和气体扩散阳极5之间放置阴离子交换膜4,并将阴极气室1、气体扩散阴极2、阴极液室3、阴离子交换膜4、气体扩散阳极5以及阳极液室6多层材料夹紧,阴极气室1和气体扩散阴极2之间设有气流通道,气体扩散阳极5和阳极液室6之间设有电解液通道,同时将气体扩散阴极2和气体扩散阳极5通过导线分别连接直流电源的负极和正极。以中空纤维膜组件为氨回收装置7,同时将阴极液室3和氨回收装置7通过管道串联连接。本发明中气体扩散阴极2采用采用负载金属单原子或纳米团簇的多孔气体扩散电极,能够在气液固三相界面处将氮氧化物选择性还原为氨。氨回收装置7采用中空纤维疏水膜并选用酸液作为吸收液,能够高效分离和回收随阴极电解液进入中空纤维膜组件中的氨。In the present invention, the power supply adopts a DC power supply, and a titanium foam gas diffusion electrode loaded with metal single atoms or nanoclusters is used as the gas diffusion cathode 2, a ruthenium-iridium coated electrode is used as the gas diffusion anode 5, the catholyte chamber 3 and the gas diffusion anode 5 Anion exchange membrane 4 is placed between them, and the multi-layer materials of cathode gas chamber 1, gas diffusion cathode 2, catholyte chamber 3, anion exchange membrane 4, gas diffusion anode 5 and anolyte chamber 6 are clamped, and the cathode gas chamber 1 and There is a gas flow channel between the gas diffusion cathode 2, and an electrolyte channel between the gas diffusion anode 5 and the anolyte chamber 6. At the same time, the gas diffusion cathode 2 and the gas diffusion anode 5 are connected to the negative electrode and the positive electrode of the DC power supply respectively through wires. The hollow fiber membrane module is used as the ammonia recovery device 7, and the catholyte chamber 3 and the ammonia recovery device 7 are connected in series through pipelines. The gas diffusion cathode 2 in the present invention adopts a porous gas diffusion electrode loaded with metal single atoms or nanoclusters, which can selectively reduce nitrogen oxides to ammonia at the gas-liquid-solid three-phase interface. The ammonia recovery device 7 adopts a hollow fiber hydrophobic membrane and uses acid liquid as the absorbing liquid, which can efficiently separate and recover ammonia that enters the hollow fiber membrane module with the catholyte.
因此,可以理解的,本发明的技术方案,由于气体扩散阴极2采用负载金属单原子或纳米团簇的多孔气体扩散电极,能够在气液固三相界面处将氮氧化物选择性还原为氨,氨随阴极电解液进入氨回收装置7中的中空纤维膜组件,随后利用中空纤维膜两侧的氨蒸发压差实现电解液中氨的高效分离,最终氨被氨回收装置7中的酸液吸收。故,本发明选择性还原氮氧化物为氨耦合氨回收的装置能够实现氮氧化物到氨的选择性转化和氨同步回收,有利于实现氮氧化物污染物控制和资源化利用。并且泡沫钛基金属单原子或纳米团簇电极的活性较高,稳定性较好,有助于氮氧化物污染物转化为氨选择性的提高。并且疏水性中空纤维膜氨回收选择性较高,有助于氨回收率的提高。Therefore, it can be understood that the technical solution of the present invention, because the gas diffusion cathode 2 adopts a porous gas diffusion electrode loaded with metal single atoms or nanoclusters, can selectively reduce nitrogen oxides to ammonia at the gas-liquid-solid three-phase interface. , ammonia enters the hollow fiber membrane module in the ammonia recovery device 7 with the catholyte, and then uses the ammonia evaporation pressure difference on both sides of the hollow fiber membrane to achieve efficient separation of ammonia in the electrolyte, and finally the ammonia is absorbed by the acid liquid in the ammonia recovery device 7 absorb. Therefore, the device of the present invention for selectively reducing nitrogen oxides to ammonia coupled with ammonia recovery can realize selective conversion of nitrogen oxides to ammonia and simultaneous recovery of ammonia, which is beneficial to the control and resource utilization of nitrogen oxide pollutants. Moreover, foam titanium-based metal single atom or nanocluster electrodes have higher activity and better stability, which helps to improve the selectivity of converting nitrogen oxide pollutants into ammonia. Moreover, the hydrophobic hollow fiber membrane has high ammonia recovery selectivity, which helps to increase the ammonia recovery rate.
需要说明的是,电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置还包括输送设备8和输送管道(包括输送烟气的输送管道,输送电解液的输送管道、输送吸收液的输送管道以及连通氨回收装置7和阴极液室3的输送管道),其中的输送管道与阴极气室1连通(进气系统),输送管道与阳极液室6连通(电解液进液系统),输送管道将阴极液室3和氨回收装置7连通,输送管道上均设置有输送设备8,输送设备8根据通过的流体可以选择为风机或气泵、水泵。It should be noted that the device for recycling nitrogen oxide exhaust gas using electrochemical reduction technology coupled with gas-liquid separation membrane technology also includes transportation equipment 8 and transportation pipelines (including transportation pipelines for transporting flue gas, transport pipelines for transporting electrolyte, transport and absorption liquid transportation pipeline and the transportation pipeline connecting the ammonia recovery device 7 and the cathode liquid chamber 3), the transportation pipeline is connected to the cathode gas chamber 1 (air inlet system), and the transportation pipeline is connected to the anolyte liquid chamber 6 (electrolyte liquid inlet system) ), the transport pipeline connects the catholyte chamber 3 and the ammonia recovery device 7, and the transport pipelines are equipped with transport equipment 8. The transport equipment 8 can be selected as a fan, air pump, or water pump according to the passing fluid.
可选地,气体扩散阴极2实现氮氧化物选择性还原为氨的活性成分为锰、铁、钴、镍、铜、钼、钌、铑、钯、银、锇、铱、铂、金单原子、纳米团簇的至少一种。锰、铁、钴、镍、铜、钼、钌、铑、钯、银、锇、铱、铂、金单原子、纳米团簇均可作为气体扩散阴极2实现氮氧化物选择性还原为氨的活性成分,在使用时可选用其中的一种或多种组合。Optionally, the active components of the gas diffusion cathode 2 to achieve selective reduction of nitrogen oxides to ammonia are single atoms of manganese, iron, cobalt, nickel, copper, molybdenum, ruthenium, rhodium, palladium, silver, osmium, iridium, platinum, and gold. , at least one type of nanocluster. Manganese, iron, cobalt, nickel, copper, molybdenum, ruthenium, rhodium, palladium, silver, osmium, iridium, platinum, gold single atoms, and nanoclusters can all be used as gas diffusion cathodes 2 to achieve selective reduction of nitrogen oxides to ammonia. Active ingredients, one or more combinations thereof can be selected during use.
可选地,氨回收装置7的中空纤维膜为聚丙烯纤维膜、聚四氟乙烯纤维膜、聚氯乙烯中空纤维膜等疏水性多孔膜的一种。在组装氨回收装置7时,疏水性多孔膜可选用这些物质的一种。Optionally, the hollow fiber membrane of the ammonia recovery device 7 is a type of hydrophobic porous membrane such as polypropylene fiber membrane, polytetrafluoroethylene fiber membrane, polyvinyl chloride hollow fiber membrane, etc. When assembling the ammonia recovery device 7, one of these substances can be used as the hydrophobic porous membrane.
可选地,气体扩散阴极2活性物质的负载量范围为0.01%-20%。比如活性物质的负载量为0.01%、0.1%、1%、5%、10%或20%。优选地,负载量为0.1%-1%,比如为0.1%、0.2%、0.4%、0.8%或1%。Optionally, the loading amount of the active material of the gas diffusion cathode 2 ranges from 0.01% to 20%. For example, the loading of active substance is 0.01%, 0.1%, 1%, 5%, 10% or 20%. Preferably, the loading is 0.1%-1%, such as 0.1%, 0.2%, 0.4%, 0.8% or 1%.
本发明另一方面提供了一种装置在处理含氮氧化物工业烟气上的应用。Another aspect of the present invention provides an application of a device in treating industrial flue gas containing nitrogen oxides.
本发明提供的装置,能有效降低处理工业烟气中氮氧化物的能耗,而且电极性能高,可高效、高选择性转化氮氧化物为氨以及高效回收氮氧化物选择性转化所得氨,对于当今环境保护和废气资源化利用具有重要的意义,也具有重大的市场应用前景。The device provided by the invention can effectively reduce the energy consumption for processing nitrogen oxides in industrial flue gas, and has high electrode performance. It can efficiently and highly selectively convert nitrogen oxides into ammonia and efficiently recover ammonia obtained by selective conversion of nitrogen oxides. It is of great significance for today's environmental protection and waste gas resource utilization, and also has great market application prospects.
本发明还提供了一种电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的使用方法,应用于如前所述一种电化学还原技术耦合气液分离膜技术资源化处理氮氧化物废气的装置,包括以下步骤:The present invention also provides a method for using electrochemical reduction technology coupled with gas-liquid separation membrane technology to resource-process nitrogen oxide waste gas, which is applied to the above-mentioned electrochemical reduction technology coupled with gas-liquid separation membrane technology to resource-process nitrogen. The device for oxide waste gas includes the following steps:
将含氮氧化物污染物的烟气通入阴极气室1内,将电解液通入阴极液室3和阳极液室6内,将吸收液通入氨回收装置7内,并在气体扩散阳极5和气体扩散阴极2之间施加0.5V-36V的直流电压。控制烟气流速范围为0.001m/s-10m/s,电解液和吸收液流速范围为1mL/min-500mL/min。The flue gas containing nitrogen oxide pollutants is passed into the cathode gas chamber 1, the electrolyte is passed into the catholyte chamber 3 and the anolyte chamber 6, the absorption liquid is passed into the ammonia recovery device 7, and the gas diffusion anode is A DC voltage of 0.5V-36V is applied between 5 and the gas diffusion cathode 2. The control flue gas flow rate range is 0.001m/s-10m/s, and the electrolyte and absorption liquid flow rate range is 1mL/min-500mL/min.
这里直流电压范围优选2V-5V,比如施加的电压为2V、3V、4V或5V。通过调节直流电压和气体流量使得氮氧化物污染物高选择性还原为氨。Here, the DC voltage range is preferably 2V-5V, for example, the applied voltage is 2V, 3V, 4V or 5V. By adjusting the DC voltage and gas flow, nitrogen oxide pollutants are highly selectively reduced to ammonia.
这里阴极电解液和吸收液的流速范围优选50-250mL/min,比如采用的流速为50mL/min、100mL/min、150mL/min、200mL/min或250mL/min。通过调节阴极电解液和吸收液的流速使得电化学反应器气体扩散阴极2所转换的氨在氨回收装置7中得以高效回收。Here, the flow rate range of the catholyte and absorption liquid is preferably 50-250 mL/min, for example, the flow rate used is 50 mL/min, 100 mL/min, 150 mL/min, 200 mL/min or 250 mL/min. By adjusting the flow rates of the catholyte and absorbing liquid, the ammonia converted by the gas diffusion cathode 2 of the electrochemical reactor can be efficiently recovered in the ammonia recovery device 7 .
以下通过具体实施例对本发明资源化处理氮氧化物废气的方法及其装置进行详细说明。The method and device for recycling nitrogen oxide exhaust gas according to the present invention will be described in detail below through specific examples.
实施例1Example 1
(1)气体扩散阴极2的制备:将20mg氯化铜溶解在5mL乙醇中,然后将氯化铜乙醇溶液喷涂到2cm(长)*2cm(宽)*0.68cm(厚)的多孔泡沫钛表面,最后在H2/Ar气氛下,400℃下煅烧得到铜单原子泡沫钛气体扩散阴极2。铜单原子的气体扩散阴极2的实物图和AC-TEM图像参见图2和图3。(1) Preparation of gas diffusion cathode 2: Dissolve 20mg copper chloride in 5mL ethanol, and then spray the copper chloride ethanol solution onto the surface of porous titanium foam of 2cm (length) * 2cm (width) * 0.68cm (thickness) , and finally calcined at 400°C in H 2 /Ar atmosphere to obtain copper single-atom foam titanium gas diffusion cathode 2. See Figures 2 and 3 for the physical picture and AC-TEM image of the copper single-atom gas diffusion cathode 2.
(2)电化学反应器和回收氨串联装置的组装:将步骤(1)制备的电极作为气体扩散阴极2,将铱钌涂层电极作为气体扩散阳极5,随后将阴极气室1、气体扩散阴极2、阴极液室3、阴离子交换膜4、气体扩散阳极5以及阳极液室6夹紧,阴极气室1和和气体扩散阴极2之间设有气流通道,阳极液室6和气体扩散阳极5之间设有电解液通道,同时将气体扩散阴极2和气体扩散阳极5通过导线分别连接直流电源的负极和正极,便可得到电化学反应器。用输送管道将基于中空纤维膜组件的氨回收装置7与电化学反应器阴极液室3连接便可得到电化学反应器和回收氨串联装置。(2) Assembly of the electrochemical reactor and ammonia recovery series device: use the electrode prepared in step (1) as the gas diffusion cathode 2, use the iridium-ruthenium coated electrode as the gas diffusion anode 5, and then use the cathode gas chamber 1 and the gas diffusion anode 5. The cathode 2, catholyte chamber 3, anion exchange membrane 4, gas diffusion anode 5 and anolyte chamber 6 are clamped. There is an air flow channel between the cathode gas chamber 1 and the gas diffusion cathode 2. The anolyte chamber 6 and the gas diffusion anode are There is an electrolyte channel between 5, and at the same time, the gas diffusion cathode 2 and the gas diffusion anode 5 are respectively connected to the negative electrode and the positive electrode of the DC power supply through wires to obtain an electrochemical reactor. The electrochemical reactor and the ammonia recovery device in series can be obtained by connecting the ammonia recovery device 7 based on the hollow fiber membrane module with the catholyte chamber 3 of the electrochemical reactor using a transportation pipeline.
(3)利用步骤(2)电化学反应器和回收氨串联装置处理氮氧化物污染物的方法,包括以下步骤:将含有氮氧化物的气体通入阴极气室1,氮氧化物的浓度为20%,以Ar气作为平衡气,总流量控制在100mL/min。通过输送设备8(水泵)将0.5mol/L的硫酸钾电解液持续通入阴极液室3和阳极液室6,流量为100mL/min。然后在气体扩散阴极2和气体扩散阳极5间施加直流电压,并检测阴极液室3电解液和氨回收装置7吸收液中的氨浓度,催化性能参见图4,回收效率和选择性参见图5。(3) A method for treating nitrogen oxide pollutants using an electrochemical reactor and an ammonia recovery series device in step (2), including the following steps: passing gas containing nitrogen oxides into the cathode gas chamber 1, and the concentration of nitrogen oxides is 20%, using Ar gas as the balance gas, and the total flow rate is controlled at 100 mL/min. The 0.5 mol/L potassium sulfate electrolyte is continuously passed into the catholyte chamber 3 and the anolyte chamber 6 through the conveying equipment 8 (water pump), with a flow rate of 100 mL/min. Then apply a DC voltage between the gas diffusion cathode 2 and the gas diffusion anode 5, and detect the ammonia concentration in the electrolyte in the catholyte chamber 3 and the absorption liquid of the ammonia recovery device 7. See Figure 4 for the catalytic performance, and see Figure 5 for the recovery efficiency and selectivity. .
由图4可知,在2-3V电压范围内,氮氧化物选择性还原为氨的法拉第效率均在90%以上,随着电压的升高,产氨速率逐步升高,最高可达1200mmol/h/cm,氮氧化物转化为氨的催化效率较高。由图5可知,在连续运行50小时内,串联装置的氨回收效率在90%以上,选择性接近100%。串联装置回收氨的效率和选择性较高。As can be seen from Figure 4, in the voltage range of 2-3V, the Faradaic efficiency of selective reduction of nitrogen oxides to ammonia is above 90%. As the voltage increases, the ammonia production rate gradually increases, up to 1200mmol/h. /cm, the catalytic efficiency of converting nitrogen oxides into ammonia is relatively high. It can be seen from Figure 5 that within 50 hours of continuous operation, the ammonia recovery efficiency of the series device is above 90%, and the selectivity is close to 100%. The efficiency and selectivity of ammonia recovery in series units are high.
实施例2Example 2
装置处理含不同氮氧化物浓度的模拟烟气的能力:采用实施例1组装的串联装置,将含有0%、1%、5%、10%、20%氮氧化物通入阴极气室,以Ar气作为平衡气,总流量控制在100mL/min。通过水泵将0.5mol/L的硫酸钾电解液持续通入阴极液室和阳极液室,流量为100mL/min。然后在阴极和阳极间施加3V的直流电压,并检测阴极液室电解液和氨回收装置吸收液中的氨浓度,催化性能参见图6。The ability of the device to process simulated flue gas containing different concentrations of nitrogen oxides: Use the series device assembled in Example 1 to pass nitrogen oxides containing 0%, 1%, 5%, 10%, and 20% into the cathode gas chamber to Ar gas was used as a balance gas, and the total flow rate was controlled at 100 mL/min. 0.5mol/L potassium sulfate electrolyte was continuously passed into the catholyte chamber and anolyte chamber through a water pump, with a flow rate of 100mL/min. Then apply a DC voltage of 3V between the cathode and anode, and detect the ammonia concentration in the electrolyte in the catholyte chamber and the absorption solution of the ammonia recovery device. See Figure 6 for the catalytic performance.
由图6可知,随着模拟烟气中氮氧化物浓度的升高,电极氮氧化物选择性还原为氨的法拉第效率均在90%以上,产氨速率逐步升高,装置对不同浓度氮氧化物的处理能力均较高。It can be seen from Figure 6 that as the concentration of nitrogen oxides in the simulated flue gas increases, the Faradaic efficiency of the selective reduction of nitrogen oxides to ammonia at the electrode is above 90%, the ammonia production rate gradually increases, and the device oxidizes nitrogen at different concentrations. The material processing capacity is higher.
实施例3Example 3
装置的抗干扰能力测试:采用实施例1组装的串联装置,将含有5%二氧化硫和20%氮氧化物通入阴极气室,以Ar气作为平衡气,总流量控制在100mL/min。通过水泵将0.5mol/L的硫酸钾电解液持续通入阴极液室和阳极液室,流量为100mL/min。然后在阴极和阳极间施加直流电压,并检测阴极液室电解液和氨回收装置吸收液中的氨浓度,催化性能参见图7,回收效率和选择性参见图8。Anti-interference ability test of the device: Using the series device assembled in Example 1, the cathode gas chamber containing 5% sulfur dioxide and 20% nitrogen oxide was passed into the cathode gas chamber, with Ar gas as the balance gas, and the total flow rate was controlled at 100 mL/min. 0.5mol/L potassium sulfate electrolyte was continuously passed into the catholyte chamber and anolyte chamber through a water pump, with a flow rate of 100mL/min. Then apply a DC voltage between the cathode and the anode, and detect the ammonia concentration in the electrolyte in the catholyte chamber and the absorption fluid of the ammonia recovery device. See Figure 7 for the catalytic performance, and Figure 8 for the recovery efficiency and selectivity.
由图7和图8可知,在2-3V电压范围内,模拟烟气中二氧化硫的存在对装置选择性转化氮氧化物为氨的法拉第效率和产氨速率以及装置氨回收效率和选择性的影响不大,装置的抗干扰能力良好。It can be seen from Figures 7 and 8 that in the voltage range of 2-3V, the impact of the presence of sulfur dioxide in the simulated flue gas on the Faradaic efficiency and ammonia production rate of the device for selectively converting nitrogen oxides into ammonia, as well as the ammonia recovery efficiency and selectivity of the device Not big, the anti-interference ability of the device is good.
上述的对实施例的描述是为便于该技术领域的普通技术人员能理解和使用发明。熟悉本领域技术的人员显然可以容易地对这些实施例做出各种修改,并把在此说明的一般原理应用到其他实施例中而不必经过创造性的劳动。因此,本发明不限于上述实施例,本领域技术人员根据本发明的揭示,不脱离本发明范畴所做出的改进和修改都应该在本发明的保护范围之内。The above description of the embodiments is to facilitate those of ordinary skill in the technical field to understand and use the invention. It is obvious that those skilled in the art can easily make various modifications to these embodiments and apply the general principles described herein to other embodiments without inventive efforts. Therefore, the present invention is not limited to the above embodiments. Based on the disclosure of the present invention, improvements and modifications made by those skilled in the art without departing from the scope of the present invention should be within the protection scope of the present invention.
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