CN105749914B - A kind of method of symmetrical difunctional photochemical catalyst, dual chamber Photoreactor and photocatalytic reduction of carbon oxide - Google Patents
A kind of method of symmetrical difunctional photochemical catalyst, dual chamber Photoreactor and photocatalytic reduction of carbon oxide Download PDFInfo
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Abstract
本发明公开了一种对称双功能光催化剂及相应的双室光反应器,属于二氧化碳综合利用技术领域,其中对称双功能光催化剂包括双面TiO2纳米管阵列基底上沉积石墨烯中间电子传输层,再沉积窄禁带半导体纳米颗粒作为光敏化剂。本发明提供的对称光催化剂通过电子传输层和光敏剂组分的引入使三元复合光催化剂的光响应扩展到可见光区域,同时促进了光生电子‑空穴对的有效分离,增强了复合催化剂光催化还原CO2的能力;该双面对称三元复合催化剂在匹配双室光反应器后,使光催化水氧化和CO2还原反应分别在独立的区域进行,减少了逆反应的发生,进一步提高光催化CO2还原效率。
The invention discloses a symmetrical double-function photocatalyst and a corresponding double-chamber photoreactor, belonging to the technical field of comprehensive utilization of carbon dioxide, wherein the symmetrical double-functional photocatalyst includes a graphene intermediate electron transport layer deposited on a double-sided TiO2 nanotube array substrate , and then deposited narrow-bandgap semiconductor nanoparticles as photosensitizers. The symmetrical photocatalyst provided by the present invention expands the photoresponse of the ternary composite photocatalyst to the visible light region through the introduction of the electron transport layer and the photosensitizer component, and at the same time promotes the effective separation of photogenerated electron-hole pairs, and enhances the photosensitivity of the composite catalyst. The ability of catalytic reduction of CO 2 ; the double-sided symmetric ternary composite catalyst is matched with a dual-chamber photoreactor, so that the photocatalytic water oxidation and CO 2 reduction reactions are carried out in separate areas, reducing the occurrence of reverse reactions and further improving the photocatalytic performance. Catalytic CO2 reduction efficiency.
Description
技术领域technical field
本发明属于二氧化碳综合利用技术领域,特别涉及一种对称双功能光催化剂、双室光反应器及光催化还原二氧化碳的方法。The invention belongs to the technical field of comprehensive utilization of carbon dioxide, and in particular relates to a symmetrical double-function photocatalyst, a double-chamber photoreactor and a method for photocatalytically reducing carbon dioxide.
背景技术Background technique
能源短缺以及二氧化碳(CO2)引发的温室效应已经成为威胁社会发展和人们日常生活的主要问题,但同时,因为储量丰富的CO2本身也是一种重要的化工原料,如何高效广泛的将其转化利用对人们提出了挑战和机遇。然而,由于CO2本身化学性质稳定,需要额外的能源输入才能将其活化并转化为有用的化合物。太阳能是一种清洁、廉价、分布广泛的可再生能源,利用太阳能光催化技术将CO2还原为太阳能燃料,对于缓解能源短缺、改善生态环境都有十分重要的意义。Energy shortage and the greenhouse effect caused by carbon dioxide (CO 2 ) have become the main problems threatening social development and people's daily life, but at the same time, because the abundant CO 2 itself is also an important chemical raw material, how to convert it efficiently and extensively Utilization presents challenges and opportunities for people. However, since CO2 itself is chemically stable, additional energy input is required to activate and convert it into useful compounds. Solar energy is a clean, cheap, and widely distributed renewable energy. Using solar photocatalysis technology to reduce CO2 to solar fuel is of great significance for alleviating energy shortage and improving the ecological environment.
目前光催化还原CO2的研究主要集中于两个方面:光催化剂的构建和反应器的设计。在目前应用的光催化剂中,研究较为普遍的是粉末型催化剂。虽然粉末型催化剂制备方法简单,产品分散性好,但存在回收困难、产物不便分离、光生电荷易复合、光催化效率低等缺点。因此,对于粉体光催化剂的固定化及膜基催化剂的研究正成为热点。由于光电催化作用可以较大程度地提升CO2还原效率,因而被广泛研究。但光电催化技术最大的不足就是需要外加电能输入,这样就增加了总体能源耗费与设备成本。同时,在外电场作用下,膜电极本身也可能会引发副反应,对于催化剂的稳定性有较大影响。鉴于以上问题,寻求一类高效稳定的膜基光催化剂是影响光催化还原CO2技术能否工业化应用的关键。Current research on photocatalytic reduction of CO2 mainly focuses on two aspects: the construction of photocatalysts and the design of reactors. Among the currently applied photocatalysts, powder-type catalysts are more commonly studied. Although the preparation method of powder-type catalyst is simple and the product has good dispersibility, there are disadvantages such as difficult recovery, inconvenient separation of products, easy recombination of photogenerated charges, and low photocatalytic efficiency. Therefore, the research on immobilization of powder photocatalysts and film-based catalysts is becoming a hot spot. Photoelectrocatalysis has been widely studied because it can greatly enhance the CO2 reduction efficiency. However, the biggest shortcoming of photocatalytic technology is the need for external electric energy input, which increases the overall energy consumption and equipment cost. At the same time, under the action of an external electric field, the membrane electrode itself may also cause side reactions, which have a great impact on the stability of the catalyst. In view of the above problems, finding a kind of efficient and stable film-based photocatalyst is the key to the industrial application of photocatalytic CO2 reduction technology.
另一个影响光还原CO2技术的因素就是反应器的设计。高效的膜基光催化剂需要有针对其结构优化设计的光反应器的配合,这样形成的光催化体系才能最大限度发挥其还原CO2的能力。相对于传统的单室光催化反应器,双室反应器能够有效地使氧化还原产物独立产生,减少了逆反应及副反应的发生,提高了光催化CO2还原效率。目前,双室反应器多应用于光电催化体系,仅采用光催化过程实现CO2还原的专利报道还较少。中国专利CN103348039A公布了一种在双室反应器中光催化还原CO2的方法,以氮化物半导体叠层为阳极,铟或铟化物为阴极,由外接导线将两个单独的光化学电极连接。但在该发明中由于外接导线的存在,使整个装置结构复杂,而且由于导线电压降和热效应而使光转换效率降低。中国专利CN103898548A公布了一种利用石墨烯和TiO2纳米管光电催化还原的方法,以掺Pt石墨烯负载于泡沫镍上作为电阴极,TiO2纳米管阵列作为光阳极,并将其分别贴在Nafion质子交换膜的两侧制成催化剂电极,放置于双室反应器之间,同时在阴、阳极上外加电压进行光电催化还原CO2的应用。同样地在该发明中由于外加电路的存在,既使整个反应的能量输入的增加,又可能在电子传递过程中会产生能量的损耗。Another factor affecting the photoreduction of CO2 technology is the design of the reactor. High-efficiency film-based photocatalysts require the cooperation of photoreactors optimized for their structures, so that the formed photocatalytic system can maximize its ability to reduce CO 2 . Compared with the traditional single-chamber photocatalytic reactor, the double-chamber reactor can effectively generate redox products independently, reduce the occurrence of reverse reactions and side reactions, and improve the photocatalytic CO2 reduction efficiency. At present, dual-chamber reactors are mostly used in photocatalytic systems, and there are few patent reports on CO2 reduction using only photocatalytic processes. Chinese patent CN103348039A discloses a method for photocatalytic reduction of CO2 in a double-chamber reactor, using a nitride semiconductor stack as the anode, indium or indium compound as the cathode, and two separate photochemical electrodes are connected by external wires. However, in this invention, due to the existence of external wires, the structure of the entire device is complicated, and the light conversion efficiency is reduced due to the voltage drop of the wires and thermal effects. Chinese patent CN103898548A discloses a method for photocatalytic reduction using graphene and TiO2 nanotubes, in which Pt-doped graphene is loaded on nickel foam as an electric cathode, and the TiO2 nanotube array is used as a photoanode, and they are respectively pasted on The two sides of the Nafion proton exchange membrane are made of catalyst electrodes, which are placed between the double-chamber reactors. At the same time, an external voltage is applied to the cathode and anode for the application of photoelectric catalytic reduction of CO 2 . Also in this invention, due to the existence of the external circuit, even if the energy input of the whole reaction increases, energy loss may occur during the electron transfer process.
发明内容Contents of the invention
本发明的目的在于提供一种对称双功能光催化剂及相应的双室光反应器,提供光催化还原二氧化碳的方法则是本发明的另一个目的。The purpose of the present invention is to provide a symmetrical double-functional photocatalyst and a corresponding double-chamber photoreactor, and to provide a method for photocatalytic reduction of carbon dioxide is another purpose of the present invention.
基于上述目的,本发明采用如下技术方案:一种对称双功能光催化剂,包括由纯钛通过两步阳极氧化法制备得到双面TiO2纳米管阵列(TNA)膜基底,基底表面电沉积有石墨烯层,石墨烯层为电子传输层,通过调控电化学参数来改变石墨烯沉积层厚度,调控电子在复合对称双功能光催化剂中的传输,改善光电子-空穴对再复合几率;然后在石墨烯层上沉积窄禁带半导体纳米颗粒作为光敏化剂。Based on the above purpose, the present invention adopts the following technical scheme: a symmetrical bifunctional photocatalyst, including a double-sided TiO2 nanotube array (TNA) film substrate prepared from pure titanium by a two-step anodic oxidation method, and graphite is electrodeposited on the surface of the substrate Graphene layer, the graphene layer is the electron transport layer, by adjusting the electrochemical parameters to change the thickness of the graphene deposition layer, adjust the transmission of electrons in the composite symmetrical bifunctional photocatalyst, improve the recombination probability of photoelectron-hole pairs; Narrow bandgap semiconductor nanoparticles were deposited on the olefin layer as photosensitizers.
优选地,所述窄禁带半导体纳米颗粒为氧化亚铜、氧化铜、硫化镉、氧化锌、硫化铅、氧化铅中的一种或两种及以上的混合。Preferably, the narrow bandgap semiconductor nanoparticles are one or a mixture of two or more of cuprous oxide, copper oxide, cadmium sulfide, zinc oxide, lead sulfide, and lead oxide.
优选地,所述电沉积的方法为循环伏安法、恒电流沉积法或恒电位沉积法。Preferably, the electrodeposition method is cyclic voltammetry, constant current deposition or constant potential deposition.
优选地,在石墨烯层上沉积窄禁带半导体纳米颗粒的方法为电化学沉积、湿化学法沉积、水热法沉积、溶剂热法沉积或光化学法沉积。Preferably, the method for depositing narrow-bandgap semiconductor nanoparticles on the graphene layer is electrochemical deposition, wet chemical deposition, hydrothermal deposition, solvothermal deposition or photochemical deposition.
采用上述对称双功能光催化剂的双室光反应器,包括对称设置的阳极反应池和阴极反应池,阴极反应池和阳极反应池之间设有两个连接口,一个连接口中间固定设有Nafion质子交换膜,另一个连接口中间固定设有由对称双功能光催化剂制成的基片,阴极反应池和阳极反应池顶部均设有进气口和出气口,阳极反应池侧壁上设有光窗口。The dual-chamber photoreactor adopting the above-mentioned symmetrical bifunctional photocatalyst includes symmetrically arranged anode reaction cells and cathode reaction cells, two connection ports are arranged between the cathode reaction cell and the anode reaction cell, and a Nafion proton is fixed in the middle of a connection port The exchange membrane is fixed with a substrate made of symmetrical bifunctional photocatalyst in the middle of the other connection port, the top of the cathode reaction pool and the anode reaction pool are equipped with air inlets and outlets, and the side wall of the anode reaction pool is equipped with a light window.
进一步地,阳极反应池和阴极反应池中为水或电解质溶液,阳极反应池的电解质溶液为Na2SO4、NaCl、Na2SO3溶液中的一种或两种及以上的混合物;阴极反应池的电解质溶液为NaHCO3、Na2CO3、NaOH、KOH、K2CO3溶液中的一种或两种及以上的混合物。Further, the anode reaction pool and the cathode reaction pool are water or an electrolyte solution, and the electrolyte solution of the anode reaction pool is one or a mixture of two or more of Na 2 SO 4 , NaCl, and Na 2 SO 3 solutions; the cathode reaction The electrolyte solution of the cell is one or a mixture of two or more of NaHCO 3 , Na 2 CO 3 , NaOH, KOH, K 2 CO 3 solutions.
进一步地,阴极反应池的侧壁上设有取液口,通过取液口或出气口用气相色谱检测分析液相或者气相还原产物产率。Further, a liquid intake port is provided on the side wall of the cathode reaction cell, and the liquid or gas phase reduction product yield is detected and analyzed by gas chromatography through the liquid intake port or the gas outlet.
采用上述双室光反应器光催化还原二氧化碳的方法,包括以下步骤:在双室光反应器的阳极反应池和阴极反应池加入水或电解质溶液;将催化剂基片和Nafion质子交换膜分别夹持在反应器两个连接口上,使阳极反应池和阴极反应池直接互不相通,仅有质子可通过Nafion膜在两池间流动;光线由光窗口射入阳极反应池后直接照射在基片上,高纯N2、CO2气体分别通过进气口各自通入阳极反应池、阴极反应池的电解质溶液中,气相产物随载气由出气口排出反应器,形成一个连续进料、开放的光催化还原CO2反应体系;光源(包括紫外光、可见光或全光谱光源)激发基片上的光敏化剂在阳极面上产生光电子-空穴对,电子通过匹配的能级排列和电子传输层的作用向阴极面传递,空穴和电子分别迁移至光催化剂的阳极面和阴极面,在独立分离的反应池中参与水的光氧化和CO2的还原反应。The method for photocatalytic reduction of carbon dioxide using the above-mentioned dual-chamber photoreactor comprises the following steps: adding water or an electrolyte solution to the anode reaction cell and the cathode reaction cell of the dual-chamber photoreactor; clamping the catalyst substrate and the Nafion proton exchange membrane respectively On the two connection ports of the reactor, the anode reaction cell and the cathode reaction cell are not directly connected to each other, and only protons can flow between the two cells through the Nafion membrane; the light is injected into the anode reaction cell through the light window and directly irradiates on the substrate. High-purity N 2 and CO 2 gases are respectively passed into the electrolyte solution of the anode reaction cell and the cathode reaction cell through the inlet ports, and the gas phase products are discharged from the reactor through the gas outlet along with the carrier gas, forming a continuous feeding, open photocatalytic Reduction of CO 2 reaction system; light source (including ultraviolet light, visible light or full-spectrum light source) excites the photosensitizer on the substrate to generate photoelectron-hole pairs on the anode surface, and the electrons go to the On the cathode side, the holes and electrons migrate to the anode and cathode sides of the photocatalyst, respectively, and participate in the photooxidation of water and the reduction of CO2 in a separate reaction cell.
进一步地,CO2的还原产物为醇类、烃类、一氧化碳中的一种或两种及以上的混合物。Further, the CO 2 reduction product is one or a mixture of two or more of alcohols, hydrocarbons, and carbon monoxide.
本发明采用TiO2纳米管阵列(TNA)为基底,方便直接应用、回收和更换,通过引入电子传输层和光敏剂组分,使三元复合光催化剂的光响应扩展到可见光区域,同时促进了光生电子-空穴对的有效分离,增强了复合催化剂光催化还原CO2的能力;在匹配双室光催化反应器后使氧化还原反应分别在独立的区域进行,减少了逆反应的发生,进一步提高光催化CO2还原效率。另外,本发明不需外加电能输入,降低能源耗费。The present invention uses TiO2 nanotube array (TNA) as the substrate, which is convenient for direct application, recycling and replacement. By introducing the electron transport layer and photosensitizer components, the photoresponse of the ternary composite photocatalyst is extended to the visible light region, and at the same time it promotes The effective separation of photogenerated electron-hole pairs enhances the ability of the composite catalyst to photocatalytically reduce CO2 ; after matching the double-chamber photocatalytic reactor, the oxidation-reduction reactions are carried out in independent areas, which reduces the occurrence of reverse reactions and further improves Photocatalytic CO2 reduction efficiency. In addition, the present invention does not require external electric energy input, thereby reducing energy consumption.
同时,本发明采用双面对称双功能光催化剂直接作为双室光反应器的隔离膜,省去外电路连接,通过催化剂中多重异质结界面的形成,高效分离光生电荷,提高CO2的还原效率,采用这种体系进行光还原CO2的文献目前还未见报道。At the same time, the present invention uses a double-sided symmetric dual-function photocatalyst directly as the isolation film of the dual-chamber photoreactor, eliminating the need for external circuit connections, and efficiently separating photogenerated charges through the formation of multiple heterojunction interfaces in the catalyst to improve the reduction of CO2 Efficiency, the literature using this system for photoreduction of CO2 has not been reported yet.
附图说明Description of drawings
图1为对称双功能光催化剂的制备流程图;Fig. 1 is the preparation flowchart of symmetrical bifunctional photocatalyst;
图2为实施例1中制备样品的扫描电镜图,其中(a)为TNA的电镜扫描表面图;(b)为G/TNA的电镜扫描表面图;(c)为Cu2O/G/TNA的电镜扫描表面图;(d)为Cu2O/G/TNA的电镜扫描断面图;Figure 2 is the scanning electron microscope image of the sample prepared in Example 1, in which (a) is the electron microscope scanning surface image of TNA; (b) is the electron microscope scanning surface image of G/TNA; (c) is Cu 2 O/G/TNA SEM surface image of ; (d) SEM cross-sectional image of Cu 2 O/G/TNA;
图3为双室光催化反应器主视图;Fig. 3 is the front view of double-chamber photocatalytic reactor;
图4为双室光催化反应器的俯视图;Fig. 4 is the top view of double-chamber photocatalytic reactor;
图5是双室光催化反应器的左视图;Fig. 5 is the left side view of dual-chamber photocatalytic reactor;
图6为对称双功能光催化剂在双室光反应器中进行光催化还原CO2示意图;Figure 6 is a schematic diagram of the photocatalytic reduction of CO by a symmetrical bifunctional photocatalyst in a dual-chamber photoreactor;
图7为实施例1、6、7、8中制得的Cu2O/G/TNA、CdS/G/TNA、PbO2/G/TNA、ZnO/G/TNA在图3~5所示反应器中光催化还原CO2的甲醇产量。Fig. 7 is Cu 2 O/G/TNA, CdS/G/TNA, PbO 2 /G/TNA, ZnO/G/TNA prepared in embodiment 1, 6, 7, 8 in the reaction shown in Fig. 3 ~ 5 Methanol production from photocatalytic reduction of CO2 in a device.
具体实施方式Detailed ways
下面结合实施例对本发明做进一步的说明解释。Below in conjunction with embodiment the present invention is further described and explained.
实施例1Example 1
1. 对称双功能Cu2O/G/TNA膜光催化剂的制备1. Preparation of symmetrical bifunctional Cu 2 O/G/TNA film photocatalyst
一种对称双功能光催化剂,包括由纯钛通过两步阳极氧化法制备得到双面TiO2纳米管阵列(TNA)膜基底,基底表面电沉积有石墨烯层,通过调控电化学参数来改变石墨烯沉积层厚度,从而调控电子在复合对称双功能光催化剂中的传输,改善光电子-空穴对再复合几率;然后在石墨烯层上沉积窄禁带半导体纳米颗粒作为光敏化剂,其制备过程如图1所示,包括以下步骤:A symmetrical bifunctional photocatalyst, including a double-sided TiO 2 nanotube array (TNA) film substrate prepared from pure titanium by a two-step anodic oxidation method, and a graphene layer is electrodeposited on the surface of the substrate, and the graphite can be changed by adjusting the electrochemical parameters The thickness of the graphene deposition layer can be adjusted to regulate the transport of electrons in the compound symmetrical bifunctional photocatalyst and improve the recombination probability of photoelectron-hole pairs; As shown in Figure 1, the following steps are included:
(1)制备TNA膜基片:将纯钛箔经过物理打磨和超声清洗后,在化学酸洗液中浸泡进行化学抛光;然后将钛箔置于质量分数为0.25% NH4F的乙二醇-水混合溶液中,其中乙二醇与水体积比为49:1,采用三电极体系在同样条件下进行两次阳极氧化后,经去离子水清洗晾干,置于马弗炉中,空气氛围500 oC下焙烧2 h,最终得到双面对称TNA膜基片。其电镜扫描表面图如图2(a)所示,从图中可知,TNA膜基片表层形貌规整,孔径均一,底层为纳米管阵列,孔径约为30 nm,管长在500 nm左右;(1) Preparation of TNA film substrate: After physical grinding and ultrasonic cleaning, the pure titanium foil was soaked in chemical pickling solution for chemical polishing; then the titanium foil was placed in ethylene glycol with a mass fraction of 0.25% NH 4 F -In the water mixed solution, wherein the volume ratio of ethylene glycol to water is 49:1, after using the three-electrode system to carry out anodic oxidation twice under the same conditions, wash and dry with deionized water, place in a muffle furnace, and air Baking at 500 o C for 2 h, the double-sided symmetrical TNA film substrate was finally obtained. The surface image scanned by the electron microscope is shown in Figure 2(a). From the figure, it can be seen that the surface layer of the TNA membrane substrate has a regular appearance and uniform pore size, and the bottom layer is a nanotube array with a pore size of about 30 nm and a tube length of about 500 nm;
(2)制备G/TNA基片(沉积石墨烯):在以TNA膜基片作为工作电极的三电极体系中,采用循环伏安法在氧化石墨烯水分散液中将石墨烯片层沉积在TNA膜表面,扫描电压范围为-1.5~+1 V,扫描圈数为20圈,即得沉积有石墨烯的TNA膜基片(G/TNA)。其电镜扫描表面图如图2(b)所示,从图中可以看到明显的石墨烯特征褶皱结构及在其覆盖下的TNA表面形貌,由此证明一定厚度的薄层石墨烯被沉积到TNA表面;(2) Preparation of G/TNA substrate (deposited graphene): In a three-electrode system with TNA film substrate as the working electrode, graphene sheets were deposited on the graphene oxide aqueous dispersion by cyclic voltammetry. On the surface of the TNA film, the scanning voltage range is -1.5 to +1 V, and the number of scanning cycles is 20, that is, the TNA film substrate (G/TNA) deposited with graphene is obtained. Its electron microscope scanning surface image is shown in Figure 2(b). From the figure, it can be seen that the characteristic folded structure of graphene and the surface morphology of TNA under its coverage prove that a thin layer of graphene with a certain thickness is deposited. to the TNA surface;
(3)制备Cu2O/G/TNA基片(在G/TNA基片沉积窄禁带半导体纳米颗粒):采用电化学沉积法将Cu2O纳米颗粒沉积在G/TNA表面,沉积Cu2O的电解液为CuSO4的乳酸水溶液,CuSO4的浓度为0.4 mol/L,乳酸的浓度为3 mol/L,通过5 mol/L NaOH将pH值调为10,沉积电压为-0.4 V,沉积时间为600 s。沉积完成后,用去离子水冲洗,吹干,即得到双面对称Cu2O/G/TNA膜光催化剂,记为样品1。其电镜扫描表面图如图2(c)所示,从图中可知Cu2O纳米颗粒均匀分布在石墨烯层表面,粒径约为80 nm;其电镜扫描单侧断面图如图2(d)所示,由图可知,石墨烯层和Cu2O纳米颗粒依次成功地沉积在TNA的表面并形成了三元复合光催化剂Cu2O/G/TNA。(3) Preparation of Cu 2 O/G/TNA substrate (deposition of narrow-bandgap semiconductor nanoparticles on G/TNA substrate): Cu 2 O nanoparticles were deposited on the surface of G/TNA by electrochemical deposition, and Cu 2 The electrolyte of O is CuSO 4 lactic acid aqueous solution, the concentration of CuSO 4 is 0.4 mol/L, the concentration of lactic acid is 3 mol/L, the pH value is adjusted to 10 by 5 mol/L NaOH, and the deposition voltage is -0.4 V, The deposition time was 600 s. After the deposition was completed, it was washed with deionized water and dried to obtain a double-sided symmetric Cu 2 O/G/TNA film photocatalyst, which was designated as sample 1. The surface image scanned by electron microscope is shown in Figure 2(c). It can be seen from the figure that Cu 2 O nanoparticles are uniformly distributed on the surface of the graphene layer, with a particle size of about 80 nm; ), it can be seen from the figure that the graphene layer and Cu 2 O nanoparticles were successively deposited on the surface of TNA and formed a ternary composite photocatalyst Cu 2 O/G/TNA.
.双室光反应器. Dual Chamber Photoreactor
双室光反应器,其结构如图3~5所示,包括阳极反应池A和阴极反应池B。分别向阳极反应池A和阴极反应池B内加入1 mol/L 的Na2SO4和NaHCO3溶液作为电解质,阳极反应池A和阴极反应池B之间的连接口7中间夹持Nafion质子交换膜,使阳极反应池和阴极反应池直接互不相通,仅有质子可通过Nafion膜在两池间流动;连接口6中间夹持Cu2O/G/TNA膜光催化剂制成的基片;阳极反应池A顶部均设有第一进气口1和第一出气口2,阳极反应池A侧壁上设有光窗口8;阴极反应池B顶部均设有第二进气口3和第二出气口4,侧壁上设有取液口5。The structure of the double-chamber photoreactor is shown in Figures 3 to 5, including an anode reaction pool A and a cathode reaction pool B. Add 1 mol/L Na 2 SO 4 and NaHCO 3 solutions into the anode reaction pool A and the cathode reaction pool B respectively as electrolytes, and the connection port 7 between the anode reaction pool A and the cathode reaction pool B is sandwiched between Nafion proton exchange Membrane, so that the anode reaction cell and the cathode reaction cell are directly isolated from each other, and only protons can flow between the two cells through the Nafion membrane; the substrate made of Cu 2 O/G/TNA film photocatalyst is clamped in the middle of the connection port 6; The top of the anode reaction pool A is equipped with a first air inlet 1 and a first air outlet 2, and the side wall of the anode reaction pool A is provided with a light window 8; the top of the cathode reaction pool B is equipped with a second air inlet 3 and a second air outlet. Two air outlets 4, and a liquid intake port 5 is arranged on the side wall.
光催化还原CO2实验Photocatalytic reduction of CO2 experiments
以附加400 nm紫外截止滤波片的300 W氙灯作为光源(λ>400 nm),反应开始后,高纯N2从第一进气口1进入阳极反应池A,从第一出气口2排出,CO2从第二进气口3进入阴极反应池B,从第二出气口4排出,光源激发基片上的光敏化剂在阳极面上产生光电子-空穴对,电子通过匹配的能级排列和电子传输层的作用向阴极面传递,空穴和电子分别迁移至光催化剂的阳极面和阴极面,在独立分离的反应池中参与水的光氧化和CO2的还原反应,光催化还原CO2过程示意图如图6所示。每隔1 h,从取液口5取出10 μL反应液,取样6次,通过配备有火焰离子检测器的气相色谱进行产物分析检测,以液相产物甲醇产量为催化性能评价指标,计算得到其产量分别为67.5、125、148、180、223及275 μmol/cm2,具体结果见图7。Using a 300 W xenon lamp with a 400 nm UV cut-off filter as the light source (λ>400 nm), after the reaction starts, high-purity N enters the anode reaction cell A from the first gas inlet 1 , and is discharged from the first gas outlet 2. CO2 enters the cathode reaction cell B from the second air inlet 3, and is discharged from the second air outlet 4. The light source excites the photosensitizer on the substrate to generate photoelectron-hole pairs on the anode surface, and the electrons pass through the matching energy level arrangement and The role of the electron transport layer is transmitted to the cathode surface, and the holes and electrons migrate to the anode and cathode surfaces of the photocatalyst, respectively, and participate in the photooxidation of water and the reduction of CO 2 in an independent reaction cell, and the photocatalytic reduction of CO 2 The schematic diagram of the process is shown in Figure 6. Every 1 h, 10 μL of the reaction solution was taken out from the liquid extraction port 5, and samples were taken 6 times, and the product was analyzed and detected by gas chromatography equipped with a flame ion detector. The yields were 67.5, 125, 148, 180, 223 and 275 μmol/cm 2 , respectively, and the specific results are shown in Figure 7.
实施例2~5Example 2~5
实施例2、3、4、5制备TNA膜基片的方法与实施例1相同,制备G/TNA基片和Cu2O/G/TNA基片的过程参考实施例1,具体的工艺参数见表1,相应的Cu2O/G/TNA基片依次标记为样品2、样品3、样品4、样品5。Examples 2, 3, 4, and 5 The method for preparing TNA film substrates is the same as that of Example 1, and the process for preparing G/TNA substrates and Cu2O /G/TNA substrates refers to Example 1. For specific process parameters, see In Table 1, the corresponding Cu 2 O/G/TNA substrates are marked as sample 2, sample 3, sample 4, and sample 5 in sequence.
实施例2、3、4、5的双室光反应器的连接口6中间分别夹持样品2、样品3、样品4、样品5,阳极反应池A和阴极反应池B内注入的电解质溶液种类见表1。Sample 2, sample 3, sample 4, sample 5 are respectively clamped in the middle of the connection port 6 of the double-chamber photoreactor of embodiment 2, 3, 4, 5, and the type of electrolyte solution injected in the anode reaction pool A and the cathode reaction pool B See Table 1.
实施例2、3、4、5光催化还原CO2制备甲醇实验的过程与实施例1相同。Examples 2, 3, 4, 5 The photocatalytic reduction of CO 2 The process of producing methanol experiment is the same as that of Example 1.
表1实施例1~5的工艺参数表The technological parameter table of table 1 embodiment 1~5
实施例6Example 6
G/TNA膜基片的制备过程与实施例1制备过程相同。The preparation process of the G/TNA film substrate is the same as that of Example 1.
采用水热沉淀法在G/TNA表面沉积CdS,过程为:分别配制浓度为0.004mol/L的氯化镉水溶液和硫脲的水溶液,按氯化镉水溶液︰硫脲的水溶液(物质的量比)为1∶3 的比例均匀混合。G/TNA膜基片竖直固定放置于高压反应釜内,加入氯化镉和硫脲混合溶液,将密封后的反应釜置于170 ℃烘箱中,反应时间为6 h。反应完毕后取出样品用蒸馏水清洗后在Ar气氛中400 ℃热处理3 h,制得CdS/G/TNA膜基片。CdS is deposited on the surface of G/TNA by hydrothermal precipitation method. The process is: respectively prepare cadmium chloride aqueous solution and thiourea aqueous solution with a concentration of 0.004mol/L, according to cadmium chloride aqueous solution: thiourea aqueous solution (mass ratio ) in a ratio of 1:3 and mixed evenly. The G/TNA membrane substrate was placed vertically in a high-pressure reactor, and a mixed solution of cadmium chloride and thiourea was added, and the sealed reactor was placed in an oven at 170 °C for 6 h. After the reaction, the sample was taken out, washed with distilled water, and then heat-treated at 400 °C for 3 h in an Ar atmosphere to prepare a CdS/G/TNA film substrate.
在双室光反应器的连接口6中间夹持CdS/G/TNA膜基片,光催化还原CO2制备甲醇,具体产物检测分析过程与实施例1相同,计算得到甲醇产量分别为52、78、110、130、151、170μmol/cm2,具体结果见图7。The CdS/G/TNA film substrate is clamped in the middle of the connection port 6 of the double-chamber photoreactor, and the photocatalytic reduction of CO is used to prepare methanol . The specific product detection and analysis process is the same as in Example 1, and the calculated methanol yields are 52 and 78, respectively. , 110, 130, 151, and 170 μmol/cm 2 , see Figure 7 for specific results.
实施例7Example 7
G/TNA膜基片的制备过程与实施例1的制备过程相同。The preparation process of the G/TNA film substrate is the same as that of Example 1.
采用光化学沉积法在G/TNA表面沉积ZnO,过程为:配置浓度为0.5 mol/L硝酸锌水溶液,将G/TNA膜基片竖直浸入硝酸锌溶液中,在紫外灯下对基片两面同时照射15 min,取出后用去离子水清洗干净后置于100℃下真空干燥,再在Ar气氛中450 ℃热处理1 h,即得采用光化学沉积法制备的ZnO/G/TNA膜基片。ZnO was deposited on the surface of G/TNA by photochemical deposition. The process was as follows: a zinc nitrate aqueous solution with a concentration of 0.5 mol/L was prepared, the G/TNA film substrate was vertically immersed in the zinc nitrate solution, and both sides of the substrate were simultaneously treated under an ultraviolet lamp. After irradiating for 15 min, take it out, wash it with deionized water, dry it in vacuum at 100 °C, and then heat-treat it in Ar atmosphere at 450 °C for 1 h, then the ZnO/G/TNA film substrate prepared by photochemical deposition method is obtained.
在双室光反应器的连接口6中间夹持ZnO/G/TNA膜基片,光催化还原CO2制备甲醇,具体产物检测分析过程与实施例1相同,计算得到甲醇产量分别为12.5、20、26、29、30、31 μmol/cm2,具体结果见图7。The ZnO/G/TNA film substrate is clamped in the middle of the connection port 6 of the double-chamber photoreactor, and the photocatalytic reduction of CO is used to prepare methanol . The specific product detection and analysis process is the same as in Example 1, and the calculated methanol production is 12.5, 20, respectively. , 26, 29, 30, 31 μmol/cm 2 , the specific results are shown in Figure 7.
实施例8Example 8
G/TNA膜基片的制备过程与实施例1的制备过程相同。The preparation process of the G/TNA film substrate is the same as that of Example 1.
采用电化学沉积法制备PbO2/G/TNA膜基片,过程为:先配制电镀液:电镀液中硝酸铅的浓度为20.5 mol /L,硝酸的浓度为0.1 mol /L,氟化钠的浓度为0.04 mol /L,再将G/TNA基片放置电镀液中,采用三电极体系,实施脉冲电沉积,温度为333 K,搅拌速度为300r/min,电沉积10 min,即得β-PbO2修饰的G/TNA基片,即PbO2/G/TNA膜基片。The PbO 2 /G/TNA film substrate was prepared by electrochemical deposition, the process is: first prepare the electroplating solution: the concentration of lead nitrate in the electroplating solution is 20.5 mol/L, the concentration of nitric acid is 0.1 mol/L, and the concentration of sodium fluoride The concentration was 0.04 mol/L, and then the G/TNA substrate was placed in the electroplating solution, and a three-electrode system was used to perform pulse electrodeposition at a temperature of 333 K, a stirring speed of 300r/min, and electrodeposition for 10 min to obtain β- PbO 2 modified G/TNA substrate, that is, PbO 2 /G/TNA film substrate.
在双室光反应器的连接口6中间夹持PbO2/G/TNA膜基片,光催化还原CO2制备甲醇,具体产物检测分析过程与实施例1相同,计算得到甲醇产量分别为40、51、55、68、73、75 μmol/cm2,具体结果见图7。The PbO2 /G/TNA membrane substrate is clamped in the middle of the connection port 6 of the double-chamber photoreactor, and the photocatalytic reduction of CO2 prepares methanol. The specific product detection and analysis process is the same as that of Example 1, and the calculated methanol production is 40, 51, 55, 68, 73, 75 μmol/cm 2 , see Figure 7 for specific results.
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| CN112354496B (en) * | 2020-11-27 | 2024-06-18 | 天津大学 | Building emission reduction reactor based on photoelectrocatalysis system |
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