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Cu/盘状ZnO模型催化剂催化CO2加氢反应中生成CO的活性位研究
引用本文:黄春蕾,钟雯,文进军,张明远,黄皓旻,付名利,吴军良,叶代启,陈礼敏.Cu/盘状ZnO模型催化剂催化CO2加氢反应中生成CO的活性位研究[J].环境科学学报,2019,39(6):1942-1951.
作者姓名:黄春蕾  钟雯  文进军  张明远  黄皓旻  付名利  吴军良  叶代启  陈礼敏
作者单位:华南理工大学环境与能源学院,广州,510006;华南理工大学环境与能源学院,广州510006;挥发性有机物污染治理技术与装备国家工程实验室,广州510006;广东省大气环境与污染控制重点实验室,广州510006;广东省环境风险防控与应急处置工程技术研究中心,广州510006
基金项目:国家自然科学基金(No.91645119,21207039,51878292);广东省自然科学基金(No.2017A030310537,S2011010000737);中央高校基本科研业务费(No.2017ZD076);广州市科技计划项目(No.201607010095);厦门大学固体表面物理化学国家重点实验室(No.201602)
摘    要:通过水热法合成盘状ZnO,并在其表面负载Cu得到Cu/盘状ZnO模型催化剂,将不同气氛下(5%CO/Ar、2.5%H_2/2.5%CO/Ar、5%H_2/Ar,分别记为CZ-5CO、CZ-2.5H_2-2.5CO、CZ-5H_2)还原的模型催化剂用于逆水煤气变换反应.对催化剂进行热重分析(TGA)、X射线衍射(XRD)、扫描电子显微镜(SEM)、X射线光电子能谱(XPS)、原位紫外拉曼光谱(in situ UV-Raman)表征.结果表明,不同的还原气氛可得到不同尺寸的Cu颗粒及不同缺陷浓度的Cu-ZnO界面.CO_2程序升温脱附(CO_2-TPD)结果表明,不同的Cu-ZnO界面具有不同的CO_2活化能力.其中CZ-5H_2形成的Cu-ZnO界面对CO_2活化能力最强,表现出最佳的逆水煤气变换反应活性;CZ-5CO具有更多的表面缺陷可能是由于存在Cu_3Zn合金,但Cu-ZnO界面上CO_2的吸附容量降低,导致逆水煤气变换反应活性低;CZ-2.5H_2-2.5CO的活性介于CZ-5H_2与CZ-5CO之间,界面对CO_2的活化量也介于两者之间.

关 键 词:Cu/盘状ZnO  模型催化剂  逆水煤气变换  Cu-ZnO界面  表面缺陷
收稿时间:2019/1/9 0:00:00
修稿时间:2019/3/9 0:00:00

The active sites study of Cu/ZnO plate model catalyst for CO2 hydrogenation to CO
HUANG Chunlei,ZHONG Wen,WEN Jinjun,ZHANG Mingyuan,HUANG Haomin,FU Mingli,WU Junliang,YE Daiqi and CHEN Limin.The active sites study of Cu/ZnO plate model catalyst for CO2 hydrogenation to CO[J].Acta Scientiae Circumstantiae,2019,39(6):1942-1951.
Authors:HUANG Chunlei  ZHONG Wen  WEN Jinjun  ZHANG Mingyuan  HUANG Haomin  FU Mingli  WU Junliang  YE Daiqi and CHEN Limin
Institution:School of Environment and Energy, South China University of Technology, Guangzhou 510006,School of Environment and Energy, South China University of Technology, Guangzhou 510006,School of Environment and Energy, South China University of Technology, Guangzhou 510006,School of Environment and Energy, South China University of Technology, Guangzhou 510006,1. School of Environment and Energy, South China University of Technology, Guangzhou 510006;2. National Engineering Laboratory for VOCs Pollution Control Technology and Equipment, Guangzhou 510006;3. Guangdong Provincial Key Laboratory of Atmospheric Environment and Pollution Control(SCUT), Guangzhou 510006;4. Guangdong Provincial Engineering and Technology Research Centre for Environmental Risk Prevention and Emergency Disposal, South China University of Technology, Guangzhou Higher Education Mega Centre, Guangzhou 510006,1. School of Environment and Energy, South China University of Technology, Guangzhou 510006;2. National Engineering Laboratory for VOCs Pollution Control Technology and Equipment, Guangzhou 510006;3. Guangdong Provincial Key Laboratory of Atmospheric Environment and Pollution Control(SCUT), Guangzhou 510006;4. Guangdong Provincial Engineering and Technology Research Centre for Environmental Risk Prevention and Emergency Disposal, South China University of Technology, Guangzhou Higher Education Mega Centre, Guangzhou 510006,1. School of Environment and Energy, South China University of Technology, Guangzhou 510006;2. National Engineering Laboratory for VOCs Pollution Control Technology and Equipment, Guangzhou 510006;3. Guangdong Provincial Key Laboratory of Atmospheric Environment and Pollution Control(SCUT), Guangzhou 510006;4. Guangdong Provincial Engineering and Technology Research Centre for Environmental Risk Prevention and Emergency Disposal, South China University of Technology, Guangzhou Higher Education Mega Centre, Guangzhou 510006,1. School of Environment and Energy, South China University of Technology, Guangzhou 510006;2. National Engineering Laboratory for VOCs Pollution Control Technology and Equipment, Guangzhou 510006;3. Guangdong Provincial Key Laboratory of Atmospheric Environment and Pollution Control(SCUT), Guangzhou 510006;4. Guangdong Provincial Engineering and Technology Research Centre for Environmental Risk Prevention and Emergency Disposal, South China University of Technology, Guangzhou Higher Education Mega Centre, Guangzhou 510006 and 1. School of Environment and Energy, South China University of Technology, Guangzhou 510006;2. National Engineering Laboratory for VOCs Pollution Control Technology and Equipment, Guangzhou 510006;3. Guangdong Provincial Key Laboratory of Atmospheric Environment and Pollution Control(SCUT), Guangzhou 510006;4. Guangdong Provincial Engineering and Technology Research Centre for Environmental Risk Prevention and Emergency Disposal, South China University of Technology, Guangzhou Higher Education Mega Centre, Guangzhou 510006
Abstract:ZnO plate was synthesized by hydrothermal method, and Cu was loaded on the surface of ZnO to obtain Cu/ZnO plate model catalyst. The catalyst was reduced under different atmospheres (5%CO/Ar, 2.5%H2/2.5%CO/Ar, 5%H2/Ar, labeled as CZ-5CO, CZ-2.5H2-2.5CO, CZ-5H2, respectively) and then evaluated for the reverse water gas shift reaction. Specifically, the catalysts were characterized by thermogravimetric analysis (TGA), X-ray diffraction (XRD), scanning electron microscopy (SEM), X-ray photoelectron spectroscopy (XPS) and in situ UV-Raman spectroscopy. The results indicate that the treatments under different reducing atmospheres can result in different Cu particle sizes and Cu-ZnO interfaces with different surface defect concentrations. And CO2 temperature programmed desorption (CO2-TPD) results show that different Cu-ZnO interfaces possess different CO2 activation capabilities. The Cu-ZnO interface formed in CZ-5H2 has the strongest CO2 activation ability and exhibits the best reverse water gas shift reaction activity. CZ-5CO has much more surface defects which may be due to the presence of Cu3Zn alloy, leading to lower CO2 adsorption capacity at the Cu-ZnO interface, resulting in low activity for reverse water gas shift reaction. In addition, the activity and the CO2 activation amount of CZ-2.5H2-2.5CO at the interface are both between those of CZ-5H2 and CZ-5CO.
Keywords:Cu/ZnO plate  model catalyst  RWGS  Cu-ZnO interface  surface defects
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