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活性氧自由基生成及传输对g-C_3N_4上NO光催化去除的影响:原位红外光谱与计算模拟结合法(英文) 被引量:4
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作者 李解元 颜萍 +5 位作者 李康璐 岑望来 于晓巍 袁山东 楚英豪 王正明 《Chinese Journal of Catalysis》 SCIE EI CAS CSCD 北大核心 2018年第10期1695-1703,共9页
石墨相氮化碳(g-C_3N_4)具有独特的二维层状结构和合适的能带结构,因而在可见光催化领域广受关注.尤其是在可见光去除环境污染物领域,得到了较为充分的研究与应用.然而g-C_3N_4去除环境污机理的反应机理尚不明确.因此,本文采用理论计算... 石墨相氮化碳(g-C_3N_4)具有独特的二维层状结构和合适的能带结构,因而在可见光催化领域广受关注.尤其是在可见光去除环境污染物领域,得到了较为充分的研究与应用.然而g-C_3N_4去除环境污机理的反应机理尚不明确.因此,本文采用理论计算与实验高度结合的研究方法,以光催化NO去除为例,深入阐述了光照下g-C_3N_4表面活性氧物种(ROS)的生成及转化过程,及其介导下的NO光催化氧化机理.X射线衍射结果表明,g-C_3N_4是三嗪环层内聚合后层层堆叠而成,并由红外光谱确定了其表面的官能团类型.该结构经扫描电镜和透射电镜得到了进一步的验证.采用光致激发谱和紫外可见漫反射光谱等实验表征与密度泛函理论计算结合的光电性质分析,我们发现,g-C_3N_4在可见光下具有一定的响应,这为其在光催化去除NO中奠定了基础.同时,其价带位置过高,无法自行产生氧化性较强的羟基自由基(.OH).电子自旋共振技术结果表明g-C_3N_4在光照下能捕获到·O_2^-和·OH两种活性自由基.采用反应路径计算发现,·OH是由·O_2^-在导带上逐步得到电子被还原而生成,其中的速率控制步骤是H_2O_2的解离.因此,促进O_2分子的吸附和活化和克服H_2O_2解离的反应活化能是产生·OH和提升g-C_3N_4光催化氧化活性的关键.采用原位红外光谱技术对g-C_3N_4上NO的氧化去除过程进行了表征,发现其主要中间产物为NO_2,主要终产物为NO_2^-和NO_3^-,采用反应路径计算对该反应过程进行了理论模拟,发现在·O_2^-介导下,最高反应活化能为0.66 eV,而在·OH介导下,该活化能降低至0.46 eV,表明·OH的氧化性要明显强于·O_2^-.总之,本文采用一种可行的、高度结合的实验与计算手段研究了g-C_3N_4上ROS的生成及转化过程及其对NO去除的反应历程,在原子尺度揭示了该反应的机理,加深了对ROS在光催化环境污染物降解过程中作用的理解. 展开更多
关键词 光催化 活性氧物种 石墨相氮化碳 NO去除 反应机理
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Lanthanum-doped Cu-Mn composite oxide catalysts for catalytic oxidation of toluene 被引量:5
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作者 Jing Pan Wentao Du +2 位作者 Yongjun Liu Yan Cheng shandong yuan 《Journal of Rare Earths》 SCIE EI CAS CSCD 2019年第6期602-608,共7页
CuMn mixed oxides catalysts doped with La were prepared following a co-precipitation method and used for the catalytic oxidation of toluene. Catalysts properties of the catalysts were investigated by X-ray diffraction... CuMn mixed oxides catalysts doped with La were prepared following a co-precipitation method and used for the catalytic oxidation of toluene. Catalysts properties of the catalysts were investigated by X-ray diffraction, N_2 adsorption/desorption,scanning electron microscopy, H_2-temperature-programmed reduction(H_2-TPR), O_2-temperature-programmed desorption(O_2-TPD) and X-ray photoelectron spectroscopy techniques. Characterization data reveal that the phase change and decrease in crystallinity of the La-doped catalysts increase the number of oxygen vacancies. Improvements in reducibility and an increase in the amount of chemisorbed oxygen of the La-doped catalysts were also verified by H_2-TPR and O_2-TPD. The activity of the CuMn mixed oxides catalysts is significantly improved by the addition of a nominal amount of La. The CuMn/La-4 mol% catalyst exhibits the best catalytic activity, with a 90%conversion temperature of 255 ℃,attributed to a high Mn^(3+)ratio, superficial chemisorbed oxygen,and high surface area. This study indicates La to be a promising dopant for Cu-Mn catalysts toward toluene oxidation. 展开更多
关键词 MANGANESE Copper LANTHANUM CATALYTIC combustion TOLUENE RARE earths
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Effect of doped strontium on catalytic properties of La_(1-x)SrxMnO_(3) for rhodamine B degradation 被引量:2
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作者 Jiaxiu Guo YueJing +3 位作者 Ting Shen Hongdi Luo Juan Liang shandong yuan 《Journal of Rare Earths》 SCIE EI CAS CSCD 2021年第11期1362-1369,I0002,共9页
A series of La_(1-x)Sr_(x)MnO_(3) samples were prepared by sol-gel method and used to degrade rhodamine B(RhB) in water.All samples were characterized by X-ray diffraction(XRD),X-ray photoelectron spectroscopy(XPS),N_... A series of La_(1-x)Sr_(x)MnO_(3) samples were prepared by sol-gel method and used to degrade rhodamine B(RhB) in water.All samples were characterized by X-ray diffraction(XRD),X-ray photoelectron spectroscopy(XPS),N_(2) adsorption-desorption,temperature-programmed reduction of H_(2)(H_(2)-TPR) and temperature-programmed desorption of O_(2)(O_(2)-TPD).The results show that the degradation of RhB is highly dependent on the initial pH value of solution.Sr doping enhances the degradation ability of LaMnO_(3) for RhB in the time range of 0-40 min under a strong acidic environment,but all samples exhibit similar degradation rate from 40 to 60 min.In La_(0.7)Sr_(0.3)MnO_(3)-RhB reaction system,there are two different degradation pathways,including N-de-ethylation,chromophore cleavage,ring-opening and mineralization.La_(1-x)Sr_(x)MnO_(3)(x ≤0.3) has the perovskite structure of La-Mn oxides,while La_(0.6)Sr_(0.4)MnO_(3) exhibits a Sr_(0.4)MnLa_(0.6)O_(2).98 perovskite phase.Sr doping leads to distortion of rhombohedral crystal structure and increases the relative content of Mn^(4+).The perovskite structure is stable in strong acidic environment during RhB degradation,but the relative content of Mn^(4+)and Mn^(3+) on the material surface changes.Sr doped LaMnO_(3) achieves specific surface area of 58.8 m^(2)/g and total pore volume of 0.152 cm^(3)/g.Furthermore,Sr^(2+)doping improves redox properties of La-Mn oxides,and the presence of defects makes oxygen diffusion easier compared with the undoped samples. 展开更多
关键词 Organic pollutant DEGRADATION Rhodamine B LaMnO_(3) SR PEROVSKITE
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