Seeing Cation Dopants in Gd-doped Ceria with STEM-EELS
Seeing Cation Dopants in Gd-doped Ceria with STEM-EELS
复制标题
使用 STEM-EELS 查看掺钆氧化铈中的阳离子掺杂剂
DOI:
10.1093/micmic/ozad067.195
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发表时间:
2023
影响因子:
2.8
通讯作者:
Crozier, Peter A
中科院分区:
文献类型:
--
作者:
Tan, Mai;Yang, Shize;Crozier, Peter A
Gd-doped ceria (GDC) is one of the most promising materials using in solid oxide fuel cell (SOFC) at median operating temperature below 700 C. It has shown high ion conductivity and stability at low/median temperatures compared with other candidate materials [1]. GDC is a non-stoichiometric oxide material that is known for its ability to exchange lattice oxygen with surrounding ambient environment. Adding the aliovalent dopant Gd to pure ceria enhances the oxygen exchange ability by creating more extrinsic oxygen vacancies, which results conductivity improvement [2]. The dopants distribution and local concentration may play an important role in oxygen exchange functionality. However, the relationship between the surface exchange rate and the atomic level defect location/distribution is not well understood. To understand a possible influence of point defect structures and location on exchange sites, it’s important to develop visualization methods to locate the defects. The atomic level Gd defect concentrations can be measured using scanning transmission electron microscopy coupled with electron energy-loss spectroscopy (STEM-EELS). However, for elemental mapping, the Gd EELS signal-to-noise ratio (SNR) is low, which making it difficult to detect and quantify. To address this weakness, we present a hybrid method involving EELS and high angle-annular dark-field imaging (HAADF).15% Gd-doped ceria (atomic weight%) nanoparticles were synthesized using a solution-based hydrothermal methods [3]. Gd cation point defects were detected and quantified via STEM-EELS spectrum imaging performed on an aberration-corrected Nion UltraSTEM 100 microscope (operated at 100kV). Nanoparticles were tilted into the [110] zone axis orientation, and EELS spectrum images were collected near (110) surfaces. HAADF image were collected simultaneous with the spectra. To calculate the local concentration of Gd, two approaches have been employed: traditional EELS mapping of Ce and Gd and, a hybrid HAADF/EELS approach. In the traditional approach, spectral processing involves background subtraction and separation of the overlapping Ce M23 and Gd M45 peaks to generate the Gd M45 elemental map. Figure 1 shows the HAADF image and the simultaneously acquired Ce and Gd elemental maps. Gd is not homogeneously distributed, and cluster formation is observed by comparing the Gd and Ce maps. Note that in elemental maps, there is an anti-correlation between the Gd and Ce signals. However, the Gd map is very noisy making it difficult to provide more detail information of the Gd distribution. Because the Gd signal is weak, we have developed a hybrid approach that relies primarily on the stronger Ce EELS signal and HAADF signals to deduce the Gd content. The method assumes that Gd ions substitute for Ce and that the HAADF cation signal is proportional to the total number of cations in the column. Figure 2 is a plot of the HAADF column intensity versus the sum of Ce+ Gd column intensity from the EELS maps (total EELS cation signal) for all the columns in Figure 1. Figure 2 shows that there is the linear relationship between these two integrated intensities. This implies that, for a particular column, a comparison of the Ce column intensity with the corresponding HAADF column intensity should allow the Gd EELS signal to be deduced. The Gd signal is then determined by subtracting Ce EELS signal from suitable scaled HAADF signal. Figure 3 shows results for local Gd column concentration determined with the traditional and hybrid methods. Both methods can successfully determine the concentration variation and showed the …