Jung Ji-Eun, Liguori Simona, Jew Adam D, Brown Gordon E, Wilcox Jennifer
a Department of Energy Resources Engineering, School of Earth, Energy, and Environmental Sciences , Stanford University , Stanford , CA , USA.
b Department of Geological Sciences, School of Earth, Energy, and Environmental Sciences , Stanford University , Stanford , CA , USA.
J Air Waste Manag Assoc. 2018 Jan;68(1):39-53. doi: 10.1080/10962247.2017.1362364. Epub 2017 Dec 6.
One of the biggest environmental concerns caused by coal-fired power plants is the emission of mercury (Hg), which is toxic metal. To control the emission of Hg from coal-derived flue gas, it is important to understand the behavior and speciation of Hg as well as the interaction between Hg and solid materials in the flue gas stream. In this study, atomic-scale theoretical investigations using density functional theory (DFT) were carried out in conjunction with laboratory-scale experimental studies to investigate the adsorption behavior of Hg on hematite (α-FeO). According to the DFT simulation, the adsorption energy calculation proposes that Hg physisorbs to the α-FeO(0001) surface with an adsorption energy of -0.278 eV, and the subsequent Bader charge analysis confirms that Hg is slightly oxidized. In addition, Cl introduced to the Hg-adsorbed surface strengthens the Hg stability on the α-FeO(0001) surface, as evidenced by a shortened Hg-surface equilibrium distance. The projected density of states (PDOS) analysis also suggests that Cl enhances the chemical bonding between the surface and the adsorbate, thereby increasing the adsorption strength. In summary, α-FeO has the ability to adsorb and oxidize Hg, and this reactivity is enhanced in the presence of Cl. For the laboratory-scale experiments, three types of α-FeO nanoparticles were prepared using the precursors Fe(NO), Fe(ClO), and FeCl, respectively. The particle shapes varied from diamond to irregular stepped and subrounded, and particle size ranged from 20 to 500 nm depending on the precursor used. The nanoparticles had the highest surface area (84.5 m/g) due to their highly stepped surface morphology. Packed-bed reactor Hg exposure experiments resulted in this nanoparticles adsorbing more than 300 μg Hg/g. The Hg L-edge extended X-ray absorption fine structure spectroscopy also indicated that HgCl physisorbed onto the α-FeO nanoparticles.
Atomic-scale theoretical simulations proposes that Hg physisorbs to the α-FeO(0001) surface with an adsorption energy of -0.278 eV, and the subsequent Bader charge analysis confirms that Hg is slightly oxidized. In addition, Cl introduced to the Hg-adsorbed surface strengthens the Hg stability on the α-FeO(0001) surface, as evidenced by a shortened Hg-surface equilibrium distance. The PDOS analysis also suggests that Cl enhances the chemical bonding between the surface and the adsorbate, thereby increasing the adsorption strength. Following laboratory-scale experiment of Hg sorption also shows that HgCl physisorbs onto α-FeO nanoparticles which have highly stepped structure.
燃煤发电厂造成的最大环境问题之一是汞(Hg)排放,汞是一种有毒金属。为了控制煤衍生烟道气中的汞排放,了解汞的行为和形态以及汞与烟道气流中固体材料之间的相互作用非常重要。在本研究中,结合实验室规模的实验研究,使用密度泛函理论(DFT)进行了原子尺度的理论研究,以研究汞在赤铁矿(α-Fe₂O₃)上的吸附行为。根据DFT模拟,吸附能计算表明汞以-0.278 eV的吸附能物理吸附在α-Fe₂O₃(0001)表面,随后的巴德电荷分析证实汞被轻微氧化。此外,引入到汞吸附表面的氯增强了汞在α-Fe₂O₃(0001)表面的稳定性,汞-表面平衡距离缩短证明了这一点。态密度投影(PDOS)分析还表明,氯增强了表面与吸附质之间的化学键,从而提高了吸附强度。总之,α-Fe₂O₃具有吸附和氧化汞的能力,并且在氯存在下这种反应性会增强。对于实验室规模的实验,分别使用前驱体Fe(NO₃)₃、Fe(ClO₄)₃和FeCl₃制备了三种类型的α-Fe₂O₃纳米颗粒。颗粒形状从菱形到不规则阶梯状和次圆形不等,粒径根据所用前驱体的不同在20到500 nm之间。由于其高度阶梯状的表面形态,这些纳米颗粒具有最高的表面积(84.5 m²/g)。固定床反应器汞暴露实验结果表明,这些纳米颗粒吸附的汞超过300 μg/g。汞L边扩展X射线吸收精细结构光谱也表明HgCl物理吸附在α-Fe₂O₃纳米颗粒上。
原子尺度的理论模拟表明,汞以-0.278 eV的吸附能物理吸附在α-Fe₂O₃(0001)表面,随后的巴德电荷分析证实汞被轻微氧化。此外,引入到汞吸附表面的氯增强了汞在α-Fe₂O₃(0001)表面的稳定性,汞-表面平衡距离缩短证明了这一点。PDOS分析还表明,氯增强了表面与吸附质之间的化学键,从而提高了吸附强度。随后的汞吸附实验室规模实验也表明,HgCl物理吸附在具有高度阶梯结构的α-Fe₂O₃纳米颗粒上。