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Carbon monoxide (CO) is a gaseous pollutant with adverse effects on human health and the environment. Kaolinite is a natural mineral resource that can be used for different applications, including that it can also be used for retention of pollutant gases. The adsorption behavior of carbon monoxide molecules on the (001) surface of kaolinite was studied systematically by using density-functional theory and supercell models for a range coverage from 0.11 to 1.0 monolayers (ML). The CO adsorbed on the three-fold hollow, two-fold bridge, and one-fold top sites of the kaolinite(001) was tilted with respect to the surface. The strongest adsorbed site of carbon monoxide on the kaolinite (001) surface is the hollow site followed by the bridge and top site. The adsorption energy of CO decreased when increasing the coverage, thus indicating the lower stability of surface adsorption due to the repulsion of neighboring CO molecules. In addition to the adsorption structures and energetics, the lattice relaxation, the electronic density of states, and the different charge distribution have been investigated for different surface coverages.
High levels of gases such as pollutants coming from both natural and industrial activities are present in the atmosphere.[1,2] Carbon monoxide (CO) is categorized as a main pollutant by the US Environmental Protection Agency.[3] Carbon monoxide arises from the incomplete burning of materials, natural gas, industrial processes, sewage leaking, and biological decay.[4,5] Estimates of annual global emissions of CO vary from 2040 to 3315 terrogram (Tg).[6] The presence of CO in the atmosphere has a significant impact on climate, human health, and plants.[7–9] With the purpose of mitigating the effects it causes the health and longevity of both human beings and the earth’s fragile ecosystems, many researchers have investigated experimentally the removal of CO using physical and chemical treatments.[10–13] Adsorption, as a technique with increasingly innovative applications, in number and type, is one of the most appropriate easy ways to remove CO gas pollutant before being liberated.[14–17]
Natural clay minerals, in particular, have received much attention as an abundant, possible low-cost, and environment friendly material that can be used for different applications. Because of their large propensity for adsorbing and immobilizing extraneous species, clay minerals can serve as material for pollution control, carriers of pesticides, liners in waste disposal, and barriers in nuclear waste management. Adsorption properties of clay minerals have been known for many years and used as adsorbent in the retention of CO taken from contaminated air. Numerous studies reported that clay minerals are used to remove CO.[1,18–20] For example, Venaruzzo’s group investigated experimentally the adsorptions of CO, CO2, and SO2 gases on bentonitic clay minerals in natural state and after acid treatment. Itadani et al. have reported on low-pressure CO adsorption at room temperature on Al-pillared montmorillonite clay minerals by experimental techniques. Due to the limitations of experimental methods used, a theoretical analysis of the adsorption mechanism of CO molecules on natural clay minerals from a microscopic point of view will improve understanding of the adsorptive properties of the clay minerals–CO interface and the influence of CO adsorbed on the structure of clay minerals. Computer simulation in high-performance and the density-functional theory (DFT) offers accurate and inexpensive routes to study CO–solid interfaces at the molecular level, where the calculated results were very close to the experimental values.[21,22] Leydier’s group calculated theoretically the adsorption of CO on amorphous silica-alumina (ASA) by using density functional theory, while the infrared features results matched closely the experimental data. Several works[23–25] have investigated the adsorption of carbon monoxide on Cu(I)-ZSM-5 or Ag(I)-ZSM-5 zeolite by using ab initio density functional theory study. These results are in accord with previous study and available experimental findings.
Kaolinite is a specific and very common clay mineral.[26,27] Existing experimental[28–30] and theoretical[31–36] data on the kaolinite Al2Si2O5(OH)4 surface are often rationalized by modelling two surfaces as an almost perfect 1:1 layer structure constituted by two different surfaces of aluminosilicate: one side of the lamella consists of a silica sheet in which Si atoms are coordinated tetrahedrally by oxygen anions and the other side consists of a gibbsite type sheet where aluminum atoms are coordinated octahedrally by oxygen anions and hydroxyl groups. Some studies showed that hydrogen bonding and a certain degree of van der Waals attraction exist between hydroxyl groups of Al oxide side and adjoining oxygen atoms of silica sheet in kaolinite.[37] Kaolinite microparticles exist as hexagonal plates with a dominant (001) basal surface with almost perfect cleavage; this is the plane mainly exposed in kaolinite crystals. The hydroxylated (001) surface of kaolinite is said to be hydrophilic and is the surface of primary interest in adsorption behavior studies.[37–39] Since we have tested the adsorption energy of carbon monoxide on siloxane and hydroxylated surface of kaolinite, respectively and the results showed that carbon monoxide adsorbs more weakly on siloxane surface than it does on the hydroxylated surface, here we only examine the hydroxylated (001) surface. Hence, a greater insight into the adsorption of CO molecules on hydroxylated (001) surface of kaolinite through a periodic density functional analysis is needed. In the present paper, the CO adsorption geometries, CO structure during and after being adsorbed, adsorption energies, the electronic density of states, charge transfer, and the electronic density of states were investigated systematically.
All total-energy calculations of adsorption behavior of CO on the kaolinite (001) were performed using VASP (Vienna ab initio simulation package) code[40] that allows the simulation of periodic systems within the DFT method. The electrons are fully quantum-mechanical treated by solving the Kohn–Sham equations. The local-density approximation (LDA) and the projector augmented wave potential of Blöchl are employed to describe the electron exchange-correlation energy as described below and the electron–ion interaction, respectively.[41–44] The energy cutoff for the plane-wave expansion was set to 400 eV, which was sufficient to ensure the error from calculations of adsorption energies below 0.01 eV. The so-called ‘repeated slab’ geometries were employed. The clean kaolinite (001) surface was modelled by a slab consisting of six atomic layers separated by 20 Å of vacuum. The CO molecules were adsorbed on the (001) surface of the slab in a symmetric way for all slab calculations. During the calculation, the positions of H, O, and Al atoms in the outermost three layers as well as the CO molecules were allowed to relax until the forces on the ions are below 0.02 eV/Å. The other atoms in the bottom three atomic layers of the slab were kept fixed at the calculated bulk positions.[45–47] Furthermore, a Fermi broadening of 0.02 eV was chosen to smear the occupation of the bands around
In order to estimate the stability of these molecular adsorption configurations, the average adsorption energy of CO adsorption on the kaolinite (001) surface at different coverage is calculated by
![]() |
Here
![]() | Fig. 2. (color online) Adsorption geometry of CO molecule on the (a) top, (b) bridge, and (c) hollow sites of kaolinite (001). The adsorbed CO molecule is shown in blue for clarity. |
![]() | Table 1.
The adsorption energy |
One can see that at the coverage of 0.11 ML (for
Calculated geometries for CO molecule adsorption on the top, bridge, and hollow sites of kaolinite (001) at Θ = 0.11, 0.25, 0.33, 0.5, 0.75, and 1.0, including the C–O bond lengths
![]() | Table 2.
The calculated geometries for the CO molecule adsorption on top, bridge, and hollow sites of kaolinite (001). The C–O bond lengths |
Finally, we can easily see from Table
To gain more insights into the bonding interaction of the chemisorbed CO molecule with the neighboring O atoms of the kaolinite (001) surface, we calculated and analyzed the electronic partial density of state (PDOS) and the electron density difference
As a typical example, the PDOS of the adsorbed CO molecular orbitals (3σ, 4σ, 5σ, 1π, and 2
The projected DOS for CO molecule (in the stable bridge) and the neighboring O and H atoms of the (001) surface are calculated (Figs.
Finally, the PDOS of the tilted CO adsorbed on hollow site is depicted in Fig.
The PDOS for the CO molecule adsorption on top site and on surface H and O atoms at coverage of Θ = 0.25 and Θ = 1.0 ML, are shown in Figs.
The adsorption mechanism of CO molecule on the (001) surface of kaolinite are investigated systematically using first-principles DFT theory with total energy calculations. We consider a large range of coverage from 0.11 to 1.0 ML using two types of surface models (i.e.,
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