Zheng
Zhang
ab,
Qiang
Zhao
*ab,
Mei
Huang
ab,
Xiaodong
Zhang
ab and
Xiaoping
Ouyang
acd
aBeijing Key Laboratory of Passive Safety Technology for Nuclear Energy, North China Electric Power University, Beijing 102206, People's Republic of China. E-mail: qzhao@ncepu.edu.cn
bSchool of Nuclear Science and Engineering, North China Electric Power University, Beijing 102206, People's Republic of China
cNorthwest Institute of Nuclear Technology, Xi'an 710024, People's Republic of China
dSchool of Materials Science and Engineering, Xiangtan University, Xiangtan 411105, People's Republic of China
First published on 10th September 2018
In the process of developing nuclear energy, removing radioactive waste in the environment is a challenging problem that human beings have to face. The main work of this paper is to investigate the mechanism of the interaction between metallic radionuclides (Cs, Sr, and Ba) and a monolayer MoS2 nanosheet, and the work is completed by using the first principles calculation method. The results show that all of the three kinds of metallic radionuclides can be chemisorbed on the monolayer MoS2 nanosheet. The optimum adsorption site for the metallic radionuclides adsorbed on the monolayer MoS2 is TMo (top of the Mo atom), because the metallic radionuclides can interact with the three nearest S atoms when the metallic radionuclides are at the TMo site. The chemisorption strength of the metallic radionuclides on the monolayer MoS2 is Ba > Sr > Cs. The mechanism of the chemisorption is explored by using the total charge transfer, density of states, and electron density difference. The final analysis shows that the s orbital of S atoms plays an important role in the chemisorption.
In the past few decades, a considerable number of materials were studied to find out a candidate material for the efficient removal of radionuclides, and the related research on zeolites, molecular sieves, and other materials has achieved great progress. Since graphene was invented, the research on the two-dimensional material has received increasing attention from scientists and engineers, due to its unique band structure, semi-conducting or superconducting properties, excellent mechanical performance, and so on. The two-dimensional material is widely considered for use in electronic devices, catalysis, energy storage, tools used under extreme conditions, and other fields. With the deepening of the research, the two-dimensional material is considered as a new kind of candidate material, which is used in environmental remediation. Through the hard work of Wang's team,5–9 the mechanism of graphene removing radionuclides from the environment has been clarified, and their studies show that oxygen-containing functional groups are crucial for improving the adsorption capacity of graphene for radionuclides. Meanwhile, scientists have found that MoS2 has some adsorption capacity for heavy metal ions10,11 and toxic gas molecules,12–15 and the optical properties of monolayer MoS2 changed when some organic macromolecules were adsorbed on monolayer MoS2.16 Monolayer MoS2 can also be considered as a candidate cathode material for Li-ion batteries.17 Based on the above research, MoS2 is considered as a potential material for environmental restoration.18 Especially, scientists believe that MoS2 is a potential sensor material for toxic gases, such as CO, NO, HS2, NH3, SO2 and so on. Using the first principles calculation method, the electronic and magnetic properties of MoS2 have been investigated,19 and the adsorption energy and charge transfer of different kinds of toxic gas molecules adsorbed on monolayer MoS2 have been reported,20–22 and the result shows that MoS2 can monitor toxic gases in the atmosphere. Based on this research, we think that MoS2 might be a candidate material for radionuclide removal from the environment. As for the preparation of monolayer MoS2, three successful methods have been reported, such as mechanical exfoliation, liquid exfoliation, and chemical vapor deposition (CVD). The successful preparation of the material has provided the possibility for its large-scale application, especially in the field of radioactive environmental restoration.
89Sr, 90Sr, 134Cs, 137Cs, and 140Ba are the common radionuclides in waste water from nuclear plants, and the half-time of 89Sr, 90Sr, 134Cs, 137Cs, and 140Ba is about 50.5 days, 28.6 years, 2.06 years, 30.17 years, and 12.75 days, respectively. 89Sr, 90Sr, and 140Ba are pure beta decay nuclides, and the maximum energy of the β ray is about 1.46 MeV, 0.546 MeV, and 1.0 MeV, respectively. 134Cs and 137Cs are both the gamma source and the beta source, and the characteristic energy of the γ ray from the emission of 137Cs is about 661.66 keV. All of the metallic radionuclides have adverse impacts on the environment, and more importantly, they are harmful to public health. How to remove the three kinds of metallic radionuclides in waste water is very important for the treatment of radioactive waste water. Therefore, we focused on the adsorption of the three kinds of metallic radionuclides on monolayer MoS2. As we know, although the atomic mass of isotopes is different, their chemical properties are basically similar. The chemical properties of metallic radionuclides depend upon the electrons on the outside. The effects of the radioactivity of metallic radionuclides on the adsorption capacity of MoS2 is beyond the scope of this study.
In our previous work,23 we just show that monolayer MoS2 can adsorb metallic radionuclides, and the adsorption belongs to chemisorption according to the adsorption energies of the metallic radionuclides on monolayer MoS2. In this paper, we aim to study why monolayer MoS2 can adsorb metallic radionuclides. The mechanism of monolayer MoS2 adsorbing metallic radionuclides has been explored clearly, which may provide a theoretical basis for relevant experimental research in the future. Based on our previous work, we calculated the charge transfer, electron density difference, total densities of states (TDOS) and partial densities of states (PDOS), to clarify the mechanism of the adsorption. We hope that our work can shed some light on environmental remediation, especially the treatment of radioactive waste water.
A 5 × 5 × 1 supercell of monolayer MoS2 (containing 25 Mo atoms and 50 S atoms) with a single metallic radionuclide adsorbed onto it is constructed to be the calculation model. Fig. 1 shows the positions of the metallic radionuclides adsorbed on the 5 × 5 × 1 MoS2 supercell, and glaucous and yellow balls represent Mo and S atoms, respectively. For the single metallic radionuclide, there are four possible adsorption sites, TMo (top of the Mo atom), TS (top of the S atom), H (the centre of the hexagon), and B (the bridge of Mo–S).
For the adsorption of the metallic radionuclides, the adsorption energy is calculated using the following relationship:
Ead = EM+MoS2 − EMoS2 − EM, | (1) |
We calculated the charge transfer Qt based on Mulliken30 and Hirshfeld31 methods. To understand the difference between Mulliken and Hirshfeld methods, here we briefly introduce these two methods of calculating atomic charge. First, the normalization condition of the molecular orbital wave function is considered,
(2) |
Where, r represents the space coordinates. The molecular orbitals ϕi are expanded by using atomic-centered basis functions χm,
(3) |
Where, C is the matrix of coefficient, and by substituting eqn (3) into eqn (2), a result can be obtained after integration,
(4) |
Where, . The first item in eqn (4) is the sum of independent contributions of each basis function to the orbit, and it is called the localized term. The second item is the cross term, and it represents the joint contribution to the orbit due to the coupling between each pair of basis functions. Mulliken defines the composition of the fundamental function m in molecular orbital i as:
(5) |
That is to say, the localized term is completely assigned to the corresponding base function, and the cross term is bisected into the corresponding two basis functions. The atomic populations can be obtained by adding up the populations of all the basis functions that belong to the same atom in all the orbitals, and the Mulliken atomic charge is given by the equation,
(6) |
Where, ZA is the nuclear charge number, and η is the orbital population.
The Hirshfeld atomic charge is defined as,
(7) |
(8) |
(9) |
The atoms have a positive charge when the Mulliken or Hirshfeld charge (e) > 0, and the atom has a negative charge when the Mulliken or Hirshfeld charge (e) < 0. The positive value of Qt shows that the electrons transferred from the metallic radionuclides to monolayer MoS2, while the negative value of Qt indicates that the electrons transferred from monolayer MoS2 to the metallic radionuclides. In order to explore the interaction mechanism between the metallic radionuclides and monolayer MoS2, we calculated the electron density difference, total densities of states (TDOS) and partial densities of states (PDOS).
Fig. 2 The band structure (a) and density of states (b) of monolayer MoS2, and the red dashed lines stand for the Fermi level. |
Configuration | E ad | Q t-Mulliken | Q t-Hirshfeld | h |
---|---|---|---|---|
TMo | −3.258 | 0.99 | 0.59 | 2.821 |
TS | −3.028 | 0.98 | 0.66 | 3.221 |
B | −3.259 | 1.00 | 0.59 | 2.829 |
H | −3.255 | 0.99 | 0.59 | 2.817 |
Fig. 3 The relaxed configuration, band structure (from −10 eV to 5 eV), density of states, and electron density difference of the radionuclide Cs on monolayer MoS2. |
In addition, it can be found that the total charge transfer Qt for different initial structures obtained by the Mulliken and Hirshfeld methods have the same trend. The total charge transfer of the radionuclide Cs adsorbed on the monolayer MoS2 nanosheet with all of the initial configurations is positive, indicating that the radionuclide Cs acts as the electron donor and the monolayer MoS2 nanosheet acts as the electron acceptor. For the adsorption of the radionuclide Cs on monolayer MoS2 with all of the initial structures, the corresponding charge transfer value based on the Mulliken method is higher than that of the Hirshfeld method. And for the adsorption of the radionuclide Cs on monolayer MoS2 with the B initial structure, the corresponding charge transfer obtained by Mulliken and Hirshfeld methods is 1.00 e and 0.59 e, respectively.
Fig. 3(b) shows the band structure of a metallic radionuclide Cs adsorbed on monolayer MoS2. There is no band gap in the band structure, and this phenomenon means that the band gap disappeared in the band structure after a metallic radionuclide Cs was adsorbed on monolayer MoS2.
In order to further explore the interaction mechanism between the radionuclide Cs and monolayer MoS2 nanosheet, we calculated the TDOS, PDOS and electron density difference of the system before and after adsorption. Fig. 3(c) shows the TDOS and PDOS of the Cs atom adsorbed on monolayer MoS2 with the B initial structure. There are four regions in the valence band, including the high energy region (from −6 eV to 0 eV), the second high energy region (near −14 eV), the medium energy region (near −36 eV), and the low energy region (near −62 eV). The high energy region, the medium energy region, and the low energy region consist of Mo d, p, and s orbitals, and the S p orbital also makes a contribution to the high energy region; the second high energy region is composed of the S s orbital. After the radionuclide Cs was adsorbed on monolayer MoS2, two small peaks (near −10 eV and −23 eV) appeared in the valence band. According to the density of states, the adsorption of the radionuclide Cs on monolayer MoS2 was mainly caused by the hybridization between Cs p and S s orbitals.
The electron density difference of radionuclide Cs adsorbed on monolayer MoS2 with the B initial structure is shown in Fig. 3(d). The red and blue regions in the figure indicate the increase and decrease of the electron density, respectively. It can be found that the electron density near the S atom increased obviously and the electron density near the Mo and Cs atoms decreased after the radionuclide Cs was adsorbed on monolayer MoS2, which further confirmed that the radionuclide Cs acts as the electron donor and monolayer MoS2 acts as the electron acceptor; more precisely, the S atoms near the radionuclide Cs act as the electron acceptor.
Configuration | E ad | Q t-Mulliken | Q t-Hirshfeld | h |
---|---|---|---|---|
TMo | −2.822 | 1.27 | 0.73 | 1.845 |
TS | −2.589 | 1.28 | 0.89 | 2.265 |
B | −3.863 | 1.24 | 0.72 | 1.836 |
H | −3.847 | 1.27 | 0.74 | 1.799 |
Fig. 4(a) shows the optimized structure of radionuclide Sr adsorbed on monolayer MoS2 with the B initial configuration. After relaxation, the bond length of Mo–S1, Mo–S2, and Mo–S3 bonds increased to 2.412 Å, 2.466 Å, and 2.424 Å, respectively. Due to the radionuclide Sr adsorbed on monolayer MoS2, the length of Mo–S bonds (near the radionuclide Sr) becomes longer than that in MoS2, and this result means that the interaction between the Mo atom and S atom is weakened by the radionuclide Sr. The distances between the radionuclide Sr and Mo, S1, S2, and S3 are 3.517 Å, 2.776 Å, 2.778 Å, and 2.764 Å, respectively. These values indicate that the interaction between the radionuclide Sr and S atoms is stronger than the interaction between the radionuclide Cs and S atoms.
Fig. 4 The relaxed configuration, band structure (from −10 eV to 5 eV), density of states, and electron density difference of the radionuclide Sr on monolayer MoS2. |
Although the total charge transfer Qt for different initial configurations obtained by the Mulliken and Hirshfeld method is different, they have the same trend. In the interaction process, the Sr atom acts as electron donor and monolayer MoS2 acts as electron acceptor. For the adsorption of Sr on monolayer MoS2 with B initial configuration, the corresponding charge transfer Qt obtained by Mulliken and Hirshfeld method is 1.24 e and 0.72 e, respectively.
Fig. 4(b) shows the band structure of a radionuclide Sr on monolayer MoS2 with the initial configuration B, and the band gap of this configuration is 0.271 eV. The decrease of the band gap is due to the adsorption of the radionuclide Sr. Fig. 4(c) shows the TDOD and PDOS of the radionuclide Sr adsorbed on monolayer MoS2. There is a hybridization exists between the s orbital of the S atom and the p orbital of the Sr atom and the Mo p orbital. When the radionuclide Sr is at the TMo site, there is an interaction between the radionuclide Sr and the three nearest S atoms.
Fig. 4(d) shows the electron density difference of the radionuclide Sr adsorbed on monolayer MoS2 with TMo configuration. The S atoms act as the electron accepter, and the Mo and Sr atoms act as the electron donor. This result is in good agreement with the total charge transfer Qt obtained by Mulliken and Hirshfeld methods.
Configuration | E ad | Q t-Mulliken | Q t-Hirshfeld | h |
---|---|---|---|---|
TMo | −2.208 | 0.95 | 0.81 | 2.128 |
TS | −4.108 | 0.95 | 0.80 | 2.185 |
B | −4.137 | 0.94 | 0.80 | 2.093 |
H | −4.114 | 0.90 | 0.78 | 2.056 |
When we calculated the total charge transfer, the difference in the total charge transfer obtained by the Mulliken and Hirshfeld methods still exists, but the total charge transfer obtained by the two methods has the same trend. Like Cs and Sr adsorbed on monolayer MoS2, the Ba atom acts as the electron donor and monolayer MoS2 acts as the electron acceptor. For Ba adsorbed on monolayer MoS2 with B initial configuration, the total charge transfer obtained by the Mulliken and Hirshfeld methods is 0.94 e and 0.80 e, respectively. The relationship between charge transfer and adsorption energy is analyzed, but the effect of the charge transfer on the adsorption energy is not obvious.
Fig. 5(b) shows the band structure of the radionuclide Ba adsorbed on monolayer MoS2. When compared with pristine monolayer MoS2, the band gap of monolayer MoS2 has narrowed due to the adsorption of the radionuclide Ba, and all of the three kinds of metallic radionuclides have similar effects on the band structure of monolayer MoS2. Fig. 5(c) shows the TDOS and PDOS of the radionuclide Ba adsorbed on monolayer MoS2, and there is a hybridization between the S s orbital and Ba p orbital, and the main reason for the adsorption of the radionuclide Ba on monolayer MoS2 might be the hybridization.
Fig. 5(d) shows the electron density difference of the radionuclide Ba adsorbed on monolayer MoS2 with the TMo configuration (relaxed from the B initial configuration). The red and blue regions in the figure indicate the increase and decrease of the electron density, respectively. The radionuclide Ba and Mo atoms act as the electron acceptor and the S atoms near the radionuclide Ba act as the electron donor, and the result is in agreement with the total charge transfer Qt obtained by the Mulliken and Hirshfeld methods.
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