Abstract
Environmental pollution by organic pollutants is a serious concern which may be solved by photocatalytic degradation of pollutants, yet the efficiency of actual photocatalytic materials is limited. For instance, conventional MoS2 nanosheets tend to agglomerate, which hinders the access of pollutants to active sites. To overcome this challenge, we hypothesized that assembling MoS2 nanosheets on a mineral support would improve access to active sites. We synthesized a catalyst made of 3–4 atomic layers of MoS2 nanosheets deposited on tourmaline using a microwave hydrothermal method. Results show that tourmaline occurs as a polyhedron single crystal that supports the epitaxial growth of 2H-MoS2 layers on tourmaline (77\(\overline{3}\)) facets, while an intrinsic rolling up behavior of MoS2 layer from [002] to [106] on the mineral surface accounts for the curly morphology. The pangolin-like MoS2/tourmaline composite degrades rhodamine B much better than the pure MoS2 nanosheets assembled microspheres. This is explained by the reduced thickness of MoS2 nanosheets according to the density functional theory. Overall, our findings represent a new tactic for the cost-effective batch preparation of two-dimensional materials with high catalytic performance.
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Introduction
With the development of industry, excessive discharge of organic wastewater has become one of the most serious environmental problems around the world, which poses a significant threat to environment and human health due to its persistence and toxicity (Saravanan et al. 2021; Madima et al. 2020; Mecha. et al. 2020). At present, photocatalysis as a simple and economical method has been widely used to remove organic pollutants from wastewater (de Lima et al. 2020; Saeed et al. 2018). Compared with the common photocatalyst containing TiO2 and CdS, molybdenum sulfide (MoS2), a typical layered two-dimensional semiconductor material, has received considerable attention in the photo-degradation of organic pollutants due to its strong visible light response, layered structure, and environment-friendly nature (Gan et al. 2020; Wang and Mi 2017). However, due to its high specific surface energy, nanostructured MoS2 suffers from aggregation inevitably which causes rapid recombination of electron–hole pairs and thus poor catalytic performance (Qu et al. 2013). One effective solution is to disperse the MoS2 on support materials, such as graphene (Kumar et al. 2019), graphitic carbon nitride (Liu et al. 2018), reduced graphene oxide (Sun et al. 2017), titanium dioxide (Zhao et al. 2019), and Bi2MoO6 (Li et al. 2018). However, the high preparation cost and the problematic environmental load limit these fabrication approaches from industrial applications. It becomes practically important that the MoS2 nanostructures with few layers and full of active sites could be stably assembled on a support of highly natural abundance, e.g., minerals. Mineral carriers own merits of low-cost and environmental benignity (Wang et al. 2021; Hao et al. 2021; Saja et al. 2020), making them as promising candidates as a functional support. However, only few studies have focused on the fabrication of MoS2 nanostructures using mineral supports, especially tourmaline. Tourmaline-supported MoS2 is believed to be structurally beneficial to provide more active sites via good assembly flexibility based on its unique characteristics including spontaneous polarization and far infrared radiation.
Tourmaline is a borosilicate mineral with the R3m space group (Guerra et al. 2012) and the chemical formula of XY3Z6Si6O18(BO3)3W4, where X is Na+, Ca2+, K+, or vacancies; Y is Mg2+, Mn2+, Fe2+, Al3+, Fe3+, Mn3+, or Li+; Z is Al3+, Fe3+, Cr3+, or Mg2+; and W is OH−, F−, or O2−. It has been extensively studied due to the spontaneous and permanent poles which can produce an electric dipole (Zhou et al. 2018). Moreover, the strong electric field formed on the tourmaline surface can accelerate the separation/transportation of photoexcited charge carriers (Li et al. 2015). Besides, other unique properties such as pyroelectric, piezoelectric, and far infrared radiation have made tourmaline flexible in various fields (Zhang et al. 2014). Therefore, tourmaline owns not only the merits of the low cost but also several unique properties compared with some common carbon materials including carbon powder, biochar, and carbon nanotubes (Xu et al. 2020, 2019, 2016). In our previous studies, tourmaline has been found to effectively decrease agglomeration of silica hollow microspheres (Wang et al. 2017), as well as the nanoparticle’s size (Zhang et al. 2017a). In addition, our previous study was successful in fabricating a FeMnTiOx catalyst synergized with tourmaline support for low-temperature NH3-SCR (Wang et al. 2019). These works serve as direct evidence that tourmaline can be used to improve catalytic activity. In this work, using a one-step microwave hydrothermal method, we report the first preparation of an ingenious MoS2/tourmaline composite composed of atomically few layered MoS2 nanosheets growing along the surface of tourmaline particles. This structure significantly increases the dispersion of MoS2 nanosheets and provides more active sites for catalysis. The spontaneous polarization and far infrared radiation of tourmaline support ensure even adsorption and nucleation of MoS2 species through promoting the thermal vibration and reducing the diffusion activation energy of Mo and S atoms. Meanwhile, strong electric field on the surface of tourmaline can restrain the recombination of photo-generated electron–hole pairs (Tzeng et al. 2019). This work provides an inspiring scheme for low-cost batch preparation of high-quality two-dimensional materials via assembly on tourmaline mineral functional materials.
Materials and methods
Materials
The tourmaline was provided by HY Technology Co., Ltd. The ammonium molybdate (NH4)6Mo7O24·4H2O), thiourea (CH4N2S) and rhodamine B (RhB) were supplied by Kewei Chemical Group Co., Ltd. These materials were used as received. Deionized (DI) water was used in all experiments.
Synthesis of MoS2/tourmaline composites
2.4 g (NH4)6Mo7O24·4H2O and 2.28 g CH4N2S were dissolved in 70 mL deionized water and stirred for 0.5 h. Then, 0.84 g of tourmaline powder was added into the above solution and mechanically stirred for another 0.5 h. Next, the suspension was sonicated for 0.5 h. After that, 50 mL of the above suspension was transferred into a 100 mL Teflon-lined stainless steel autoclave and kept at different hydrothermal temperatures including 190, 200, 210, 220, and 230 °C for 3 h. After the samples were cooled to room temperature, the final products were obtained by filtration, washed thoroughly with deionized water, and dried at 80 °C for 12 h. The samples synthesized at 190 °C, 200 °C, 210 °C, 220 °C, and 230 °C were named as T-190, T-200, T-210, T-220, and T-230, respectively.
Characterizations
X-ray diffraction was performed on a D8 ADVANCE X-ray diffractometer with nickel-filtered Cu Kα radiation as the X-ray source, and V = 40 kV, I = 40 mA, and λ = 1.54 Å. Fourier-transform infrared spectroscopy (FTIR) spectra were recorded in transmission mode from 400 to 4000 cm−1 on a Tensor II Fourier transform infrared spectrometer purchased from Bruker in Germany. The morphology of the samples was observed using a Quanta FEG450 scanning electron microscope working at 200 kV. Transmission electron microscope (TEM) and high-resolution TEM (HRTEM) images were acquired using a JEM 2100F transmission electron microscope from JEOL in Japan at an accelerating voltage of 200 kV. X-ray photoelectron spectroscopy (XPS) measurements were performed on an ESCALAB250 spectrometer.
The atomic resolution scanning transmission electron microscope (STEM) was realized on a JEM-ARM200F equipped with EDS analyzer (200 kV, probe Cs-corrector, 68–174 mrad collection angle for high-angle annular dark field imaging, ~ 0.8 Å spatial resolution). The samples were ground into fine powders, dispersed in ethanol, dropped onto a lacey carbon film-Cu TEM ready grid from TedPella Co., and then dried on a hot plate at 70 °C. STEM images were taken using the high-angle annular dark field detector. Energy-dispersive X-ray spectroscopy (EDS) was measured on an EDS analyzer (JEOL, EX-230 100 m2 detector) equipped on a JEM-ARM200F microscope. The elemental mapping was performed at a sampling resolution of 128 × 128 pixels and a dwell time of 0.1 ms/pixel under multiple frame integration.
Computational methodology
Density functional theory (DFT) calculations were conducted using the Vienna Ab-initio Simulation Package (VASP). The core and valence electrons were described by the projector augmented wave method (Blöchl 1994) and the Kohn–Sham wave functions being expanded in plane wave basis (Kohn and Sham 1965). The energy cutoff was set as 400 eV for all of the calculations. The electronic exchange and correlation were described by a generalized gradient approximation; the functional method developed by Perdew, Burke, and Ernzerhof was chosen for the calculations (Perdew et al. 1996). The Brillouin zone was sampled within a (3 × 3 × 1) k-point mesh using the method developed by Monkhorst and Pack (Monkhorst and Pack 1976). Structures were considered as being optimized after all the forces fell below 0.05 eV per Å.
Photocatalytic tests
Photocatalytic activity of the as-prepared samples was assessed by the photocatalytic degradation of rhodamine B under visible light irradiation, where optical absorption of rhodamine B at 553 nm was used as a major wavelength. In a typical experiment, 20 mg of sample was added into 100 mL of rhodamine B solution, yielding the suspension under stirring in the dark for 0.5 h to reach the adsorption/desorption equilibrium. The suspension was subjected to irradiation by a 500 W Xe lamp at λ > 420 nm under stirring at ambient conditions. At intervals of 0.5 h, 6 mL of the suspension was extracted and centrifuged to remove the photocatalysts. The filtrates were analyzed by recording the UV–vis spectra using a Shimadzu UV-1800 spectrophotometer (Osman et al. 2017). The residual percentage of the rhodamine B is calculated through Ct/C0, where C0 represents the concentration of rhodamine B before the irradiation, Ct represents the concentration of rhodamine B after irradiating time t was utilized to represent the photocatalytic performance of the catalyst.
Results and discussion
Here we studied the phase, morphology, structure, vibrational bands and the specific interactions, surface elemental composition and chemical status of the as-prepared MoS2/tourmaline composites, and the growth mechanism of the composite was raised. Next, the photocatalytic test was carried out and both density functional theory calculations and proposed synergic effects between tourmaline and MoS2 for rhodamine B degradation were used to explain the high catalytic efficiency of the composite.
Morphology observation of the MoS2/tourmaline composite
Scanning electron microscopy images of the as-prepared MoS2/tourmaline composites delineate the overall architectures. For the MoS2/tourmaline samples, MoS2 nanosheets are evenly distributed on the surface of tourmaline particles, displaying a gripping pangolin-like structure (Fig. 1a and Fig. S1). As the synthesis temperature ramps, the coverage of the MoS2 nanosheets over the tourmaline particles increases. As revealed by Fig. 1a, MoS2 nanosheets are consistently grown on the surface of tourmaline particles in the sample prepared at 210 °C. High-resolution transmission electron microscope image (Fig. S2) further shows direct evidence that MoS2 phase has been uniformly loaded on the tourmaline particles, which benefits charge separation during electron transfer (Yin et al. 2017) and catalytic efficiency.
Phase study of the MoS2/tourmaline composite
X-ray diffraction patterns further testified the phases compositions of tourmaline (JCPDS Card No. 43–1464) and 2H-MoS2 (JCPDS Card No.37–1492). As shown in Fig. 1c, the peak of the MoS2 diffraction (002) shifts slightly to a smaller angle, which is probably due to the inhalation of ammonium ions into the MoS2 layers (Wang et al. 2020). Meanwhile, the specific peaks of the tourmaline diffraction shift to larger angles indicating the shrinkage of tourmaline unit cell (Table S1), which is caused by the oxidation of Fe2+ to Fe3+ inside the tourmaline. (Guo 2019). The diffraction peak becomes sharper as the temperature increases, indicating the crystallinity of MoS2 is enhanced (Wang et al. 2014), and the various fabrication times demonstrate a consistent tendency with the temperature change (Figs. S3, S4).
FTIR and X-ray spectroscopy analysis of the MoS2/tourmaline composite
FTIR results (Fig. 1d) identified the functional groups of the tourmaline skeleton, such as the stretching vibration at 3562 cm−1 for O–H, 1266 cm−1 and 1350 cm−1 for antisymmetric B-O, 980 cm−1 for Si–O-Al, 712 cm−1, 780 cm−1 and 1030 cm−1 for Si–O-Si, 491 cm−1, 573 cm−1, and 655 cm−1 for octahedral cation M–O, along with the 470 cm−1 for Mo-S stretching vibration (Luo et al. 2020; Yu et al. 2020; Pramoda et al. 2016). Furthermore, XPS measurements show a significant overall blue shift for MoS2 when assembling on the tourmaline (Fig. S5), indicating the fact of electron transfer from MoS2 to the tourmaline support with the surface electric field (Liu et al. 2015a).
Atomic structural details for tourmaline, MoS2 and their interface
To study the atomic structures of the synthesized MoS2/tourmaline composites, probe aberration-corrected scanning transmission electron microscopy (AC-STEM) was performed (Fig. 2). High-angle annular dark field imaging combined with X-ray EDS was also used to further characterize the morphology of MoS2/tourmaline composite (Fig. 2a), atomic structure details of tourmaline (Fig. 2b, c), and MoS2-tourmaline interface (Fig. 2d). It can be seen that tourmaline structures facilitate a good dispersion of the two-dimensional MoS2 nanosheets (Figs. 1b, 2a). Particularly, this turns to be the first time to directly image the atomic structure of a tourmaline crystal (Fig. 2b), where the atom-coordination details are in good agreement with the ideal structure (Bosi et al. 2005). It proves that tourmaline belongs to the R3m space group with six-membered Si rings, Fe–Mg octahedra, B triangles; structural units linked together by Al octahedra (Bosi and Lucchesi 2007). This unique structure is noncentrosymmetric and polar, the c axis is threefold symmetry, and there is no axis plane of symmetry perpendicular to c and no center of symmetry (Nakamura et al. 1992; Wang et al. 2011). Therefore, tourmaline is usually in the shapes of trilateral and hexagonal column, with properties of far infrared radiation, spontaneous polarization, pyroelectricity, and piezoelectricity (Wang et al. 2019; Chen et al. 2020; Dietrich 1985). Moreover, close examination of tourmaline/MoS2 interface reveals it was the uniform anchor of MoSx clusters on the mineral surface of tourmaline (77\(\overline{3}\)) facets (Fig. 2c) that benefits the uniform growth of MoS2 nanosheets, while these MoS2 sheets are in atomic thickness of only 3–4 layers epitaxially stacking (Zhang et al. 2017b) in a 2H sequence on the mineral surface in relationship of tourmaline (77\(\overline{3}\))||MoS2 (002) (Fig. 2d). Intriguingly, the MoS2 nanosheets evolve into curly and intercross morphology, which according to the microscopy evidence, herein, should be attributed to the intrinsic behaviors of MoS2 layer rolling up during stacking at the tourmaline/MoS2 interface, e.g., in Fig. 2d, the initial MoS2(002) termination rolls up to be MoS2(106).
Proposed growth mechanism of MoS2/tourmaline composite
According to the above structural analysis, the growth mechanism of MoS2/tourmaline composites can be illustrated schematically in Fig. 2e, where Mo and S atoms gradually adhere to the tourmaline followed by the epitaxial growth of MoS2 nanosheets with curly edges on the surface of tourmaline particles. More surprisingly, using the naturally abundant mineral to support highly dispersed MoS2, the fabrication cost has been reduced to be less than one-thousandth of the commercial counterparts (Fig. S6).
Density functional theory calculations
To understand the potential structure–activity relation of MoS2/tourmaline, DFT calculations were performed to study the bandgap and d-band center, i.e., average energy of d-electrons of MoS2 with the number of layer varying from 1 to 4 (Fig. 3).
Interestingly, it can be seen that reducing the thickness leads to a wider bandgap (Fig. 3a), while a monolayer of MoS2 owns the bandgap close to that of optimum for photocatalysis (Liu et al. 2015b). Meanwhile, with a thinner layer of MoS2, there is a significant upshift of the d-band center toward the Fermi level, indicating stronger bond activation capacity for degradation reaction (Li et al 2019). Both these theoretical calculations indicate a significant advantage of using tourmaline for the preparation of MoS2: The use of tourmaline results in a controllable thickness of MoS2, while a thin layer of MoS2 guarantees a better photocatalytic activity.
Photocatalytic performance of the composite toward rhodamine B degradation
Photocatalysis is an effective technology which has been frequently utilized for water splitting and degradation of organic pollutants (Li et al. 2020; Liao et al. 2019; Zhong et al. 2018). The photocatalytic activity of the MoS2/tourmaline composites was evaluated using the rhodamine B degradation as a probe reaction, as shown in Fig. 4. The degradation processes of all the MoS2/tourmaline composites exhibit much higher efficiencies than that, ~ 41.2%, of the pure MoS2 after photocatalytic reaction for 150 min (Fig. 4a). Notably, the T-210 sample reaches the highest degradation efficiency of ~ 93%, roughly 2.3 times the degradation efficiency of the pure MoS2. These numbers suggest that the distinct architecture of the MoS2/tourmaline composite produces much greater photocatalytic degradation efficiency. In addition, the T-220 and T-230 samples exhibit a slightly lower degradation rate than the T-210, which may be due to the agglomeration of MoS2 nanosheets at higher temperature. For all the samples, the changes in the fabrication time (Fig. 4a) and fabrication temperature (Fig. 4b) exhibit similar tendencies.
Comparison of pristine MoS2 and MoS2/tourmaline composite during photocatalysis
Evidently, although the as-synthesized MoS2 microspheres are assembled by MoS2 nanosheets (Fig. 4c), most of them are encapsulated inside of the microspheres, which have little-to-zero access to the visible light irradiation and thus contribute much less to the photocatalytic degradation of rhodamine B compared with the outmost MoS2 nanosheets in the microspheres. In contrast, MoS2 nanosheets in the MoS2/tourmaline composite are highly dispersed, offering much more exposed 3–4 layered ultrathin MoS2 nanosheets with the epitaxial and curly stacking for the photocatalysis process, which enhanced the absorption of photons and the efficiency of charge transfer (Fig. 4c) (Zhou et al. 2019; Dai et al. 2016).
Proposed synergic effects between tourmaline and MoS2 in photocatalytic rhodamine B degradation
Figure 4d further illustrates the synergic effects between the tourmaline and the grown MoS2 nanosheets in the MoS2/tourmaline composite. First, OH is the dominant oxidant for photocatalytic degradation in wastewater treatment, tourmaline can polarize water (Wang et al. 2012) to produce OH− (Eq. 1) and decrease the water association degree on the tourmaline surface (Eq. 2) (Tzeng et al. 2019), thus it can form more •OH species from the oxidation of OH− or H2O via photogenerated holes (Eq. 3). Second, tourmaline, schorl herein, is a natural mineral bearing iron ions, which can catalyze H2O2 that formed in the photocatalytic reaction to produce •OH and •O2− (Eq. 4) (Xu et al. 2010; Wang et al. 2013), the details of the formation of H2O2, as well as its catalytic mechanism, are shown in Fig. S7. Third, the holes show high affinities for the electrons and the high degree of the recombination of the electron–hole pairs is a major limiting factor controlling the photocatalytic efficiency. O2 acts primarily as an efficient electron trap to prevent the recombination of the photogenerated electron–hole pairs, while tourmaline can augment the content of dissolved O2 in water by ionizing water (Eq. 5) (Wang et al. 2013). Fourth, the photo-induced electrons from the MoS2 are adsorbed tightly on the anode of tourmaline due to the ‘electrostatic poles’ on the surface of tourmaline, which prolongs the charge lifetime from MoS2 (Eq. 6) (Yu et al. 2016). Such retardation effect of charge not only results in trapping the charge to suppress the recombination of h+–e– pairs, but also transferring the trapped charges to contact with the reactants (Eq. 7). In the mean time, the remaining holes also migrate outward to form reactive species (Eq. 8). Therefore, the MoS2/tourmaline composite demonstrates much higher photocatalytic activity than that of the pure MoS2 microspheres (Eq. 9). The main steps of the synergistic effects are shown as follows:
In conclusion, the unique MoS2/tourmaline structure with the excellent synergism of tourmaline significantly facilitates photocatalytic degradation compared with the pure MoS2 microspheres.
Conclusion
MoS2 nanosheets with 3–4 atomic layers are uniformly assembled on the tourmaline particles via a facile microwave hydrothermal method. In this new composite architecture, tourmaline carrier is in a form of polyhedron single crystal which supports the epitaxial growth of 2H-MoS2 layers at the tourmaline (77\(\overline{3}\)) facets, while an intrinsic rolling up behavior of MoS2 layer along the support surface from direction [002] to [106] accounts for the structural origin of the overall curly morphology. In a typical photocatalytic application, the as-prepared MoS2/tourmaline has demonstrated considerably enhanced photocatalytic rhodamine B degradation. To the best of our knowledge, this is the first report on the combination of atomically thin two-dimensional MoS2 nanosheets and tourmaline mineral. Density functional theory calculations further showed that thinner MoS2 nanosheets lead to wider bandgap and the upshift of d-band centers, which in turn enhances the photocatalystic activity. This work provides new insights for the low-cost mass production of high-quality, atomically thin two-dimensional materials supported on tourmaline minerals.
Data availability
The data that support the findings of this study are available from the corresponding author upon reasonable request.
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Acknowledgements
This work was financially supported by the National Natural Science Foundation of China (No. 51874115), the Postdoctoral Science Foundation funded project of China (No. 2020T130166), the CAS Youth Innovation Promotion Association (No. 2019190), the Introduced Overseas Scholars Program of Hebei province, China (No. C201808), the Enterprise Science and Technology Commissioner Project of Tianjin City, China (No. 19JCTPJC56100) and the Excellent Young Scientist Foundation of Hebei province, China (No. E2018202241).
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FW and JL conceived and supervised experiments. MH, LC, XX and DW performed experiments. WL and FW performed and analyzed the STEM characterization. HL performed the DFT simulations. FW, WL, BF, MH and LC prepared and revised the manuscript. All authors contributed to the experiments and manuscript preparation.
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Hao, M., Li, H., Cui, L. et al. Higher photocatalytic removal of organic pollutants using pangolin-like composites made of 3–4 atomic layers of MoS2 nanosheets deposited on tourmaline. Environ Chem Lett 19, 3573–3582 (2021). https://doi.org/10.1007/s10311-021-01235-6
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DOI: https://doi.org/10.1007/s10311-021-01235-6