Víctor de la
Asunción-Nadal
a,
Beatriz
Jurado-Sánchez
*ab,
Luis
Vázquez
c and
Alberto
Escarpa
*ab
aDepartment of Analytical Chemistry, Physical Chemistry and Chemical Engineering, University of Alcalá, Alcala de Henares, Madrid, E-28871, Spain. E-mail: beatriz.jurado@uah.es; alberto.escarpa@uah.es; Tel: +34 91 8854995
bChemical Research Institute “Andrés M. del Río”, University of Alcala, Alcala de Henares, Madrid, E-28871, Spain
cMaterials Science Factory, Institute of Materials Science of Madrid (ICMM-CSIC), Cantoblanco, E-28049 Madrid, Spain
First published on 28th October 2019
Tungsten disulfide (WS2)-based micromotors with enhanced electrochemical and photo-catalytic activities are synthesized using a greatly simplified electrochemical deposition protocol at room temperature involving exclusively tungstic acid and sulfate as metal and sulfur sources without further building chemistry. The WS2-based micromotors exhibit dual electrochemical and photo-catalytic behavior in the inner and outer layers, respectively, due to the combination of the unique properties of the sp2 hybridized WS2 outer layer with highly reactive WS2-induced inner catalytic layers, accounting for this material's exclusive enhanced performances. A rough inner Pt–Ni layer allows tailoring the micromotor propulsion, with a speed increase of up to 1.6 times after external control of the micromotor with a magnetic field due to enhanced fuel accessibility. Such a coupling of the attractive capabilities of WS2 with enhanced micromotor movement holds considerable promise to address the growing energy crisis and environmental pollution concerns.
The field of micromotors has only recently started to benefit from the outstanding properties of TMDs. Micromotor design and the synthetic route adopted will exert a strong influence on the overall catalytic performance for each specific application.24–31 Thus, Pumera's group demonstrated the autonomous movement of naphthalene doped MoS2 nanoparticles that can be self-propelled via the combination of self-exfoliation and Marangoni effects.32 Later on, the same group incorporated WS2 nanoparticles onto the surface of polyaniline microrockets via template electrodeposition for on-demand delivery of the capacitive elements.33 TMDs can be used as a scaffold for building more complex structures exploiting their high surface area, as drug carriers or as sensing elements by modifying their surface with fluorescent molecules. Wang's group illustrated the use of template electrodeposited MoS2 micromotors for drug delivery and (bio)chemical sensing.34 In this latter application, their luminescence and photochemical properties make them promising candidates for further development of micromotors. However, despite the outstanding properties demonstrated by such early micromotor proof-of-concept applications, the design and applications of TMD micromotors still remain largely unexplored.
We report here, for the first time, the synthesis and application of micromotors with an in situ room-temperature electrodeposited WS2 external layer with dual “inner and outer” catalytic activities. To this end, we adopt a simplified electrochemical deposition technique at room temperature using tungstic acid and sulfate exclusively as sources for micromotor synthesis. Successful materials synthesis will be illustrated by scanning electron microscopy, atomic force microscopy and Raman characterization. We will also describe the dual “inner and outer” catalytic activities of the micromotors associated with the presence of a high density of edges and inherent photoinduced electron transfer (outer layer) and a rough catalytic patch (inner layer). The rough inner Pt–Ni layer allows tailoring of the micromotor propulsion, with a speed increase of up to 1.6 times after external control of the micromotor with a magnetic field due to enhanced fuel accessibility. The catalytic performance of the micromotors will be also illustrated for future “on-the-move” energy generation schemes. More interestingly, WS2 micromotors possess inherent NIR responsive properties, which will be exploited here for the enhanced removal of a model pollutant dye. Current trends in renewable energy utilization are aimed at the use of solar light for photocatalytic pollutant degradation and hydrogen generation via water splitting. Up to now, UV and visible light-triggered micromotors have been extensively studied for photodegradation processes,35–37 with NIR light only used for enhanced propulsion and triggered drug release schemes.38,39 Unlike such early efforts, the new micromotors described here hold considerable promise for the utilization of solar light for a myriad of renewable energy utilization schemes.
W6+ + 2e− → W4+ |
W4+ + S2− → WS2 |
Next, the effect of WS2 electrodeposition time was evaluated by varying the number of scans from 2 to 50 and using Pt as a second metallic layer. A low content of the material was electrodeposited after 2 scans, which resulted in ill-defined structures that collapse easily. Defined surface morphology and efficient propulsion in peroxide solutions were observed after 10 cycling scans. No noticeable differences were noted by increasing the number of scans; thus 10 scans were selected as optimal. The resulting electrically conductive WS2 continuous film provides an ideal template for the electrodeposition of magnetic (Ni) and catalytic (Pt) layers for further functionalization and autonomous movement in the intended applications, as will be described later.
To further support the proposed electrodeposition mechanism, Raman characterization was carefully performed. The WS2 crystalline structure is characterized by a trigonal prismatic arrangement of S–W–S atoms in which each plane contains a trilayer composed of an individual tungsten layer, sandwiched between two sulfur layers in trigonal prismatic coordination. Thus, such a structure displays characteristic optical phonon modes at the Brillouin zone center: E12g (in-plane optical mode), A1g (out-of-plane vibration of the sulfur atoms) and LA(M) (longitudinal acoustic mode at the M point or in-plane collective movements of the atoms in the lattice).40 The Raman spectra in Fig. 1C display the above-mentioned peaks: LA(M) at 330 cm−1, E12g at 350 cm−1 and A1g at 410 cm−1. According to the literature, this might be an indication that the material is present in the film as a mix of monolayer and bilayer structures.41 Overall, the Raman profile indicates the successful formation of the WS2 outer layer of the as-synthesized micromotors. This is fully supported by the energy-dispersive X-ray (EDX) spectroscopy mapping in Fig. 1D, which illustrates a uniform distribution of W and S along the resulting microtubes, with an inner Pt–Ni metallic layer. Top and cross-view scanning electron microscopy (SEM) images in Fig. 1E reveal the well-defined conical structure of the micromotors with a thin outer WS2 layer composed of granular particles with an average diameter of ∼190 nm. The geometry of the micromotors was characterized by observation of the SEM images of 50 micromotors. The average length was 11.4 ± 1.1 μm, with a thin outer Ni–Pt layer with an average thickness of 0.41 ± 0.24 μm and an average inner opening of 4.6 ± 0.3 μm. The micromotors are considered cylindrical, with two openings with radii Rj. For comparison, Fig. 1F displays the SEM images of MoS2 micromotors prepared using a similar procedure to that described by Wang's group.34
Interestingly, the observed granular structure of the catalytic layer of the as-synthesized micromotors in Fig. 1E (associated with the roughness of the WS2 layer) has a strong influence on the propulsion performance and catalytic activity of the inner layer (see Fig. 2). The inner catalytic Pt layer triggers the decomposition of the peroxide fuel, releasing oxygen bubbles from one side of the micromotors, which reached average speeds of 94 μm s−1 (0.5% H2O2) and 179 μm s−1 (1% H2O2). This speed is higher than that observed for WS2NPs–PANI/Pt and PANI/Pt micromotors, which propel at speeds of 71 and 39 μm s−1 (1% H2O2).33 Higher speeds were obtained for MoS2/Pt micromotors (370 μm s−1, 1% H2O2).34 However, it is worth noting here that the inclusion of Ni magnetic layers results in the decrease in the speed compared to the case where a Pt layer is included. To check this assumption, we prepared MoS2 micromotors with a Ni layer, and the speed decreased to 80 μm s−1 (1% H2O2). Compared with magnetic carbon-based nanomaterials containing a similar Ni layer, the speed of the WS2 micromotors was similar to that observed for micromotors containing carbon black (90 μm s−1) as the outer layer but slightly lower than that of multiwalled carbon nanotube based micromotors (200 μm s−1) propelling in 1% peroxide solution.42 As the micromotor contains an inner Ni layer, propulsion can be improved by the application of external magnetic fields. Interestingly, as displayed in Fig. 2A, at low peroxide levels (0.5 to 1%), the speed increases up to 60% after external control of the micromotor with a magnetic field. The corresponding time-lapse images are depicted in Fig. 2B. We attribute such a phenomenon to better fuel accessibility towards the catalytic layer, due to the specific orientation induced with the magnet, resulting in a larger exposed area for enhanced fuel decomposition. To check that such different speeds attributed to the motion in the linear and circular ways is not caused by different drag forces applied on the different part of the tubes, we studied a total of 50 micromotors in both modes and found a similar trend with no statistical differences. Numerical simulations (not shown) illustrate how the application of magnetic fields results in an increase of the overall speed, mainly due to a change in the flow regime (from turbulent to laminar) and better fuel accessibility. This increases the residence time and improves the contact of the fuel with the catalyst, resulting in a higher oxygen generation rate and an increase in the capillary force exerted by the generated bubbles. The effect is more pronounced as the level of fuel decreases. Yet, under unguided conditions, the fuel–inner wall contact is hindered, resulting in lower speeds. A similar behaviour was observed for MoS2/Ni/Pt and PEDOT/Ni/Pt micromotors. Thus, the speed of MoS2 and PEDOT based micromotors increased from 210 and 82 μm s−1 in non-magnetic mode to 265 and 140 μm s−1 in magnetic mode (from 1.3 to 1.6 times), similar to that observed for the as-synthesized micromotors. The numerical simulations describing such phenomena have been very recently described by our research group.43 From the above mentioned, it can be concluded that WS2 does not influence the peroxide decomposition activity. Yet, it can indirectly affect it by imparting an increased surface roughness to the inner Ni and Pt layers, as reflected by the increased speeds. This finding holds considerable promise for “on-demand” regulation of the micromotor movement. The efficiency of the micromotors under each condition (guided and unguided) was calculated (at 1% peroxide levels) following the model described by the Mallouk group.44 The efficiency of WS2 micromotors was found to be 2.40 × 10−7 and 2.60 × 10−7 in bubble and catalytically induced magnetic mode, respectively (see Table S1†). Such an efficiency is much higher than that previously reported for Pt-based tubular rolled-up micromotors (2.40 × 10−10, 3% H2O2)45 or even higher than that of C60 fullerene/Pt (1.44 × 10−7, 1% H2O2) and carbon-black–Pt (1.02 × 10−7, 1% H2O2) micromotors with a similar surface roughness and slightly lower than that of carbon nanotubes and graphene/Pt-based micromotors (from 3.28 to 4.92 × 10−7).46
Fig. 2 Tailored propulsion of WS2/Ni/Pt micromotors. (A) Speed dependence on peroxide concentration both in the absence (“bubble-mode”) and presence (“magnetic mode”) of a magnetic field. (B) Time-lapse images (taken from Video S1†) of micromotor propulsion at different peroxide concentrations in “bubble-mode” (absence of a magnetic field, top part) and “magnetic mode” (bottom part). Scale bars, 10 μm. Note the different lengths of the scale bar in the “bubble-mode” and “magnetic mode” images, which shows the longer trajectories for the latter case. |
The outer morphology and surface roughness of the WS2 micromotors were then characterized by atomic force microscopy (AFM). The topographical AFM images in Fig. 3A illustrate the rough and jagged outer morphology of WS2 based micromotors (mean roughness value = 28 nm), with a granular peak-and-valley type structure, with valleys indicated in blue-green color and protrusions in orange color. For comparison, we include similar TMD based control MoS2 (mean roughness value = 4.2 nm) micromotors, which interestingly are relatively smooth in comparison with WS2 ones (note the different vertical scales). Thus, the resulting outer exposed surface area possesses a high density of edges that are potential active sites, which can be very relevant for achieving enhanced electrochemical performance and sensing. Accordingly, in order to obtain further insights into the catalytic properties of the outer WS2 layer of the as-synthesized micromotors, we explore its potential for the hydrogen evolution reaction (HER). To this end, we modified different electrodes with WS2/Pt and MoS2/Pt control microtubes (indeed, since they are a static control, here they act as microtubes only). First, Nyquist plots in Fig. 3B illustrate that a lower charge transfer resistance was obtained for WS2 microtube electrodes (Rs = 302 Ω) as compared with MoS2 microtube electrodes (Rs = 350 Ω), indicating superior conductivity. Then we carried out HER measurements in 0.5 M H2SO4 using a standard three electrode configuration (for more details, see the Experimental section in the ESI†). For comparison, polarization curves of Pt and bare electrodes are also included, yielding similar values to those reported in the literature.47 The linear sweep voltammograms (LSVs) in Fig. 3C illustrate that the current response of WS2/Pt and MoS2/Pt at similar onset potentials toward hydrogen evolution (2H+ + 2e− → H2) was greater than that of bare surfaces, although so far from that of Pt, as expected. Interestingly, such a result indicates that the inner catalytic layer in the WS2 microtubes still retains its catalytic properties for HER-based applications, holding considerable promise to reduce the high cost of such catalysts in these applications. Indeed, the high catalytic activity of WS2 microtube-supported platinum reflects the synergetic effect of the hybrid nanostructure, in which Pt provides highly active hydrogen adsorption sites and facilitates the charge transfer process for H+ reduction.48,49
The rich outer surface chemistry and the inherent photocatalytic properties of WS2 based micromotors were also exploited for “on the fly” NIR degradation of pollutants. First, the bandgap energy of the as-synthesized micromotors was investigated from the plot of (αhν)2vs. hν by extrapolating the linear portion of the plot to the X axis (see Fig. 4A) and was found to be ∼1.2 eV. Previous studies have reported that layered WS2 structures display NIR activity associated with the indirect bandgap (1.20–1.39 eV) coupled with its high valence band (1.17 eV vs. NHE).7,50 Thus, the micromotors possess a relatively high NIR photocatalytic activity which can be activated upon irradiation with wavelengths from 700 to 1000 nm (which correspond to photon energies from 1.77 to 1.24 eV). Upon interaction with NIR light, an electron (e−) will be promoted from the valence band to the conduction band in the WS2 outer micromotor layer; creating a hole (h+) in the valence band. The WS2 film promotes the rapid transfer of such electrons, inhibiting the recombination of photogenerated electron–hole pairs. The photogenerated electrons (e−) reduce adsorbed O2 molecules to generate O2− radicals, whereas the holes (h+) in the valence band oxidize surface-absorbed water to produce OH− radicals.51 Such photogenerated radicals along with the holes (h+) contribute to the photocatalytic degradation of dye pollutants and other organic compounds, as described in Fig. 4B. Such a fact holds considerable promise for novel environmental degradation mechanisms and for “on-the-move” water splitting applications.52
To further prove the concept and the NIR light photocatalytic activities of the as-synthesized WS2 micromotors, we examined their ability for the degradation of the model pollutant Remazol Brilliant Blue R (RBB). To this end, we designed a photocatalytic chamber (see the Experimental section for more details and a picture) integrating a 50 W NIR lamp with maximum emission at 800 nm. We first studied the effect of pH on the rate of photocatalytic degradation. Thus, 1 mL of water samples at different pH values contaminated with RBB (Co = 35 mg L−1) was adjusted to the desired pH and added to a microcentrifuge tube containing the micromotors (2.5 × 105 micromotors per mL), 1% SDS and 1% H2O2. Next, the tube was placed in the photocatalytic chamber for 120 min. The extent of RBB degradation was monitored by the decrease in its typical absorbance peak at 590 nm. As shown in Fig. 4C, pH 3 was optimal for degradation, with the highest degradation rates. At acidic pH, RBB is present in the anionic form, whereas the excess of H+ ions in solution induces a positive charge on the catalyst/micromotor surface. Thus, RBB adsorbs on its surface, where the positive holes (h+) can directly oxidize it. Furthermore, e− can oxidize the oxygen adsorbed on the surface of the micromotors and promote the formation of radicals, resulting in additional RBB degradation.53 We next evaluated the effect of time and the number of micromotors upon degradation. Degradation rates increase as the number of motors and time increase up to 5 × 105 micromotors per mL (which corresponds to 288 μg of micromotors) and 120 min, respectively, then reaching a plateau. Under the optimized conditions, several control experiments were performed. Remarkably low (30%) or negligible degradation rates were obtained using either static micromotors upon NIR light irradiation (in the absence of peroxide fuel) or magnetically stirred micromotors. We also evaluated the effect of pristine WS2 on micromotor degradation under the same conditions evaluated for the moving micromotors. The bandgap of such a material ranges from 1.4 to 2.0 eV. Commercial nanoparticles have a diameter of 90 nm (for additional SEM morphology, see Fig. S4†). As can be seen in Fig. 4D, degradation rates of 48 and 20% were obtained with and without NIR light irradiation, respectively. Such percentages are much lower than those obtained for moving micromotors but slightly higher than those observed for static micromotors. Such differences may arise from the difficulties in using the same amount of micromotors/particles. Yet, overall, such results reveal the inherent photocatalytic properties of the as-synthesized micromotors under NIR light irradiation and the crucial role of micromotor movement upon enhanced fluid mixing in improved degradation efficiencies. Additional control experiments were performed to address the role of peroxide and potential induced thermal effects in RBB degradation. To check the influence of H2O2 on RBB degradation, we performed control experiments in solutions containing the dye, 5% SDS, 1% H2O2 and Pt nanoparticles in the absence and presence of light. Negligible degradation was noted in all cases, revealing the negligible effect of peroxide on RBB degradation. Additionally, experiments were also conducted in the absence of Pt nanoparticles, with negligible degradation rates (not shown). In the case of Pt nanoparticles (which do not contain a bandgap for subsequent radical generation) negligible degradation was noted both in the presence and absence of light, indicating also the negligible effect of the local temperature on the degradation efficiency. UV-vis spectra in Fig. S3† clearly show the decrease of the 590 nm peak intensity with time. In the by-product spectrum, the 630 nm peak disappears, which, along with the red-shift and band broadening, indicates the breakup of the highly conjugated RBB system. Data were further processed under pseudo-first-order and pseudo-second-order degradation kinetic models (see the Experimental section for more details). As can be seen in Fig. S5,† RBB photocatalytic degradation obeys first-order kinetics, characterized by the Langmuir–Hinshelwood model (saturation kinetic mechanism). The slope of the plot of ln(C0/C) vs. time is 0.020 min−1, which is 2-fold higher than that reported for pristine WS2 (0.010 min−1) and 6-fold higher than that of WS2@MoS2 (0.0030 min−1), indicating the superior photocatalytic performance of the as-synthesized micromotors.54 Finally, the magnetic properties of the as-synthesized micromotors allow for complete recovery after solution treatment for subsequent reusability. Excellent performance is observed in the reusability test during four consecutive cycles, with almost 100% degradation rates in all cases.
Pseudo-first-order kinetics were calculated according to the equation:
Pseudo-second-order kinetics were expressed as:
C o and C are the concentration of each pollutant in solution initially and at any time t, respectively. V is the volume of the solution (1 mL) and m is the mass of micromotors used (280 μg). The model was evaluated by plotting t/q2versus time.
Footnote |
† Electronic supplementary information (ESI) available: Supporting tables and figures and Video S1. See DOI: 10.1039/c9sc03156a |
This journal is © The Royal Society of Chemistry 2020 |