Abstract
Ni(OH)2 doped with cerium cations was synthesized by a hydrothermal method and its electrochemical, photoelectrochemical and photocatalytic behavior was determined by the corresponding suitable techniques. Ni(OH)2 films doped with different Ce proportions were evaluated in a KOH support electrolyte solution by cyclic voltammetry. Scan-rate dependent voltammograms displayed pseudo-capacitive behavior while the charge transfer resistance of Ce-doped samples was determined through electrochemical impedance spectroscopy. The calculated charge transfer resistance value was 132 Ω for Ni(OH)2 containing 350 μmoles of Ce. Chronoamperometry under intermittent UV light was employed to measure the photo-response of nanomaterials. The experimental results indicated that the photocurrent of Ni(OH)2 containing 350 µmoles of Ce was ten times greater than that of pure Ni(OH)2. Photocatalytic activity of the powders was demonstrated under UV light irradiation accomplishing 83% of methyl orange degradation after 140 min of reaction with pseudo-first-order kinetics and the calculated degradation rate constant was 0.0125 min− 1. The results evidenced the electrochemical, photoelectrochemical and photocatalytic activity of the synthesized materials, which sets them as suitable materials for a wide range of promising photo-based applications.
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1 Introduction
Metal-oxide and hydroxide-based semiconductor materials became popular in several water purification methods such as photocatalysis due to their excellent physical and chemical properties. These materials have also been considered for promising electronic and optoelectronic applications, where MnO2 [1, 2], RuO2 [3], NiO [4, 5], Co(OH)2 [6] and Ni(OH)2 [7, 8] are some semiconductor materials that have been reported in the literature. From these examples, Ni(OH)2 is particularly appealing because it is a low-cost material that can be produced by different methods [9,10,11,12], has unique electrochemical properties [13] and is environmentally friendly [14]. Ni(OH)2 has had different applications like in the catalytic degradation of nitrite and nitric oxide [15], the photocatalytic degradation of organic compounds under visible light [16], super capacitor electrodes [17] and photoelectrodes [18].
In order to improve the catalytic and electrochemical activity of Ni(OH)2 [14], selective ion doping has been employed because of being one of the most effective methods for this purpose. In this context, lanthanide ions have been reported as ideal dopants in works such as those by K. T. Ranjit et al., who tested the effective lanthanide-oxide-doped-titanium dioxide in the degradation of salicylic and t-cinnamic acids [19], C. Fu et al., who decreased the TiO2 band gap by incorporating Ce [20] and P. Muthukumaran, who confirmed that Ce-doped NiO nanomaterials exhibited excellent performance in the detection of riboflavin [21]. From these ions, Ce stands out due to the availability of the Ce3+/Ce4+ redox pair and the different electronic structures between Ce3+ (4f15d0) and Ce4+ (4f05d0) that can provide different optical, catalytic and electron transfer properties [22, 23].
Thus, it is interesting to explore the properties of Ni(OH)2-based materials doped with Ce in order to find out novel applications. This work reports the sustainable synthesis and characterization of Ni(OH)2 doped with Ce. The electrochemical properties of the nanomaterials were determined by cyclic voltammetry and electrochemical impedance. Additionally, the Ce-doped Ni(OH)2 nanomaterials were used as photoelectrodes to evaluate the photo-response under UV-light, which allowed to determine the impact of Ce doping on the photoelectrochemical behavior. Finally, the photocatalytic activity of the Ce- doped Ni(OH)2 nanomaterials was tested in the degradation of the dye methyl orange (MO).
2 Experimental
2.1 Materials
Only analytical-reagent-grade chemicals were acquired. Nickel sulfate (II) hexahydrate and sodium hydroxide were purchased from Sigma-Aldrich; cerium(III) nitrate hexahydrate (Alfa-Aesar, 99.99%), methyl orange (JT Baker), KOH (Sigma-Aldrich) and ultrapure water (supplied by a MilliQ water system) were also used.
2.2 Synthesis of Ni Hydroxide Structures
The synthesis of nickel hydroxide (Ni(OH)2) nanostructures was performed by a hydrothermal method using microwave heating. The precursor solution was prepared by dissolving 7.038 g of nickel sulfate in 70 mL of 7.0 M NaOH; the solution was kept under vigorous stirring for 1 h at 700 rpm.
To obtain Ni(OH)2 doped with different Ce proportions, appropriate amounts of cerium nitrate were dissolved in 30 mL of water to obtain 214, 350 and 710 µmoles of cerium in the samples. The solutions were added dropwise to the precursor solution (Ni(OH)2) under constant stirring, and finally, they were sonicated for 5 min to ensure complete dissociation. The mixtures were transferred to a Teflon reactor, put into a microwave synthesizer (Eyela MWO-1000 Wave Magic) and heated at 120 °C for 4 h. After this time, pale green precipitates were obtained and washed with distilled water and ethanol several times. The final material was recovered using a rotary evaporator at 80 °C. Finally, the powders were dried at 80 °C for 12 h in an oven and then treated thermally at 200 °C for 2 h in order to remove precursor remnants. The obtained products were labeled as Ni(OH)2–Ce1, Ni(OH)2–Ce2 and Ni(OH)2–Ce3, which contained 214, 350 and 710 µmoles of Ce, respectively, and compared with pure Ni(OH)2.
2.3 Characterization and Measurements
The as-obtained catalysts were examined with an X-ray diffractometer Rigaku D/Max 2200 h with CuKα irradiation (λ = 1.5406 Å) operated at 40 kV and 40 mA throughout an interval ranging from 10° to 70° (XRD). The Brunauer-Emmett-Teller (BET) specific surface areas of the sample powders were obtained by nitrogen adsorption-desorption, measured on a Nova 3200 gas-sorption system. The pore size distribution was collected by the Barrett-Joyner-Halenda (BJH) method. Ultraviolet-visible (UV-vis) absorption spectra were surveyed using a UV-vis NIR spectrometer (Agilent Cary 5000). Fourier transform infrared spectra (FTIR) were collected by means of a Shimadzu IRTracer-100 spectrophotometer within an interval ranging from 4000 to 400 cm− 1. The morphologies of the prepared samples were obtained by scanning electron microscopy (SEM, Helios double beam 600 high resolution) with an operating voltage of 5 kV.
The electrochemical analysis was performed in a conventional three-electrode system using a potentiostat-galvanostat (BioLogic VSP-300) controlled by the EC-Lab software. The working electrode was fabricated from a suspension of 5 mg of photocatalyst sample in 1 mL of deionized water, which was sonicated for 10 min; then, 100 µL were spread on a clean indium tin oxide (ITO) glass substrate (active area of 2.8 cm2) and allowed to dry at room temperature. A platinum wire and Ag/AgCl 3 M electrode were used as auxiliary and reference electrodes, respectively. 0.1 M KOH was used as supporting electrolyte solution. The cyclic voltammetry measurements were performed throughout a potential interval ranging from 0.0 to 1.0 V, varying the scan rate from 5 to 100 mV s− 1. All electrochemical impedance spectroscopy (EIS) experiments were performed between 1 MHz and 0.1 Hz with excitation signal amplitude of 10 mV. The measurements were made under potentiostatic control applying the open circuit potential. The parameters of the equivalent circuits were obtained through the Z-fit program. The photocurrent measurements of the photocatalysts were examined by the chronoamperometry technique both in the dark and under UV light irradiation (λ = 254 nm) applying a constant potential of 0.7 V in the 0.1 M KOH solution and using the same three-electrode cell described above. Data were recorded at intervals of about 50 s by turning on and off the light source.
The photocatalytic activity of Ni hydroxide structures was evaluated through the photodegradation of MO. 0.025 g of each photocatalyst was suspended in 100 mL of dye solution (concentration = 10 mg mL− 1). The suspension was stirred in the dark for 60 min in order to reach adsorption-desorption equilibrium. Subsequently, the solution was irradiated with a UVP mercury pen lamp (λ = 254 nm) positioned in the center of the reactor under continuous stirring. The dye degradation rate was monitored by taking a 3-mL sample every 20 min; the photocatalyst was removed from the rest of the solution by centrifugation at 3800 rpm and then, the supernatant was analyzed by means of a UV-vis NIR spectrophotometer (Agilent Cary 5000) to determine the MO concentration reading at 464 nm.
3 Results and Discussion
3.1 Optical and Morphological Characteristics
The FTIR analysis of the synthesized nanomaterials gave insights into the composition of the surface chemical functional groups of the products. The FTIR spectra of the nanomaterials within the 400–4000 cm− 1 interval are shown in Fig. 1 and the presence of seven important transmittance bands is observed at 432, 509, 1375, 1427, 1546, 1631 and 3630 cm− 1.
The narrow band located at 3630 cm− 1 is attributed to hydroxide O-H stretching of the Ni(OH)2 nanomaterial structure [24] while the band at 1631 cm− 1 corresponds to the H-O-H bending mode of adsorbed water from the environment [25, 26]. Weak bands located between 1500 − 900 cm− 1 are due to intercalated carbonate and nitrate groups whereas the weak band near 1427 and 1375 cm− 1 corresponds to the bending vibration of ionic CO32− originated from the reaction of the samples with ambient CO2 [27]. The bands at 432 and 509 cm− 1 were assigned to the stretching vibration mode of Ni-O [28]. This result is clear evidence of the presence of nickel hydroxide crystals. The incorporation of Ce cations has no effect on the hydroxide structure.
The XRD patterns of the undoped Ni(OH)2 and other Ce-doped solids treated thermally at 200 °C are shown in Fig. 2. It can be seen that crystalline nickel hydroxide has a hexagonal structure and beta phase (JCPDS 014–0117).
The XRD patterns of the materials with Ce loadings of 214 and 350 µmoles show XRD peaks at around 28.6 from 2 theta. The small peak can be ascribed to the cubic-fluorite-type structure of CeO2 (JCPDS 00-004-0593). Thus, it is possible to assume that Ce ions can be incorporated into the Ni(OH)2 framework, favoring the formation of NiO and OH groups identified by FTIR. On the other hand, highly dispersed CeO2 nanoparticles can be formed on the Ni(OH)2 surface, since the peak for cerium oxide is observed. Furthermore, it can be seen that the peaks for the doped samples are less intense and wider than those of Ni(OH)2, which can be possibly due to the incorporation of Ce causing tension between the layers. The peak 001, related to the distance between layers, is clearly an example of the aforementioned [29].
The N2 adsorption-desorption isotherms for the undoped and Ni(OH)2-Ce2 materials are presented in Fig. 3. The surface area stands from 18 to 57 m2/g− 1 for Ni(OH)2 and Ni(OH)2-Ce2 respectively, where the effect of cerium incorporation is the increasing surface area. With 710 moles of cerium, the surface area decreased 2 m2/g− 1 approximately (data not shown). The adsorption-desorption isotherms were analogous and dependent on the amount of doped cerium. Thus, the samples are mesoporous materials represented by a type IV isotherm with slight H1 hysteresis loops according to the BDDT classification. The incorporation of cerium promoted the mesoporous texture in the hydroxide, thus facilitating the diffusion of molecules.
The optical absorption property of nanomaterials can significantly estimate their photo-response range. Absorbance spectra were obtained using a reflectance diffuse sphere system. The diffuse absorbance spectra of Ni(OH)2, Ni(OH)2–Ce1, Ni(OH)2–Ce2 and Ni(OH)2–Ce3 are shown in Fig. 4a. For all the samples, two adsorption bands located between 300 and 800 nm are observed, corresponding to the d–d transitions of the NiII cations [30]. It can also be seen that with the addition of Ce, the absorption band centered at around 300 nm is slightly red-shifted, also showing that the absorption intensity of the Ni(OH)2–Ce samples is greater than that of pure Ni(OH)2 in the UV region. This result indicates that the light absorption capacity is increased by doping with Ce; therefore, the samples are suitable for the absorption of UV photons. The absorption edges of Ni(OH)2 appear at 475 nm while Ni(OH)2–Ce1 absorbed at 500 nm, Ni(OH)2–Ce2 at 550 nm and Ni(OH)2–Ce3 at 515 nm, corresponding to the minimum energy required for photoactivation.
The Eg values obtained for the studied samples were as follows: Ni(OH)2 = 2.61 eV, Ni(OH)2–Ce1 = 2.48 eV, Ni(OH)2–Ce2 = 2.25 eV and Ni(OH)2–Ce3 = 2.4 eV. These results indicate that by increasing the amount of Ce, the Eg is extended to the visible region. The charge transfer between the Ni(OH)2 conduction band and the 4f orbitals of Ce4+ lowers the band gap energy of the samples; the same behavior is observed for Ni(OH)2-Ce1 and Ni(OH)2-Ce2. However, Eg for Ni(OH)2–Ce3 was increased and this effect may be induced by an increase in the electron concentration since a rise above the critical concentration allows partial filling of the conduction band, which in turn blocks the lower energy states and therefore widens the bandwidth [31].
UV-vis spectra of the films formed on the conductive glasses were obtained, Fig. 4b, and the absorption edges are similar to the one obtained from the powder samples. These are 405, 440, 565 and 560 nm for Ni (OH)2, Ni (OH)2–Ce1, Ni (OH)2–Ce2 and Ni (OH)2–Ce3, respectively. The shift in absorption edges may be due to a slight change caused by having the material as a film on the conductive glass. The Eg values calculated for the films were the following: Ni(OH)2 = 3.06 eV, Ni(OH)2–Ce1 = 2.81 eV, Ni(OH)2–Ce2 = 2.19 eV and Ni(OH)2–Ce3 = 2.21 eV. These results indicate that the materials immobilized on the conductive glass displayed a behavior pattern that was similar to that of powder samples.
3.2 Electrochemical Properties
3.2.1 Cyclic Voltammetry
Figure 5 shows the cyclic voltammograms of Ni(OH)2 and the Ce-doped Ni(OH)2 films at different scan rates (100 to 5 mV s− 1). The scan was performed using a potential window from 0 to 1.0 V. Anodic and cathodic peaks located at 0.94 and 0.63 V, respectively, were observed for Ni(OH)2 and they can be attributed to the following electrochemical reaction [32, 33]:
Interesting information can be extracted from voltamperograms. Firstly, the shapes of the voltammetry curves of the Ni(OH)2 and Ce-doped Ni(OH)2 films were similar and exhibited characteristics of pseudo-capacitive profiles, very different from the capacitance of the double layer in which the shape is normally close to an almost symmetrical rectangle [33].
Secondly, the calculated difference between the anodic and cathodic peak potential is 310 mV for a scan rate = 100 mV s− 1, which is greater than the theoretical value of 59 mV; this result indicates that the redox reaction is quasi-reversible. The Ipc/Ipa ratio at 5 mV s− 1 was close to 1, indicating that the system has some degree of reversibility at low scan rates.
Thirdly, it was observed that as the scan rate increased, the current of the anodic and cathodic peaks increased too, which demonstrates the pseudo-capacitance characteristics of the samples while the peak shape is similar to each other. On the other hand, the peak potential was shifted slightly in anodic and cathodic directions, respectively, due to the increase in polarization at high scan rates, resulting in a decrease in capacitance when increasing the scan rate [13].
In addition, the Ni(OH)2-Ce2 film presented more intense redox peaks than all the other samples, indicating that the presence of 350 µmoles of Ce increased the conductivity of the material; therefore, this sample has improved electrochemical activity. This behavior may be related to the fact that Ni(OH)2–Ce2 has a greater surface area and thus more active sites available for redox reactions to take place.
3.2.2 Electrochemical Impedance Spectroscopy
Electrochemical impedance measurements were made for all the films applying an open circuit potential. The results are shown in Fig. 6, where Z’ and Z” are the real and imaginary parts of the impedance, respectively. For all the films there are two regions that depend on the frequency range, where in high frequency regions a small semicircle and a line in low frequency regions are observed. Generally, the semicircle reflects the impedance of the film electrochemical reaction and the line slope in the low frequency region represents the diffusive resistance (Warburg impedance), resulting from the diffusion of the OH− ions from the bulk solution to the electrode surface [34]. The more vertical the line, the closer the material is to the ideal capacitor behavior [35]. The shape of the spectra obtained in the present work is similar to those obtained for other Ni(OH)2-based materials [17]. According to Fig. 6, the Ni(OH)2–Ce3 film had a larger arc, which means a greater charge transfer resistance [36]; this fact was verified by calculating the charge transfer resistance (Rct) through the spectra shown in Fig. 6 using the Zfit software. In the inset of Fig. 6, the equivalent circuit used in the impedance spectral adjustment procedure is shown, where Rs and Rct correspond to the resistance of the supporting electrolyte and the charge transfer, respectively; Cdl is the double layer capacitance and W is the Warburg impedance. The value of Rs remained practically constant for all the samples between 22.4 and 31.03 Ω while the calculated values of Rct were 141.7, 143.9, 132 and 178.8 Ω for Ni(OH)2, Ni(OH)2–Ce1, Ni(OH)2–Ce2 and Ni(OH)2–Ce3, respectively. Since the Ni(OH)2–Ce2 film had lower Rct, it can be inferred that Ni(OH)2–Ce2 presented a greater reaction surface than the other samples and it was more suitable for charge transfer and OH− transfer and diffusion into redox active sites. For these reasons, the film increased reactivity and reaction kinetics.
This result is consistent with those observed by cyclic voltammetry. The calculated values of Warburg impedance were 1203, 987.4, 670.4 and 1061 Ω s− 0.5 for Ni(OH)2, Ni(OH)2–Ce1, Ni(OH)2–Ce2 and Ni(OH)2–Ce3, respectively, meaning that the Ni(OH)2–Ce2 film presents less resistance to the diffusion of OH− ions within the material pores. Warburg impedance contributes a little to the total impedance, which indicates good contact between the supporting electrolyte ions and the Ni(OH)2–Ce2 material.
3.3 Photoelectrochemical Properties
To further investigate the separation and efficiency of the electrons and photo-generated holes in the Ni(OH)2, Ni(OH)2–Ce1, Ni(OH)2–Ce2 and Ni(OH)2–Ce3 samples, photocurrent measurements were made in a three-electrode system in the dark and under UV light illumination (254 nm), applying a constant potential of 0.7 V; this potential was selected because according to the cyclic voltammograms, there is no interference in the redox reaction at this potential. It is widely known that the diffusion of photoexcited electrons and the collection of photoinduced holes in the electrolyte can generate a photocurrent [37, 38]. The photocurrent-time profiles during five on-off cycles are shown in Fig. 7. The photocurrent response of Ni(OH)2 is minimal (0.09 µA) while the Ce-doped samples reached higher photocurrent levels, suggesting that cerium acts as a charge separator, thus decreasing the recombination. The increasing behavior in the anodic current observed in this work is similar to that of other NiO-metal-based materials [39,40,41,42].
The Ni(OH)2-Ce2 film showed higher photocurrent than all the other samples (0.93 µA); as the light was turned on, a rapid current increase was observed, which remained constant until the light was turned off; afterwards, drastic decay occurred. The changes in currents are almost vertical, which indicates that the charge transport rate in the synthesized catalysts was very fast. It is worth mentioning that the photoelectrochemical response shows good stability and reproducibility. This result indicates that the Ni(OH)2-Ce2 sample showed greater separation efficiency and lifetime of photogenerated holes and electrons. Photocurrent values achieved with the Ni(OH)2-Ce2 film are similar to those reported by other authors [40, 43,44,45,46,47]. Particles with higher surface area can increase the contact area with light, which is also consistent with the higher surface area of Ni(OH)2-Ce2.
These results are a precedent for the possible use of Ni(OH)2-Ce2 as photoelectrode in solar cells, UV photosensors or in optoelectronic devices [48,49,50].
3.4 Photocatalytic Activity
Photodegradation of MO under UV light (254 nm) was performed in order to investigate the photocatalytic activity of the samples. The comparison between the photocatalytic activities of Ni(OH)2 with different proportions of Ce is shown in Fig. 8. Initially, photolysis experiments were performed by irradiating a MO solution in the absence of catalyst. After 140 min of reaction, 31.8% of MO was degraded, where high energy UV irradiation is responsible for the photolysis of MO [51, 52].
When degradation occurred using the prepared nanomaterials, it was found that the efficiencies of the photocatalytic degradation of MO were improved to 73.70, 74, 83 and 68.4% for Ni(OH)2, Ni(OH)2–Ce1, Ni(OH)2–Ce2 and Ni(OH)2–Ce3, respectively; which is two times higher than photolysis. It was found that Ni(OH)2–Ce2 had the highest photocatalytic activity, which is in good agreement with what was observed in the photoelectrochemical tests. It is important to emphasize that the possibility of some MO adsorption taking place on the photocatalyst was evaluated, finding that adsorption was negligible.
This result confirms that Ce-doped materials favor the photocatalytic activity possibly because: (1) higher surface area provides more active sites for photocatalytic degradation and (2) the presence of Ce favors the absorption of photons, which can facilitate the generation of electron-hole pairs.
The degradation kinetics of MO was analyzed by a pseudo-first-order kinetic model:
where C and C0 are the concentrations at time t and time 0, respectively, and k is the degradation rate constant [52]. As shown in Fig. 9a, the plot -ln (C/C0) vs. time shows good linearity (R2 > 0.98), indicating that photodegradation of MO using the synthesized materials follows pseudo-first-order kinetics. From the slope of this graph, the degradation rate constants (k), Fig. 9b, were obtained, finding that degradation was carried out faster with the Ni(OH)2–Ce2 photocatalyst with k = 0.0125 min− 1. This value is similar [53,54,55,56] and sometimes better than the ones reported in the literature [57,58,59], having the advantage that in this work, only 0.25 mg mL− 1 of catalyst were used while others required from 1.0 to 1.5 mg mL− 1 of catalyst [53, 54, 56]. These results demonstrate the feasibility of using Ce-doped Ni(OH)2 materials for colored wastewater purification.
To understand the behavior of the most active material, SEM and TEM images were obtained for the undoped Ni(OH)2 and Ni(OH)2-Ce2 materials, Fig. 10. Both samples display laminar morphology with different sizes and thickness. The incorporation of cerium to the nickel hydroxide crystals allows the formation of thinner smaller platelets. The doped materials offer high surface area and cerium cations may be available as inhibitors of recombination centers and photoelectrochemical sites. Higher cerium loadings create recombination of surface charged sites for both photoactivity and photoelectrochemical features. The TEM images clearly show that the doping of nickel hydroxide with cerium helped achieve very thin platelets with hexagonal and translucent shapes, which is in contrast with the bare Ni(OH)2 samples.
4 Conclusions
In summary, this work provides new knowledge about photo-based applications of Ce- doped Ni(OH)2 materials. The electrochemical evaluation showed that the synthesized nanomaterials had pseudo-capacitive behavior and the Ni(OH)2–Ce2 sample exhibited lower charge transfer resistance and therefore, it had improved electrochemical activity. The photoelectrochemical analysis under UV light revealed that the performance of Ni(OH)2–Ce2 was ten times greater than that of pure Ni(OH)2 and the photocurrent rapidly responded to light irradiation. This result indicates that Ni(OH)2–Ce2 can have applications as photoelectrode in solar cells, UV photosensors and optoelectronic devices. The degradation of MO using Ni(OH)2–Ce2 reached 83% after 140 min of irradiation with a UV lamp and the calculated degradation rate constant was 0.0125 min− 1; so, this nanomaterial has high potential as a photocatalyst for removing organic contaminants from wastewater. Overall, the photoelectrochemical and photocatalytic evaluation findings set a precedent to develop high photoelectric performance electrodes to be used in the field of photoelectrochemical catalysis.
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Acknowledgements
C. Martínez-Sánchez appreciates the Postdoctoral scholarship granted by CONACYT. We gratefully acknowledge G. Labrada-Delgado and H. Silva-Pereyra from LINAN-IPICYT for the FESEM and TEM characterizations. V. Rodríguez-González is grateful to KOFTS for the Brain Pool Program No. 152S-2-31424. This research was partially supported by the National Research of Korea (NRF) funded by the Ministry of Education, Science and Technology.
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Martínez-Sánchez, C., Regmi, C., Lee, S.W. et al. Effects of Ce Doping on the Photocatalytic and Electrochemical Performance of Nickel Hydroxide Nanostructures. Top Catal 64, 73–83 (2021). https://doi.org/10.1007/s11244-020-01295-y
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DOI: https://doi.org/10.1007/s11244-020-01295-y