Synthesis of lead-free Cu/CuFeO2/CZTS thin film as a novel photocatalytic hydrogen generator from wastewater and solar cell applications
verfasst von:
Amira H. Ali, Ashour M. Ahmed, M. M. Abdelhamied, Ahmed A. Abdel-Khaliek, S. Abd El Khalik, Safaa M. Abass, Mohamed Shaban, Fuead Hasan, Mohamed Rabia
The sewage water is tested as a source of hydrogen production with a high efficiency value of 25.44% using Cu/CuFeO2 (delafossite)/CZTS (Cu2ZnSnS4, kesterite) as an investigated photocatalyst. The X-ray diffraction (XRD) analysis of the investigated photocatalyst (Cu/CuFeO2/CZTS) revealed a compact crystalline material, as witnessed by the diffraction peaks with high intensities. From the optical characterization, the recorded band gap values of Cu/CuFeO2/CZTS, Cu/CuFeO2, and CZTS are 1.15, 1.97, and 1.43 eV, respectively, inferring an obvious enhancement in the optical properties of the investigated photocatalyst, Cu/CuFeO2/CZTS. The photoelectrochemical (PEC) performance of the investigated photocatalyst for hydrogen (H2) generation was examined in wastewater. The current–time characteristic and the PEC behavior of Cu/CuFeO2/CZTS in dark and under light illumination using various power densities, monochromatic wavelengths, and different temperatures were studied. The current densities (JPh) under light illumination and (Jo) in the dark were − 8.0 and − 0.7 mA cm−2, respectively. The H2 generation rate for the Cu/CuFeO2/CZTS electrode was 0.049 mA/h. The thermodynamic parameters, respectively, ΔS*, ΔE, and ΔH* were 28.76 kJ mol−1 K−1, 21.0, and 18.28 kJ mol−1 at 390 nm. The findings of the work hold great promise for addressing energy production and the hindrances of sewage treatment at the same time.
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1 Introduction
Nowadays, developing renewable energies and clean sources have been studied worldwide for a more promising and safe future for our planet (Feng et al. 2020; Wang et al. 2016; Ali, et al. 2023). Up to now, many studies have focused on employing renewable energy sources such as solar-driven hydrogen (H2) generation (Yadav et al. 2022, 2021a, 2023; Hunge et al. 2022), electrocatalysts for hydrogen and oxygen evolution reactions (Yadav et al. 2021b), water splitting (Yadav et al. 2021c), and solar cells (Prabakaran et al. 2015a, 2015b; Manikandan et al. 2018).
Water splitting using photoelectrochemical (PEC) technology is considered one of the most effective methods for H2 generation as a source of zero-emission pollution (Wang et al. 2022; Mostafa et al. 2022). In PEC water splitting, H2 generation half-reaction can be achieved at an electrode coated with specific semiconductor materials (Pan et al. 2020; Saraswat et al. 2018). Several concerns involving the performance of semiconductor materials have been addressed (Hisatomi et al. 2014; Abdelazeez et al. 2022a; Ali et al. 2022). Several parameters could affect the produced H2 efficiency, such as effective charge carrier separation, the incorporation of semiconductors with a narrow bandgap, and the high ability of visible light absorption (Zhang et al. 2009; Fajrina and Tahir 2019; Abdelazeez et al. 2022b).
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Semiconducting delafossite-phase (CuFeO2) is one of the few photocatalysts that exhibits strong photocatalytic activity for H2 evolution (Prabhu et al. 2019; Liu et al. 2020; El-Rabiei et al. 2020). CuFeO2 thin films or particles could be prepared using a variety of methods, including sol–gel (Toupin et al. 2019), spray pyrolysis (Moumen et al. 2019), electrodeposition (Zhang et al. 2020), microwave irradiation (Jagadeesan et al. 2019), hydrothermal (Bhuvaneshwari and Gopalakrishnan 2016; Ali 2023), sonochemical (Andrade et al. 2019), sputtering (Verma et al. 2018), and thermal oxidation (Behjati et al. 2020; Lee et al. 2021). Each technique has its own influence on the surface characteristics and the direct bandgap of the prepared CuFeO2 photoelectrodes. These methods could also be applied to the doping of the CuFeO2 photocathode with various elements.
In the previous publications, some appropriate approaches were discussed to promote the photocatalytic activity of CuFeO2, such as doping or modification with elements (Jamila et al. 2020), formation of a heterojunction (Nogueira et al. 2019), and controlling the morphology (Vo et al. 2020). These strategies can limit the drawbacks of CuFeO2, such as the poor photoinduced electron–hole separation, high bandgap, and promote the photocatalytic behavior by using one or more approaches. Some of these methods can expand the particular surface area of CuFeO2, improve its electronic structure, enhance the charge separation ability, reduce the activation energy, and develop a new mechanism for electron–hole transmission with bandgap engineering (Siddiqui et al. 2020).
A possible source of sustainable and renewable energy is the production of hydrogen from water using photocatalysts without noble metals. Earth-abundant element-based copper chalcogenides, particularly CZTS (Cu2ZnSnS4), have emerged as inexpensive and environmentally good materials for photocatalysis and photovoltaics. CZTS has demonstrated a variety of benefits in terms of harnessing and harvesting solar energy. Both UV and visible light can be effectively absorbed by CZTS because of its narrow band gap of about 1.5 eV. Furthermore, its plentiful, inexpensive, and non-toxic components make CZTS a durable clean energy converter (Guo et al. 2009; Riha et al. 2009). CZTS has been employed as a catalyst for photocatalytic H2 creation under visible light irradiation in addition to being used in photovoltaic systems as a light absorber (Singh et al. 2012; Wang et al. 2012). A significant increase in photocatalytic H2 generation has been achieved by decorating CZTS with Au, Pt, and other precious metals with strong surface plasmons and strong catalytic activity (Ha et al. 2014). However, due to their rarity and high price, these noble metals are not widely used in industry because they are uncompetitive (Wu et al. 2022; Ha et al. 2015). Consequently, it would be very helpful if the catalytic efficiency of CuFeO2 could be raised by combining it with other affordable and high-performance materials, like CZTS, via a delicate interfacial design (Yu et al. 2014).
In this paper, we propose CuFeO2 hybridization with CZTS to develop a hybrid photocathode with improved catalytic behavior. The hybrid photocatalyst was prepared on Cu foil through a combination of combustion and solvothermal processes (Cu/CuFeO2/CZTS). The optical, chemical, and morphological features were investigated through various tools, such as UV–vis, XPS, XRD, and SEM. The photoelectrochemical (PEC) behavior of the investigated photocatalyst (Cu/CuFeO2/CZTS) was assessed using a three-electrode cell. The effects of light wavelength intensity and solution temperature were studied. The Nyquist plot, PCE, and thermodynamic parameters were calculated. Due to the groundbreaking nature of our recently engineered composite, Cu/CuFeO2/CZTS, and its remarkable 25.4% efficiency in producing hydrogen from wastewater, our team is actively preparing to embark on the development of a prototype. Furthermore, these materials are characterized by user-friendly preparation techniques, scalability for mass production, and cost-effective processes. Our team is poised to create a prototype that directly converts sewage water into hydrogen gas, with the ultimate aim of offering a practical solution for remote areas.
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2 Experimental part
All the chemicals are from Sigma-Aldrich, which are H2SO4 (99.999%), acetone (99.9%), ethanol (99.8%), Fe(NO3)2 nonahydrate (≥ 99.95%), copper acetate anhydride (98%), zinc acetate dehydrate (99.999%), tin(IV)acetate (95%), anisole anhydrous (99.7%), oleylamine (≥ 98%), carbon disulfide (≥ 99.9%), toluene (≥ 99.5%), methanol anhydrous (99.8%), and chloroform anhydrous (≥ 99%).
2.1 Synthesis of Cu/CuFeO2
The Cu/CuFeO2 synthesis is performed using a combustion process. Firstly, the Cu foil (0.5 mm in thickness) was ultrasonically washed using soap and distilled water for 15 min, then it was soaked in concentrated H2SO4 for 15 min until complete polishing. Finally, it was cleaned with distilled water, ethanol, and acetone for five minutes each in an ultrasonic bath. The cleaned Cu foil was immersed in 0.2 M Fe(NO3)2 for 30 min, then heated at 60 °C for 30 min. The Cu foil is calcined in the air environment at 500 °C for 10 min to produce a Cu/CuFeO2 micro-/nano-structured substrate.
2.2 Synthesis of copper zinc tin sulfide
CZTS was prepared through the solvothermal technique (Patil et al. 2016). Copper acetate anhydride, 0.22 g, zinc acetate dehydrate, 0.073 g, and tin(IV) acetate, 0.095 g, are mixed in 50 mL of anisole. The mixture was kept under stirring until a light blue color was obtained. Then, 1.2 mL of oleylamine was added and maintained under stirring till a dark blue color was observed. Carbon disulfide (0.6 mL) was added for 5 min until the dark yellow color was formed. The prepared solution is placed in an autoclave for 24 h at 170 °C. The black precipitate is separated by centrifugation once it has reached room temperature and washed sequentially with 20 mL of toluene and 40 mL of methanol.
2.3 Preparation of Cu/CuFeO2/CZTS
The prepared CZTS (0.04 g) was dissolved in 2 mL of chloroform under ultrasonication, then 150 µL of CZTS was spin-coated over the prepared Cu/CuFeO2 substrate and dried for 15 min at 70 °C. The sample is then annealed using the Muffle furnace (Chem. Tech) model for 25 min at 200 °C.
2.4 Characterization
The surficial morphologies of the prepared samples were examined by scanning electron microscopy (SEM), Auriga Zeiss FIB, with a 5 kV accelerating voltage. A Bruker/Siemens D5000 diffractometer is applied for pattern recording of the X-ray diffraction (XRD). The chemical structures of the prepared samples were investigated using X-ray photoelectron spectroscopy (XPS, K-ALPHA, USA). The optical characteristics have been investigated through a Perkin Lamba 950 double-beam UV–vis spectrophotometer (USA).
2.5 Hydrogen generation
The CHI660E electrochemical station (USA) is applied to investigate the photoelectrochemical (PEC) behavior of the Cu/CuFeO2/CZTS. The electrodes with three parts made up the PEC system, in which the Cu/CuFeO2/CZTS (1 cm2), Pt plate, and Ag/AgCl acted respectively as the working, counter, and reference electrodes. Wastewater (Egypt, Beni-Suef City, sewage water, third stage) was used as a testing electrolyte. The chemical composition of the sewage water is shown in Table 1. In the solar simulator, an Xe lamp (Newport) is applied throughout the measurements with a 100 mW cm−2 power density for light illumination.
Table 1
The chemical composition of the sewage water electrolyte that is used for H2 production
Material or element
Concentration (mg/L)
Pb2+
0.5
Phenols
0.015
F−
1.0
Al3+
3.0
As3+
0.05
Cr3+
1.0
NH3
5.0
Hg2+
0.005
Cu2+
1.5
Ni3+
0.1
Fe3+
1.5
Cd3+
0.05
Co2+
2.0
Mn2+
1.0
Zn2+
5.0
Ag+
0.1
Industrial washing
0.5
Other cations
0.1
Pesticides
0.2
Ba3+
2.0
Coli groups
4000/100 cm3
CN−1
0.1
3 Results and discussion
3.1 1Morphological analyses
Cu/CuFeO2, CZTS, and Cu/CuFeO2/CZTS samples are characterized through the SEM analysis and presented in Fig. 1a–c, respectively. The highly crystalline polyhedral CuFeO2 delafossite, Fig. 1a, and the kesterite CZTS, Fig. 1b, are free of cracks with a smooth surface; the dense uniform grains are expected to have a great advantage in enhancing the optical properties (Wang et al. 2012). Moreover, the compact and free-cracked morphology indicates the generation of electrons and photocatalytic features because the cracked surface favors the dispersion of electrons. This highly crystalline morphology matches well with other previous literature reports (Singh et al. 2012; Yu et al. 2014). The SEM morphology of the investigated photocatalyst (Cu/CuFeO2/CZTS) was seen in Fig. 1c. The inset of Fig. 1c shows the cross-sectional SEM of the Cu/CuFeO2/CZTS multilayers. The thickness of the Cu/CuFeO2/CZTS films is around 400 nm that is estimated in Fig. 1d through the cross section simulated image. After spin coating of the CZTS, the formed Cu/CuFeO2/CZTS shows a compact morphology related to the great ordering of the particles. Also, the surface of the investigated photocatalyst becomes homogeneous and less rough. In conclusion, there are no apparent pinholes at the surface of Cu/CuFeO2/CZTS film, indicating that the investigated photocatalyst has great stability (Zhou et al. 2011).
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3.2 XRD analysis
The Cu/CuFeO2 XRD pattern is displayed in Fig. 2a. The size of the crystal is estimated to be 24 nm. All Cu/CuFeO2 signals confirmed the presence of the hexagonal 2H-CuFeO2 (JCPDS card No. 01-079-1546) and the rhombohedral 3R-CuFeO2 (JCPDS card No. 00-039-0246) structural phases of CuFeO2, based on the distinctive peaks. Although the 2H–CuFeO2 phase is present, the 3R–CuFeO2 phase dominates the main XRD pattern (Gao et al. 2021). In Fig. 2a, the main characteristic peaks of CuFeO2 appeared at 36.02°, 39.12°, 58.3°, 61.78°, 67.70°, 74.96°, and 83.02°, which correspond to the (006), (012), (110), (1010), (0012), (202), and (024) lattice planes, respectively. This suggested the successful synthesis of the Cu/CuFeO2 layers. The XRD of pure CZTS in Fig. 2b showed signals of CZTS tetragonal phase, and it is quite similar to the normal pattern of kesterite CZTS. It comprises major peaks at 32.20°, 28.29°, 56.08°, and 47.84° due to the (200), (112), (312), and (220) planes, respectively. The results are consistent with the previously disclosed kesterite CZTS findings (Nishi et al. 2013). This suggested the successful synthesis of CZTS film. The XRD of the investigated photocatalyst (Cu/CuFeO2/CZTS) is presented in Fig. 2c. The crystal of the investigated photocatalyst has a calculated size of 1.73 nm. The plot comprises diffraction peaks at 32.2°, 28.29°, 56.08°, and 47.84°. Of note, these peaks are nearly in the same locations as those of the CZTS kesterite structure; this implies that these peaks might be due to the (200), (112), (312), and (220) kesterite planes of CZTS. The other diffraction peaks at 36.02°, 39.12°, 58.3°, 61.78°, 67.7°, 74.96°, and 83.02° are assigned respectively to the (006), (012), (110), (1010), (0012), (202), and (024) lattice planes of CuFeO2. This suggested the successful synthesis of the Cu/CuFeO2/CZTS multilayers.
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3.3 XPS analyses
XPS is typically accomplished by exciting a sample surface with mono-energetic Al kα x-rays, causing photoelectrons to be emitted from the sample surface. An electron energy analyzer is used to measure the energy of the emitted photoelectrons. The surface types of Fe, Cu, O, and C atoms in Cu/CuFeO2 are shown in the survey X-ray photoelectron spectrum in Fig. 3a, which displays the different elements and their corresponding binding energies (BE). The survey XPS plot comprises Fe 2p, C 1s, Cu 2p, and O 1s at 711.25, 285.0, 932.61, and 530.98 eV, respectively. The survey XPS spectrum of Cu/CuFeO2 is discussed in detail from the high-resolution XPS plots in Fig. 4a–d. The Cu 2p XPS high-resolution plot is depicted in Fig. 4a, where the peaks around 952.0 and 932.0 eV arise from the Cu+ 2p(1/2) and the Cu+ 2p(3/2) orbital binding energies, respectively. The Cu2+ satellite characteristic peak at around 943.0 eV confirmed the presence of Cu2+ near the CuFeO2 surface (Jain et al. 2019; Yamashita and Hayes 2008). In Fig. 4b, the Fe 2p XPS high-resolution spectrum could be curve-fitted with a peak around 711.12 eV due to the 2pFe(3/2) orbital binding energy, which is ascribed to the Fe3+ in CuFeO2, indicating that the Fe3+ is the characteristic intense peak (Yamashita and Hayes 2008). Figure 4c showed the O 1s spectrum around 530.0 eV, which is typical for O2− ions in the CuFeO2 matrix. Figure 4d shows the C 1s spectrum, which is well approximated by the peak around 285.0 eV, which is assigned to adventitious carbon raised from the CO2 adsorption (Sarabia et al. 2016). The above findings suggest that the Cu/CuFeO2 thin film is produced through the combustion approach.
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The survey XPS spectrum of the CZTS nanostructure is featured in Fig. 3b. The XPS plot comprises Sn 3d, Cu 2p, S 2p, and Zn 2p at 486.75, 932.7, 160.34, and 1022.06 eV, respectively. The survey XPS spectrum of CZTS has been discussed in detail from the high-resolution XPS plots in Fig. 4e–h. Figure 4e displays the spectrum of the Cu 2p, which can be deconvoluted into two main components due to Cu2p(1/2) and Cu2p(3/2) signals around 952.12 and 932.18 eV, respectively, giving an indication of the existence of Cu (I) (Zhou et al. 2011). Figure 4f showed that the Zn 2p peak comprises two characteristics, respectively, Zn2p(1/2) and Zn2p(3/2) signals around 1045.2 and 1022.1 eV, matching the 23.0 eV typical splitting, indicating the existence of Zn (II). Figure 4g shows the Sn 3d pattern, which exhibits two signals around 486.2 and 495.0 eV, evidence for Sn(IV), indicating the existence of Sn3d (5/2) and Sn3d (3/2), respectively. The XPS spectrum of the sulfur peaks is displayed in Fig. 4h. There are two expected signals from SO42-; the signal from sulfur with a zero charge S0 (2pS 3/2 and 2pS 1/2) at energies around 160.0–164.0 eV, and S6+ (2pS 3/2 and 2pS 1/2) at energies around 168.0–172.0 eV. The above findings suggest the formation of a CZTS thin film through the solvothermal method.
From the above results, we can conclude the binding energies of the investigated photocatalyst (Cu/CuFeO2/CZTS) from the survey XPS in Fig. 3c. The peaks around 530.0, 285.0, 711.0, 932.0, 160.0, 486.0, and 1022.0 eV correspond to O 1s, C 1s, Fe 2p, Cu 2p, S 2p, Sn 3d, and Zn 2p, respectively. The above findings suggest the successful synthesis of Cu/CuFeO2/CZTS photocatalyst.
3.4 Optical and bandgap
Examining the optical properties of the Cu/CuFeO2/CZTS sample is crucial for its potential application in photocatalytic hydrogen generation. Figure 5a displays the absorption curves of Cu/CuFeO2/CZTS, CZTS, and Cu/CuFeO2. These curves reveal a sharp absorbance peak at approximately 300 nm, aligning with absorption spectra observed in previous studies on CuFeO2 and CZTS films. Understanding these optical features is essential for harnessing the photocatalytic properties of the Cu/CuFeO2/CZTS sample in hydrogen generation applications. (Das, et al. 2018; Yengantiwar et al. 2018). Furthermore, all three prepared films exhibit the capability to absorb light across the near-infrared (NIR) and ultraviolet–visible (UV–vis) regions spanning from 400 to 800 nm. Notably, it is evident that the combination of CZTS with the Cu/CuFeO2 sample leads to a noticeable enhancement in the absorption intensity of Cu/CuFeO2. This enhancement can be attributed to the fact that the investigated photocatalyst, specifically Cu/CuFeO2/CZTS, possesses a narrower bandgap in comparison to the CuFeO2 layer.
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In simpler terms, all three films exhibit the ability to absorb light in both the near-infrared and UV–visible regions, which is vital for their potential as photocatalysts. The amalgamation of CZTS with the Cu/CuFeO2 sample results in a significant boost in the absorption capacity of Cu/CuFeO2. This increase can be explained by the fact that the Cu/CuFeO2/CZTS photocatalyst has a narrower energy bandgap when compared to the pure CuFeO2 layer. This narrower bandgap enables the material to capture a broader range of light wavelengths, making it a more efficient candidate for photocatalytic applications (Ju et al. 2018). Moreover, the function of Cu plasmonic materials is recognized as highly effective in capturing photons. This effectiveness stems from the generation of hot electrons, which induce a significant resonance within the surrounding CuFeO2 and CZTS semiconductor materials.
From Tauc’s equation (Shaban et al. 2018), we can calculate the energy gap, Eg, based on the direct allowed transitions:
In this equation, the parameter v is the light frequency, α is the absorption coefficient, h is the Planck constant, and β is a constant. The relation between α and the absorbance, A, is given in Eq. (2):
$$\mathrm{\alpha }= 2.303\mathrm{ A}/{\text{d}}$$
(2)
where d is the thickness. Extrapolation of the hν versus (αhv)2 linear part allows for an estimate of the band gap value through the X-axis intercept, as seen in Fig. 5b. The band gap values of Cu/CuFeO2/CZTS, CZTS, and Cu/CuFeO2 were determined as 1.15, 1.43, and 1.97 eV, respectively, which gives an enhancement in the optical absorption of the investigated photocatalyst (Cu/CuFeO2/CZTS). Despite the low band gap of CZTS (1.43 eV), it showed high photocatalytic activity. This can be recently interpreted by S. Dursunin and co-authors, who have investigated the mechanism that performs photocatalysis depending on scavenger experiments, and it was shown that holes had little impact on the process, whereas O−2 radical ions have a significant influence in the reaction (Dursun et al. 2023). Figure 5a, which is consistent with previously reported absorption spectra of CuFeO2 (Yengantiwar et al. 2018; Read et al. 2012; Prevot et al. 2015a) and CZTS films (Das, et al. 2018). In that approach, the Cu/CuFeO2/CZTS photocatalyst shifted to a longer wavelength (1.15 eV) compared to that of CZTS and CuFeO2 at 1.43 and 1.97 eV, respectively. Therefore, the Cu/CuFeO2/CZTS photocatalyst enhanced visible light harvesting and hence showed significant photocatalytic activities when illuminated by visible light. So, the investigated Cu/CuFeO2/CZTS photocatalyst can be applied in H2 generation systems.
3.5 Electrochemical H2 production
The PEC study of the Cu/CuFeO2/CZTS photoelectrode is recorded at 25 °C and a 20 mV s−1 sweep rate using wastewater solution. The PEC results under dark and light conditions using a Xenon lamp (100 mW cm−2) in the absence of an optical filter are seen in Fig. 6a, b for Cu/CuFeO2 and Cu/CuFeO2/CZTS, respectively. In Fig. 6a, the photocurrent density (Jph) values of the Cu/CuFeO2 photoelectrode are − 0.36 and − 0.89 mA cm−2 under dark and light, respectively. After CZTS coating and the formation of the Cu/CuFeO2/CZTS photoelectrode composite, the recorded Jph values for Cu/CuFeO2/CZTS (Fig. 6b) under light and dark conditions are respectively − 8.0 and − 0.7 mA cm−2. The efficient PEC water splitting is characterized by the high Jph value achieved through the light illumination. The significant current under dark conditions arises from the transferred charge through the ionic currents of the solution. Moreover, the increase in voltage applied under the illumination of a 100 mW −2 Xenon lamp gives an increased Jph value due to the photocatalytic nature of the prepared composite nanomaterial, in which a splitting in the external energy levels under light is expected. The incident photons are captured inside the material and cause the excitation of the external electrons that are collected on the surface of the composite material, from which these electrons reach the wastewater for additional reactions for the generation of hydrogen gas fuel.
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Figure 6c depicts the stability of the Cu/CuFeO2/CZTS photoelectrode. To avoid any external losses to the measuring system, a very low bias voltage of − 0.8 V (RHE) was supplied between the counter and working electrodes under simulated white light of 100 mW cm−2. The first 500 s showed a sharp decrease in the Jph value from − 2.25 to − 0.31 mA cm−2, and then the Jph value was almost constant up to 3200 s due to an increase in the accumulated ionic charges. The H2 generation rate for Cu/CuFeO2/CZTS photoelectrode is 0.049 mA/h. The reason for the decrease in Jph value in the first 500 s is related to the reaction between the electrode and the electrolyte, which causes a very small corrosion process. Also, the increase in the rate of ionic charge accumulation led to a longer lifetime of the Cu/CuFeO2/CZTS with time. This result confirms that Cu/CuFeO2/CZTS has a longer lifetime and higher chemical stability for H2 production from wastewater. The Jph-V measurements are repeated many times for Cu/CuFeO2/CZTS multilayers under a white light of 100 mW cm−2, as seen in Fig. 6d. The value of Jph decreases from − 8.0 to − 7.69 mA cm−2 after four successive repeated measurements. The small change in Jph indicates high reproducibility.
Under light illumination, Fig. 6b demonstrates the generation of photocurrent at V = 0. This indicates that the Cu/CuFeO2/CZTS multilayer has applications in solar cells, where this value of photocurrent can be indicated as short circuit current (JSC).
To measure the IPCE percent value, the study of the illuminating power density effect, Plight, on the prepared Cu/CuFeO2/CZTS photoelectrode is studied. Figure 7a exhibits the Jph variation with applied potential in the presence of Plight from 25.0 to 100 mW cm−2. As Plight increased from 25 to 100 mW cm−2, the Jph results increased, as seen in Fig. 7b, where the highest Jph of − 8.0 mA cm−2 was recorded at 102 mW cm−2.
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The relation between the Jph and the applied potential was studied at 100 mW cm−2 for the Cu/CuFeO2/CZTS in the presence of different monochromatic filters from 390 to 636 nm, as seen in Fig. 8a. From Fig. 8b, with a 390–636 nm increase in optical wavelength, the Jph values decreased. The IPCE percent value was measured for Cu/CuFeO2/CZTS under monochromatic illumination (Fig. 8c) to confirm its enhanced PEC features for efficient H2 production from wastewater. Such measurements provide useful information on the film's contribution to the conversion of incident photons into charge carriers. Equation 3 is used to calculate the IPCE at a 1 V applied potential.
where the wavelength of the monochromatic photons is λ, Jph represents the photocurrent density, and Plight denotes the illuminating light power density (100 mW cm−2) (Shi et al. 2016). As seen in Fig. 8c, the IPCE recorded a remarkable decrease from 25.44% at 390 nm to 11.09% at 636 nm. These high IPCE values in a broad light region confirm the high-efficiency properties of the prepared Cu/CuFeO2/CZTS photocatalytic electrode to use the incidence light for the generation of hydrogen gas.
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Figure 9a displays the effect of temperature on the H2 production of the prepared photocatalyst (Cu/CuFeO2/CZTS). It could be observed that with increasing temperature, the Jph values increased due to enhanced mobility of the ions. Therefore, the Jph can be used as an indication of the rate of H2 production at various temperatures.
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To calculate the reaction activation energy (Ea), the Arrhenius law is applied as follows:
In this equation, T denotes the temperature in absolute terms, R corresponds to the standard gas constant, and k denotes the rate constant. Figure 9b shows the relationship between the reciprocal temperature and the values of the ln (Jph) (rate of reaction). The Ea of the Cu/CuFeO2/CZTS film was determined to be 21.0 kJ mol−1, indicating that the film has an efficient application for H2 production. The entropy ΔS* and the enthalpy ΔH* were calculated using the Eyring Eq. (6):
Figure 9c presents the relationship between (1/T) and Ln (Jph/T). From the intercept and the slope results of the straight line, the ΔS* and ΔH* were respectively estimated to be 28.76 kJ mol−1 K−1 and 18.28 kJ mol−1.
Figure 10a depicts the Nyquist impedance plot of the Cu/CuFeO2/CZTS under white light illumination. It was observed that the impedance spectra under light conditions had two semicircles, indicating that there are two-time constants that controlled the reaction. For more accurate impedance analysis, an equivalent circuit model is suggested in Fig. 10b. It includes a double-layer capacitor, Cdl, in parallel with Rs (solution resistance) and Rct (charge transfer resistance). An extra capacitor, Cf, and a resistance, Rf, are added to account for the capacitance and resistance of the film. The Rs value under light conditions was calculated to be 0.36 Ω cm2. The small Rs value under light conditions was deduced from the small loop diameter, indicating the high current density, and this is a pre-indicator for the application of Cu/CuFeO2/CZTS in the H2 production from wastewater.
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3.6 Mechanism
The impact of incident light on the photoelectrons serves as the foundation for the photocatalytic mechanism for the sewage water-splitting process. The photoelectrons produced as a result of the light incident go through two stages. In the first, called electron–hole generation, the created electrons leave the holes and ascend to a higher level. The localized surface plasmonic resonance (LSPR) is the second step, which results in energy transmission (Cortes et al. 2020). Because the Cu and CuFeO2 nanomaterials don't have any depletion zones, and due to the small Cu/CuFeO2 band gap value, these two steps occurred easily. As a result, there is no restriction on the transfer of electrons from Cu to CuFeO2, and there is no constraint on the continuous flow of electrons. Moreover, the Cu material can act as a plasmonic material for light capture and the generation of an electric field that covers all the neighboring photocatalytic materials. The final electron cloud is collected over CZTS under the lower conducting band level, through which the electrons are transferred to the sewage water-electrolyte. Under the applied voltage, these hot electrons cause the generation of Jph (Hussain et al. 2016; Wang et al. 2014). The optical analyses (Fig. 5) and electrochemical measurements feature the experimental image of electron transfer processes under several effects, such as light wavelength and light intensity. The light capture and electron resonance processes represent the rate of hydrogen generation reactions (Cao et al. 2021; Qin et al. 2016). In Fig. 11, the energy diagram of the photocatalysis system is described for the generation of H2. Due to the low barrier height between the CuFeO2 Fermi level and the CZTS conduction band, the heated electrons can move from CuFeO2 to the CZTS after crossing the barrier (Malerba et al. 2014; Khammar et al. 2020). This prevents the carrier's recombination and permits a constant flow of electrons into the system, leading to the generation of photocurrent. This photocurrent represents the efficiency of these materials for solar cell applications and hydrogen generation. The Jph values and the H2 production reaction rate are used to represent these electrons (S. S et al. 2016). Finally, Table 2 compares the results of the current investigation to the previously published literature.
Table 2
Comparing the current study to the previously published literature (IPCE, electrolyte, and Jph values)
The Cu/CuFeO2/CZTS investigated photocatalyst was prepared for H2 production using wastewater as a test solution. The morphological, optical, and chemical properties are investigated through a variety of analyses, including SEM, XRD, UV–Vis, and XPS. From the SEM analysis, the investigated photocatalyst displayed a uniform shape with a 350 nm particle size, implying that the crystallinity of the investigated photocatalyst was significantly enhanced. From the XRD analysis, the crystal size of the Cu/CuFeO2 layer was calculated to be 24 nm; however, the XRD spectrum of the investigated photocatalyst (Cu/CuFeO2/CZTS) revealed compact, highly crystal material, indicating the improvement of the crystalline quality for the investigated photocatalyst. From the optical results, the recoded band gap values of Cu/CuFeO2/CZTS, CZTS, and Cu/CuFeO2 were 1.15, 1.43, and 1.97 eV, respectively, showing an obvious enhancement in the optical properties of the investigated photocatalyst (Cu/CuFeO2/CZTS). In the PEC study, the investigated photocatalyst recorded current densities of − 8.0 and − 0.7 mA cm−2 under light and dark illumination, respectively. The H2 generation rate for the Cu/CuFeO2/CZTS perovskite electrode was 0.049 mA/h. The calculated thermodynamic parameters ΔS*, ΔE, and ΔH* were respectively 28.76 kJ mol−1 K−1, 21.0, and 18.28 Kj mol−1 at 390 nm. From the Nyquist impedance plot, the Rs value of Cu/CuFeO2/CZTS under light conditions was 0.36 Ω cm2, which is a pre-indicator for the application of Cu/CuFeO2/CZTS in the H2 production. Soon, our team will work on the design of a prototype of PEC for direct conversion of sewage water into hydrogen fuel that can be applied in houses and high-technology devices such as airplanes and aircraft.
Acknowledgements
This paper is based on work supported by the Science, Technology & Innovation Funding Authority (STDF) under a grant given to Amira H. Ali with project number 44809.
Declarations
Conflict of interest
The authors have no conflicts of interest.
Ethical approval
This study does not include any human or animal studies.
Data availability
All data generated or analyzed during this study is included in this article.
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