An E ﬃ cient Strategy for the Fabrication of CuS as a Highly Excellent and Recyclable Photocatalyst for the Degradation of Organic Dyes

: An e ﬀ ective and practical in situ sulfuration approach has been developed in this work, for the fabrication of CuS with a 3D hierarchical network structure under mild preparation conditions. The prepared CuS consists of a primary structure of the multi-structure interchange copper foam precursor, and a secondary structure of nanoplates. The structural characteristics, morphologies, and photocatalytic performances of the prepared photocatalyst were investigated systematically. To evaluate the photocatalytic performance of the prepared CuS samples, we investigated the degradation of MB (methylene blue), RhB (Rhodamine B), and MB / RhB dye solutions over the samples under the irradiation of simulated solar light. Speciﬁcally, the degradation of RhB rapidly reached ≈ 100.0% after simulated solar light irradiation for 25 min, which is higher than those of P25 (83.0%) and bulk CuS (54.8%). For the mixed systems of MB / RhB, both the degradations of MB and RhB reached up to ≈ 99.0% after simulated solar light irradiation for 25 min. The superior photocatalytic performances of the prepared samples are attributed to the synergistic e ﬀ ects of high optical absorption, large speciﬁc surface area, and abundant active sites. The prepared catalysts can retain the photocatalytic activities during the entire reaction process without signiﬁcant loss after four catalytic cycles, which reveals that the CuS with a stable 3D hierarchical network structure has a promising prospect as an ideal recyclable catalyst.


Introduction
Owing to the energy crisis and environmental pollution issues, photocatalytic treatment, one of the most efficient, environmentally safe, and promising methods for eliminating organic and harmful pollutants in water, has attracted considerable research interest. Sunlight is a non-polluting and easy-to-access energy source, with great potential to drive environmentally friendly organic transformations [1]. In particular, the irradiation of light is essential for the photocatalysis reaction, involving the advanced oxidation process (AOP). AOP is based on hydroxyl radicals (OH·) produced by the combination of catalysts and irradiation, sometimes together with oxidants, to convert organic and harmful pollutants into small molecules (e.g., CO 2 , H 2 O) via Fenton, photo-Fenton reactions, and photocatalysis [2,3]. In particular, for the photo-Fenton reactions, the H 2 O 2 serves as an efficient scavenger that can capture the photo-generated electrons to form more OH·; thus, a certain amount of H 2 O 2 is necessary. As one of the most well-known photocatalysts, TiO 2 has been extensively used for the efficient degradation of organic pollutants [4][5][6][7]. However, the wide bandgap of TiO 2 enables the absorption of ultraviolet light only, which considerably inhibits the generation of hydroxyl free radicals that are critical in the oxidation of organic pollutants, resulting in relatively low efficiency in solar energy utilization [8][9][10][11][12]. Therefore, the development of photocatalysts with high hydroxyl free radical generation rates is desirable for the enhancement of photocatalytic performance.
Various semiconductors with narrow bandgaps have been developed to improve the photocatalytic efficiency [13][14][15][16]. Among them, copper sulfide (CuS), with a bandgap of ≈2.0 eV, has excellent optical and electrical properties with a wide range of applications in photocatalysis [17][18][19][20][21][22], which is considered as an attractive and important photocatalyst for dye degradation due to nontoxicity availability, and stability under ambient conditions [23,24]. Previous studies have shown that different morphologies of CuS can significantly impact their properties, as well as their potential applications. Compared with bulk CuS, microstructure CuS displays improved photo-electric properties and catalytic activities, enhanced electric conductivity, and capacitance owing to its small particle size and large specific energy density [25]. Recently, 1D, 2D, and 3D CuS micro/nanostructures with various morphologies, such as micro/nano-wire, sheet, and hierarchical structures have been fabricated. According to the report, nanowires [26][27][28] and nanosheets [29][30][31] have been used as building blocks for manufacturing micro/nanostructured materials with 3D hierarchical morphologies. On the basis of the 1D single nanowire or 2D nanosheet structure, 3D hierarchical structure materials afford more ion transmission paths and a stable structure, which have received increasing research attention because their 3D hierarchical structure features a large surface area and abundant surface active sites [32,33]. Therefore, research on the degradation of dye with 3D hierarchical structure CuS has attracted much attention. Over decades of research, various protocols have been developed for the fabrication of CuS with a 3D hierarchical structure, such as the sacrificial templating in the solvothermal process [34,35]. Nevertheless, the synthesis of 3D hierarchical structured materials through a one-step in situ heating sulfuration method is seldom reported. In the process of heating sulfuration, the copper foam is more effectively contacted with S to realize a one-step reaction. The heating sulfuration method is simple, low-cost, and tractable. Consequently, a straightforward and efficient one-step in situ heating sulfuration treatment is developed for the fabrication of CuS with a 3D hierarchical structure.
Herein, we prepared CuS with a 3D hierarchical network structure using a one-step in situ heating sulfuration approach. To evaluate the photocatalytic performance of the prepared CuS, we investigated the degradation of MB (methylene blue), RhB (Rhodamine B), and MB/RhB dye solutions under the irradiation of simulated solar light. Figure 1a shows the XRD pattern of the prepared CuS, which demonstrates that all diffraction peaks are in good agreement with the hexagonal CuS phase (JCPDS No. 06-0464) [20,36]. Characteristic peaks of other phases were not detected, suggesting that the copper foam completely converted into the highly pure CuS sample after the sulfuration reaction. The UV-vis spectrum of the prepared CuS was provided. As can be seen from Figure 1b, CuS displays a prominent photoabsorption ability, suggesting that it has the potential to be an efficient photocatalyst under simulated solar light irradiation. The bandgap energy of CuS was found to be 1.58 eV by using the Tauc plot approach [37,38]. The nitrogen adsorption-desorption isotherms of the prepared CuS are provided in Figure S1 (Supplementary Material). The BET surface area of the prepared CuS (12.06 cm 2 g −1 ) was larger than those of other reported CuS microflowers (7.93 cm 2 g −1 ), spheres (3.16 cm 2 g −1 ), and multiplates (6.94 cm 2 g −1 ) [25], indicating that it can provide more active sites for reaction. The morphologies of the prepared samples were also analyzed by SEM and TEM. As can be seen from Figure 2a, after one-step in situ heating sulfuration, CuS samples grew on the copper foam and maintained the characteristic structure of the copper foam (the SEM image of the original copper foam is shown in Figure S2 in Supplementary material). Compared with Figure 2a, Figure 2b clearly shows that CuS nanoplates are formed on the copper foam to afford the 3D hierarchical CuS network structure, indicating that it can provide sufficient reaction active sites. As shown in the EDS spectrum of Figure 2c, the prepared samples only consisted of Cu and S elements. The atomic ratio of Cu to S in the copper sulfide was close to one. The HRTEM image in Figure 2d reveals that the lattice fringes of 0.30 nm can be attributed to the (102) lattice plane of CuS. To further confirm the chemical composition and the valence state on the surface of the sample, we conducted the XPS analysis. As shown in Figure 3a, the binding energies of Cu 2p3/2 and Cu 2p1/2 peaks are at 932.1 and 952.1 eV, respectively, which belong to Cu 2+ in CuS [39][40][41][42][43]. In addition, two shakeup lines at 943.2 and 963.6 eV were observed, corresponding to the satellite peaks of Cu 2+ [42,43]. Furthermore, the symmetrical shapes of two Cu 2p XPS peaks also confirm the presence of pure CuS. The peaks at 162.2 and 163.3 eV (Figure 3b) are characteristic of the S 2− , which corresponds to S 2p3/2 and 2p1/2, The morphologies of the prepared samples were also analyzed by SEM and TEM. As can be seen from Figure 2a, after one-step in situ heating sulfuration, CuS samples grew on the copper foam and maintained the characteristic structure of the copper foam (the SEM image of the original copper foam is shown in Figure S2 in Supplementary Material). Compared with Figure 2a, Figure 2b clearly shows that CuS nanoplates are formed on the copper foam to afford the 3D hierarchical CuS network structure, indicating that it can provide sufficient reaction active sites. As shown in the EDS spectrum of Figure 2c, the prepared samples only consisted of Cu and S elements. The atomic ratio of Cu to S in the copper sulfide was close to one. The HRTEM image in Figure 2d reveals that the lattice fringes of 0.30 nm can be attributed to the (102) lattice plane of CuS. To further confirm the chemical composition and the valence state on the surface of the sample, we conducted the XPS analysis. The morphologies of the prepared samples were also analyzed by SEM and TEM. As can be seen from Figure 2a, after one-step in situ heating sulfuration, CuS samples grew on the copper foam and maintained the characteristic structure of the copper foam (the SEM image of the original copper foam is shown in Figure S2 in Supplementary material). Compared with Figure 2a, Figure 2b clearly shows that CuS nanoplates are formed on the copper foam to afford the 3D hierarchical CuS network structure, indicating that it can provide sufficient reaction active sites. As shown in the EDS spectrum of Figure 2c, the prepared samples only consisted of Cu and S elements. The atomic ratio of Cu to S in the copper sulfide was close to one. The HRTEM image in Figure 2d reveals that the lattice fringes of 0.30 nm can be attributed to the (102) lattice plane of CuS. To further confirm the chemical composition and the valence state on the surface of the sample, we conducted the XPS analysis. As shown in Figure 3a, the binding energies of Cu 2p3/2 and Cu 2p1/2 peaks are at 932.1 and 952.1 eV, respectively, which belong to Cu 2+ in CuS [39][40][41][42][43]. In addition, two shakeup lines at 943.2 and 963.6 eV were observed, corresponding to the satellite peaks of Cu 2+ [42,43]. Furthermore, the symmetrical shapes of two Cu 2p XPS peaks also confirm the presence of pure CuS. The peaks at 162.2 and 163.3 eV (Figure 3b) are characteristic of the S 2− , which corresponds to S 2p3/2 and 2p1/2, As shown in Figure 3a, the binding energies of Cu 2p 3/2 and Cu 2p 1/2 peaks are at 932.1 and 952.1 eV, respectively, which belong to Cu 2+ in CuS [39][40][41][42][43]. In addition, two shakeup lines at 943.2 and 963.6 eV were observed, corresponding to the satellite peaks of Cu 2+ [42,43]. Furthermore, the symmetrical shapes of two Cu 2p XPS peaks also confirm the presence of pure CuS. The peaks at 162.2 and 163.3 eV (Figure 3b) are characteristic of the S 2− , which corresponds to S 2p 3/2 and 2p 1/2 , respectively [43]. In summary, these results demonstrate that the prepared sample is of pure CuS, which is consistent with its XRD pattern.

Characterizations
Catalysts 2019, 9, x FOR PEER REVIEW 4 of 10 respectively [43]. In summary, these results demonstrate that the prepared sample is of pure CuS, which is consistent with its XRD pattern.

Photocatalytic Performance
To evaluate the photocatalytic performance of the prepared sample, we have investigated the degradation of MB, RhB, and MB/RhB dye solutions over the samples under simulated solar light irradiation. As shown in Figure 4a,b, it can be seen that the degradation of dye is negligible without light or H2O2. When a small amount of H2O2 was added (without catalyst), the degradation efficiency was slightly improved, possibly due to the photolysis of H2O2 triggered by incident light. Notably, CuS was highly active when adding H2O2 (as shown in Figure S3a). As a result, the degradation of RhB rapidly increased to ≈100.0% after simulated solar light irradiation for 25 min, which is higher than those of P25 (83.0%) and bulk CuS (54.8%) under identical experimental conditions. In addition, the degradation of MB rapidly increased to ≈100.0% after simulated solar light irradiation for 25 min, which is also more effective than that of bulk CuS (as shown in Figure S3b). To further reveal the photocatalytic efficiencies of samples, the kinetic rate constants were measured. As shown in Figure  4c, the kinetic rate constants for degradation of RhB follow the order of: CuS + H2O2 (0.11 min −1 ) > P25 + H2O2 (0.065 min −1 ) > bulk CuS + H2O2 (0.036 min −1 ) > No catalyst + H2O2 (0.0045 min −1 ) > dark (0.0021 min −1 ) > CuS (0.0019 min −1 ), suggesting the high efficiency of the prepared CuS under simulated solar light irradiation. Figure 4d is the kinetics of MB photocatalytic degradation over different photocatalysts, based on the data plotted in Figure 4b. It is obvious that the prepared CuS exhibits superior photocatalytic performance. For CuS + H2O2, as seen in Figure 4c,d, the relationships between ln(C0/Ct) and irradiation time were not linear, as they were for the reaction systems maintained at 30 °C, and the slopes seemed to increase gradually. The continuous increase in the temperature of the reaction systems was most likely the cause of the observed phenomena, which are similar to those reported in previous literature [44]. Furthermore, to better understand the photocatalytic activity of CuS, a coexisted model system is simulated using MB and RhB under the same conditions, to degrade the single dye solutions (0.05 g of photocatalyst, 40 mL of 10 mg L −1 MB/RhB, 40 μL of H2O2, pH 4, 30 °C.). As displayed in Figure 4e, it can be seen that, for the mixed systems of MB/RhB, both the degradation of MB and RhB reached up to ≈99.0% after simulated solar light irradiation for 25 min. This result indicates that the prepared CuS can not only degrade a single dye (e.g., MB, RhB), but can also degrade the mixed systems including different kinds of dyes. The photocatalytic activities of 3D hierarchical network structured CuS are also superior to those of other reported CuS catalysts, as presented in Table 1. All these results further indicate that the 3D hierarchical network structured CuS, with a high surface area, is an effective catalyst for the degradation of industrial wastewater. To confirm the mineralization degree of MB and RhB dyes, the TOC values were measured. In the process of reaction, most of the MB and RhB can be mineralized

Photocatalytic Performance
To evaluate the photocatalytic performance of the prepared sample, we have investigated the degradation of MB, RhB, and MB/RhB dye solutions over the samples under simulated solar light irradiation. As shown in Figure 4a,b, it can be seen that the degradation of dye is negligible without light or H 2 O 2 . When a small amount of H 2 O 2 was added (without catalyst), the degradation efficiency was slightly improved, possibly due to the photolysis of H 2 O 2 triggered by incident light. Notably, CuS was highly active when adding H 2 O 2 (as shown in Figure S3a). As a result, the degradation of RhB rapidly increased to ≈100.0% after simulated solar light irradiation for 25 min, which is higher than those of P25 (83.0%) and bulk CuS (54.8%) under identical experimental conditions. In addition, the degradation of MB rapidly increased to ≈100.0% after simulated solar light irradiation for 25 min, which is also more effective than that of bulk CuS (as shown in Figure S3b). To further reveal the photocatalytic efficiencies of samples, the kinetic rate constants were measured. As shown in Figure 4c Figure 4d is the kinetics of MB photocatalytic degradation over different photocatalysts, based on the data plotted in Figure 4b. It is obvious that the prepared CuS exhibits superior photocatalytic performance. For CuS + H 2 O 2 , as seen in Figure 4c,d, the relationships between ln(C 0 /C t ) and irradiation time were not linear, as they were for the reaction systems maintained at 30 • C, and the slopes seemed to increase gradually. The continuous increase in the temperature of the reaction systems was most likely the cause of the observed phenomena, which are similar to those reported in previous literature [44]. Furthermore, to better understand the photocatalytic activity of CuS, a coexisted model system is simulated using MB and RhB under the same conditions, to degrade the single dye solutions (0.05 g of photocatalyst, 40 mL of 10 mg L −1 MB/RhB, 40 µL of H 2 O 2 , pH 4, 30 • C.). As displayed in Figure 4e, it can be seen that, for the mixed systems of MB/RhB, both the degradation of MB and RhB reached up to ≈99.0% after simulated solar light irradiation for 25 min. This result indicates that the prepared CuS can not only degrade a single dye (e.g., MB, RhB), but can also degrade the mixed systems including different kinds of dyes. The photocatalytic activities of 3D hierarchical network structured CuS are also superior to those of other reported CuS catalysts, as presented in Table 1. All these results further indicate that the 3D hierarchical network structured CuS, with a high surface area, is an effective catalyst for the degradation of industrial wastewater. To confirm the mineralization degree of MB and RhB dyes, the TOC values were measured. In the process of reaction, most of the MB and RhB can be mineralized (as shown in Table S1 in Supplementary material), which indicates that the excellent photocatalytic activity of the CuS with a 3D hierarchical network structure.
Catalysts 2019, 9, x FOR PEER REVIEW 5 of 10 (as shown in Table S1 in Supplementary material), which indicates that the excellent photocatalytic activity of the CuS with a 3D hierarchical network structure.   In addition, the cycling experiments were also conducted to investigate the photostability of the CuS catalyst. As shown in Figure 5, the catalyst can retain catalytic activities during the entire reaction process, without significant loss after four cycles. This result reveals that CuS with a stable 3D hierarchical network structure possesses a promising prospect as an ideal recyclable catalyst. Furthermore, the XRD results indicate that the crystal structure of CuS hardly changes before and after the catalytic reaction (see Figure 6).   In addition, the cycling experiments were also conducted to investigate the photostability of the CuS catalyst. As shown in Figure 5, the catalyst can retain catalytic activities during the entire reaction process, without significant loss after four cycles. This result reveals that CuS with a stable 3D hierarchical network structure possesses a promising prospect as an ideal recyclable catalyst. Furthermore, the XRD results indicate that the crystal structure of CuS hardly changes before and after the catalytic reaction (see Figure 6).  Based on these experimental results, we tentatively propose a plausible mechanism for photocatalytic degradation of organic dyes over CuS under simulated solar light irradiation, in Figure  7. CuS with a 3D hierarchical structure has been demonstrated to be an efficient Fenton-like reagent [22]. When CuS is excited, the reaction of photo-generated electrons with H2O2 generates OH· [48], enabling the direct oxidation of adsorbed organic dyes by photo-generated holes [49]. Moreover, the   In addition, the cycling experiments were also conducted to investigate the photostability of the CuS catalyst. As shown in Figure 5, the catalyst can retain catalytic activities during the entire reaction process, without significant loss after four cycles. This result reveals that CuS with a stable 3D hierarchical network structure possesses a promising prospect as an ideal recyclable catalyst. Furthermore, the XRD results indicate that the crystal structure of CuS hardly changes before and after the catalytic reaction (see Figure 6).  Based on these experimental results, we tentatively propose a plausible mechanism for photocatalytic degradation of organic dyes over CuS under simulated solar light irradiation, in Figure  7. CuS with a 3D hierarchical structure has been demonstrated to be an efficient Fenton-like reagent [22]. When CuS is excited, the reaction of photo-generated electrons with H2O2 generates OH· [48], enabling the direct oxidation of adsorbed organic dyes by photo-generated holes [49]. Moreover, the Based on these experimental results, we tentatively propose a plausible mechanism for photocatalytic degradation of organic dyes over CuS under simulated solar light irradiation, in Figure 7. CuS with a 3D hierarchical structure has been demonstrated to be an efficient Fenton-like reagent [22]. When CuS is excited, the reaction of photo-generated electrons with H 2 O 2 generates OH· [48], enabling the direct oxidation of adsorbed organic dyes by photo-generated holes [49]. Moreover, the 3D hierarchical network structure of CuS favors the transmission of photo-generated electrons, which, in turn, facilitates the separation of the charge-carrier. Furthermore, the large surface area of a 3D hierarchical network structure of CuS might generate abundant catalytic sites because of improved contact and interaction between reactants and active sites. Therefore, the generation of abundant photo-generated holes and OH· radicals is ascribed to the synergistic effects of the above-mentioned processes, which considerably improves the degradation efficiency of the CuS catalyst with a 3D hierarchical network structure.

Photocatalysts Reaction Solution
Catalysts 2019, 9, x FOR PEER REVIEW 7 of 10 3D hierarchical network structure of CuS favors the transmission of photo-generated electrons, which, in turn, facilitates the separation of the charge-carrier. Furthermore, the large surface area of a 3D hierarchical network structure of CuS might generate abundant catalytic sites because of improved contact and interaction between reactants and active sites. Therefore, the generation of abundant photo-generated holes and OH· radicals is ascribed to the synergistic effects of the abovementioned processes, which considerably improves the degradation efficiency of the CuS catalyst with a 3D hierarchical network structure.

Materials
All materials and chemicals in this study were used directly without additional purification. Deionized water was acquired from local sources.

Preparation of 3D Hierarchical CuS Catalysts
The preparation of 3D hierarchical CuS catalysts was carried out via one-step heating sulfuration. Copper foam (1 cm × 1 cm, 1.5 mmol) and sulfur powder (3.0 mmol) were heated at 400 °C under N2 atmosphere for 5 h to yield the 3D hierarchical CuS catalyst.

Characterization
X-ray diffraction (XRD) patterns were recorded on a Bruker D8 Advance X-ray powder diffractometer (Karlsruhe, Germany) using Ni-filtered Cu Kα radiation. The whole solid was used for the XRD measurement. The optical property of the sample was determined using a UV−vis spectrophotometer (Perkin Elmer, Fremont, CA, USA). The Brunauer-Emmett-Teller (BET) surface areas and pore sizes of CuS samples were determined on the basis of nitrogen adsorption-desorption isotherms (Micromeritics Company, Norcross, GA, USA). X-ray photoelectron spectroscopy (XPS) measurements (Thermo Fisher Scientific, Waltham, MA, USA) were measured on an ESCALAB 250 photoelectron spectroscope, with a monochromatic Al Kα source. The powder samples were used for the characterization measurements. The morphologies of the obtained samples were taken on a ZEISS SIGMA field emission scanning electron microscope (SEM) (Carl Zeiss Ltd., Welwyn Garden City, UK). Transmission electron microscopy (TEM) images were obtained using a FEI Tecnai G2 F30 electron microscope (FEI Company, Hillsboro, OR, USA). The total organic carbon (TOC) values were measured using a TOC-2000 apparatus (Shanghai, China).

Materials
All materials and chemicals in this study were used directly without additional purification. Deionized water was acquired from local sources.

Preparation of 3D Hierarchical CuS Catalysts
The preparation of 3D hierarchical CuS catalysts was carried out via one-step heating sulfuration. Copper foam (1 cm × 1 cm, 1.5 mmol) and sulfur powder (3.0 mmol) were heated at 400 • C under N 2 atmosphere for 5 h to yield the 3D hierarchical CuS catalyst.

Characterization
X-ray diffraction (XRD) patterns were recorded on a Bruker D8 Advance X-ray powder diffractometer (Karlsruhe, Germany) using Ni-filtered Cu Kα radiation. The whole solid was used for the XRD measurement. The optical property of the sample was determined using a UV−vis spectrophotometer (Perkin Elmer, Fremont, CA, USA). The Brunauer-Emmett-Teller (BET) surface areas and pore sizes of CuS samples were determined on the basis of nitrogen adsorption-desorption isotherms (Micromeritics Company, Norcross, GA, USA). X-ray photoelectron spectroscopy (XPS) measurements (Thermo Fisher Scientific, Waltham, MA, USA) were measured on an ESCALAB 250 photoelectron spectroscope, with a monochromatic Al Kα source. The powder samples were used for the characterization measurements. The morphologies of the obtained samples were taken on a ZEISS SIGMA field emission scanning electron microscope (SEM) (Carl Zeiss Ltd., Welwyn Garden City, UK). Transmission electron microscopy (TEM) images were obtained using a FEI Tecnai G2 F30 electron microscope (FEI Company, Hillsboro, OR, USA). The total organic carbon (TOC) values were measured using a TOC-2000 apparatus (Shanghai, China).

Evaluation of Photocatalytic Activity
To assess the photocatalytic performance of the catalysts, MB and RhB were used as the model organic dyes. Typically, the photocatalytic activity studies were conducted at 30 • C in a 100 mL quartz reactor (Beijing, China) containing a prepared CuS sample and a dye solution (10 mg L −1 , 40 mL) with one of the dyes: MB, RhB, or MB/RhB (a mixed solution of MB and RhB). H 2 SO 4 (2 mol/L) was used to adjust the pH value of the reaction solution to pH = 4, with 2 mol/L H 2 SO 4 . After adding 40 µL of H 2 O 2 , the reaction mixture was slowly stirred in the dark for 1h to achieve the adsorption-desorption equilibrium. The suspension was then irradiated with a Xe lamp of 300 W (PLS-SXE 300, Beijing Perfect Light Co. Ltd., Beijing, China). During the reaction, about 3 mL of solution was taken out at an interval, and immediately used for the determination of the dye solution's concentration by using a UV-Vis spectrophotometer (Perkin Elmer, Fremont, CA, USA). When the reaction was complete, the collected sample was washed with water and ethanol successively several times. After it was thoroughly dried, the prepared sample was ready for use.

Conclusions
In summary, a simple, facile, and one-step in situ heating sulfuration strategy was developed to prepare the CuS photocatalyst with a 3D hierarchical network structure. The prepared CuS exhibits excellent photocatalytic and recyclable performance for the degradation of MB, RhB, and MB/RhB dye solutions under simulated solar light irradiation. According to the results of this study, the excellent photocatalytic performance of fabricated CuS was attributed to its large surface area and abundant active sites. This work affords a novel and convenient method for the fabrication of CuS with a 3D hierarchical structure under mild conditions, as a highly efficient and recyclable photocatalyst.

Conflicts of Interest:
The authors declare no conflict of interest.