1. Introduction
Persistent organic pollutants impart adverse effects on human health via various routes, including endocrine disorders, congenital defects, organ malfunction, chronic illness and even death in some cases [
1,
2,
3]. The degradation of such pollutants through photocatalytic reactions are being explored extensively by the researchers because of their capability to generate robust oxidizing radicals under solar irradiation that mineralize persistent organic pollutants completely through oxidation reactions [
4]. Nanoscale semi-conductor metal oxides, such as copper oxide (CuO), and their composites, are among the popular agents for efficient photocatalytic activity [
5]. CuO is a narrow bandgap semi-conductor with plentiful availability, non-toxicity, low cost, p-type semi-conductivity, excellent catalytic proficiency, and excellent chemical stability. Nevertheless, there are some limitations in the practical use of CuO as an efficient photocatalyst. Comparatively feebler visible light absorption, altered accessibility to reaction sites, and the higher likelihood of the recombination of photon-generated electron-hole pairs come up as the central issues [
6,
7,
8].
We improved the limitations of CuO via its chemical combination with the walls of SWCNTs through a straightforward recrystallization method accompanied by calcination. We prepared a group of CuO-SWCNT hetero-composites maintaining the recrystallization parameters constant and changing the durations of calcinations at a preset temperature (550 °C). We named the as-prepared composites as CuO-SWCNT-1, CuO-SWCNT-2, and CuO-SWCNT-3. We used those nanocomposites for the photocatalytic decomposition of methylene blue solution in natural sunlight exposure to convert it into harmless end products. The recycling potentiality of the as-synthesized composites was evaluated through their photocatalytic actions for five consecutive cycles. We found no substantial decrease in the photocatalytic activity and changes in their surface features after their recycling.
2. Materials and Methods
A homogeneous solution of copper (II) acetate hydrate (6.0 g) was prepared by dissolving it in ethanol (100 mL) in a beaker using bath sonication for an hour at room temperature (20 °C). SWCNTs (100 mg) were released into the above solution, and the resulting mixture was devised for magnetic stirring for one more hour. The magnetic stirring bar was withdrawn and the mixture was left untouched for recrystallization for 8 h. Recrystallized form of copper (II) acetate crystals-SWCNT aggregation was isolated from ethanol through vacuum filtration and the residual mass was dried at 70 °C in a previously heated oven for 2 h so that it is completely free of ethanol. The dried mass was finally calcined in a muffle furnace at 550 °C to construct CuO-SWCNT heterostructures. The detailed method of synthesis of nanocomposite catalysts is shown by a flowchart (
Figure 1).
3. Results
CuO nanocrystals chemically combined with the outer walls of SWCNTS and have resulted in the generation of the cauliflower-shaped nanocomposite particles with various sizes that range between 30 nm to 1 μm.
Figure 2a,b demonstrate the representative FE SEM images of the as-synthesized composites in the nano-cauliflower shape.
Figure 2c,d demonstrate the HR-TEM portrayals of the composites in which the chemical attachment of the constituents is evident. However, the nano-cauliflower architecture has been demolished in TEM images due to the strong bath sonication while preparing TEM samples. The size of the CuO-nanocrystals surrounding the SWCNTs, as measured during HR-TEM analysis, ranges between 2 to 15 nm.
X-ray diffraction (XRD) spectra of the samples confirmed monoclinic CuO geometry in the composite and no change in the crystal structure of SWCNTs during chemical combination. The crystallite size, which was calculated from the XRD profile using the Scherrer Equation, was found to be 23.95 nm. The chemical bonding between CuO and SWCNTs was further confirmed by HR-XPS, which demonstrates the oxidation states and chemical environments of chemically combined Cu, O and C in the nanocomposites. XPS results disclose that crystalline CuO and SWCNTs have combined through the origination of covalent bonds as CuO-SWCNT or Cu-OOC-SWCNT. As demonstrated via the XPS results, the TGA profiles further verified the chemical bonding between the SWCNTs and CuO nanocrystals. Such a chemical bond generates a permanent heterojunction between the surfaces of the constituents, which is crucial for the enhanced photocatalytic performance.
The improvement in the optical characteristics of the as-synthesized heterostructures were asserted through UV-vis diffuse reflectance spectra. Those spectra revealed a significant shrinkage in the bandgap energy of the composite samples compared to the pristine CuO, affirming that chemical bonding with SWCNTs has improved the catalytic properties of the samples. Specific surface area, pore-size distribution and pore volume of the samples were examined via Brunauer–Emmett–Teller (BET) and Barrett–Joyner–Halenda (BJH) analyses, and the findings display that the specific surface areas of the composite samples have augmented compared to pristine CuO due to its chemical bonding with SWCNTs.
The as-prepared CuO-SWCNT photocatalysts were investigated for their photocatalytic efficiency by accessing the catalyzed break-down of the MB solution under natural sunlight exposure. Among the different samples, CuO-SWCNT-3 displayed the best photocatalytic performance achieving 96% photo-decomposition of MB solution through 2 h of natural sunlight irradiation. However, CuO-SWCNT-2 and CuO-SWCNT-1 caused 93% and 90% photo-degradation of the MB solution, respectively under similar conditions of exposure and at the same duration. The enhanced photocatalytic performance of the composites is credited to the increased visible light absorption by the photocatalysts, production of light-induced electron-hole sets and their separation to avoid recombination so that the charge carriers can participate in the redox reactions for the decomposition of organic dyes such as MB.
4. Conclusions
Our as-synthesized photocatalysts with interesting nano-cauliflower-like structures are capable of remarkable degradation of organic dyes such as MB solutions under natural sunlight exposure. The origination of heterojunctions between CuO and SWCNTs was confirmed via different characterization techniques such as HR-TEM, XRD, TGA/DSC and XPS. Among the different samples, CuO-SWCNT-3 displayed the best photocatalytic performance, achieving 96% photo-decomposition of MB solution in 2 h natural sunlight irradiation. Similarly, CuO-SWCNT-2 and CuO-SWCNT-1 caused 93% and 90% photo-degradation of the MB solution, respectively, under similar conditions of exposure and at the same duration. The results reveal that CuO-SWCNT nanocomposites can be used as efficient photocatalysts for the deterioration of water pollutants like organic dyes.
Author Contributions
J.R.H. supervised and provided resources, support and guidance in whole research work, K.P.S. designed and performed the experiments, analyzed data and wrote the article, M.A.I., M.A.H., J.A. analyzed data and read the manuscript rigorously to upgrade it. All authors have read and agreed to the published version of the manuscript.
Acknowledgments
This work was supported by Korean Government, NRF-2018R1A2B6006155.
Conflicts of Interest
The authors declare no conflict of interest.
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