Ag2C2O4 /Ag3PO4 composites as efficient photocatalyst for solar light driven degradation of dyes pollutants
Graphical abstract
Introduction
One of the most important goals of water treatment is the elimination inorganic pollutant and the mineralization of organic pollutant to nontoxic inorganic compounds [1]. By increasing global industrialization, most of the traditional contamination purification technologies couldn't meet the needs of environmental management [2]. In the several of decades, semiconductor-based photocatalytic oxidation as a green technique was becoming a promising approach for hydrogen production, CO2 conversion and degradation of various contaminants [[3], [4], [5]]. The photocatalysis method would generally utilize a powerful oxidizing species such as ●OH and ●O−2 radicals generated based on hole and electron, which causes a sequence of reactions afterwards to decompose the macromolecules into smaller and less toxic compounds. In various cases, the macromolecule is entirely mineralized into H2O, CO2 and mineral acids [[6], [7], [8]]. Nowadays, the dyes and pigments are extensively used in textile industry, while it in turn threatens aquatic organism ecosystem as well as damage human body [9,10]. Azo-based dyes are the most usual components applied in textile and other related industries. The presence of these dyes in wastewaters prevents the photosynthesis process of aquatic plants by absorbing visible light. Due of their long-term thermal and photo-stability and high water solubility, the removal of azo-based dyes from effluent is extremely difficult [11,12].
Solar light as one kind of promising renewable alternative energy offers a free, clean, non-polluting, stable resource. The wide spectrum of solar light consist of ultraviolet (UV), visible and near-infrared (NIR) that the major driving force for the development of efficient solar light driven photocatalysts [13,14]. Among various photocatalysts, metal oxides are the most suitable substances used for photocatalytic degradation due to high capacity for elimination of toxic contaminants [[15], [16], [17]]. Unfortunately, the wide band gap of most metal oxides such as TiO2 has limited its widespread application owing to it is activated solely by UV light [18,19]. Typically, different strategies for engineering the band gap of photocatalysts and extending their absorption to the visible light region used such as doping, coupling, and sensitization approaches. Meanwhile, coupling method has been studied deeply to develop efficient photocatalysts, but it still cannot satisfy the requirements for operational conditions [20]. In recent years, many silver-containing photocatalytic substances have received high attention due to their proper band gap and relatively good performance in degradation of contaminant [21,22]. In this regard, various semiconductors such as AgCl, AgBr, AgI, Ag2O, Ag2S, Ag2Se, Ag2CrO4, Ag2CO3, Ag2SO4, Ag2WO4, Ag3PO4, Ag3VO4 and β-AgVO3 have been used for preparation of various composite photocatalysts such as Ag@AgI–AgCl [23], AgX@Ag3PO4 [24], Ag2O/Ag2CO3 [25], AgBr/Ag2CrO4 [26], Ag2WO4/AgX [27], Ag3VO4–AgBr [28], Ag2S/Ag3PO4 [29]. Ag2C2O4 showed highly efficient and stable visible light photocatalytic activity and had a narrow band gap (~3.6–3.8 eV) semiconductor [30,31]. Feng et al. investigated photo-degradation of propylene and acetaldehyde gas by Ag2C2O4/TiO2 and Ag2C2O4 under visible light irradiation [30]. Abbasi et al. studied degradation of Orange G and Trypan blue by Ag2C2O4/Ag/g-C3N4 under solar light irradiation [31]. Silver phosphate (Ag3PO4) as one of the efficient photocatalysts is a semiconductor with indirect and direct band gaps (2.36 eV and 2.43 eV, respectively), making it promising as a photocatalyst for decomposition of organic pollutants under natural light [[32], [33], [34], [35]]. However, a main problem associated with Ag3PO4 is its poor photochemical stability due to the photocatalyst is irreversibly increased to metallic silver in the lack of an appropriate electron scavenger in aqueous solutions [36]. Degradation of Methylene blue in aqueous solution by graphene-modified nanosized Ag3PO4 is studied by Xiang et al. [37]. Also, Bu et al. [38] synthesized a z-Scheme Ag3PO4/Ag/WO3−x photocatalyst and used for degradation of Rodamine B in aqueous solution. Generally, the optimizations of contaminants degradation are performed by one variable at a time (OVAT) method which failure in estimation of interactions among variables that this limitation resolved by experimental design methods such as central composite design (CCD) [39]. These method represented relationship among variables with polynomial equation by reducing the number of experiments, cost and time [40,41].
In the present study, we report on the synthesis, characterization and photocatalytic activity of a new Ag2C2O4/Ag3PO4 nanocomposite. The Ag2C2O4/Ag3PO4 nanocomposite was prepared through a facile co-precipitation methods and then was characterized by FE-SEM, EDS, XRD, FTIR, PL and UV–Vis. The solar-light driven photocatalytic activity of Ag2C2O4/Ag3PO4 nanocomposite was evaluated based on the degradation of AB and EB organic dyes. CCD approach was used for optimization and evaluation of the influence of major variables (pH, irradiation time, dyes concentration, photocatalyst dosage). Furthermore, a possible mechanism for solar-light photoactivity of the nanocomposite for the enhancing photocatalytic efficiency was also proposed based on the active species trapping experiments.
Section snippets
Materials and apparatus
Silver nitrate (AgNO3), sodium oxalate (NaC2O4), Polyvinylpyrrolidone (PVP, polyvidone 25), hydrochloric acid (HCl) and analytical grade of AB (C22H14N6Na2O9S2) and EB (C20H8Br2N2O9) were purchased from Sigma-Aldrich, USA. Sodium hydroxide (NaOH), Sodium dihydrogen phosphate (NaH2PO4), absolute ethanol (C2H5OH, Merck, >99.9%), were purchased from Merck. Water purified in a Milli-Q system (Millipore, USA) was used for the preparation of solutions. X-ray diffraction (XRD, Philips PW 1880,
Characterization of photocatalyst
Morphology and particles size of the Ag2C2O4, Ag3PO4 and Ag2C2O4/Ag3PO4 nanocomposite were investigated by FESEM technique and the results are shown in Fig. 1a–c. Fig. 1b illustrates that the as-prepared Ag3PO4 sample consists of agglomerated spherical particles. FESEM images indicate that the nano-sized primary particles have suitable porosity to adsorb and photodegraded of AM, EB molecules. In addition, it is revealed that morphology of Ag2C2O4/Ag3PO4 in the figure is the nearly spherical
Conclusion
In summary, the Ag2C2O4/Ag3PO4 photocatalyst was synthesized through a co-precipitation method and characterized by FE-SEM, EDS, XRD, FTIR, PL and UV–Vis. The as-prepared photocatalysts used for degradation of binary mixture (Amido black 10B) AB and (Eosin B) EB as target pollutants in aqueous solution in BMS reactor under solar irradiation for investigation of photocatalytic performance. DRS test indicate the extension of light absorption in the visible zone while PL results confirm the
Authorship contributions
Please indicate the specific contributions made by each author (list the authors’ initials followed by their surnames, e.g., Y.L. Cheung). The name of each author must appear at least once in each of the three categories below. Category 1: Conception and design of study: Zohreh Moradi, Mehrorang Ghaedi, Mohammad Mehdi Sabzehmeidani, Hamid Abbasi Asl Acquisition of data: Hamid Abbasi Asl , Mohammad Mehdi Sabzehmeidani, Zohreh Moradi, Mehrorang Ghaedi, Analysis and/or interpretation of data:
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
All persons who have made substantial contributions to the work reported in the manuscript (e.g., technical help, writing and editing assistance, general support), but who do not meet the criteria for authorship, are named in the Acknowledgements and have given us their written permission to be named. If we have not included an Acknowledgements, then that indicates that we have not received substantial contributions from non-authors.
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2023, International Journal of Hydrogen EnergyCitation Excerpt :The FT-IR spectra of the photocatalyst were measured using Jasco FTIR 680 model (Japan) in the wavelength range of 4000–400 cm−1 using KBr model. Fig. 2 shows the XRD (X-ray diffraction) patterns of the Ag2C2O4/Ag@GNS composite, the Ag2C2O4 showed clear diffraction peaks at 2θ = 17.3°,28.9°,29.8°, 39.6°, 51.7°, and 61.8°, which can be perfectly matched to the crystalline planes of (01–1), (020), (11–1), (120), (13–1), and (01–6) with monoclinic phases of Ag2C2O4 (JCPDS No: 22-1335) [31]. The major peak detected at 2θ = 25.2°, exemplifies the amorphous planes of GNS with miller-indices value of (011).