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. 2020 Sep 11;5(37):23808-23821.
doi: 10.1021/acsomega.0c03019. eCollection 2020 Sep 22.

Rational Design of W-Doped Ag3PO4 as an Efficient Antibacterial Agent and Photocatalyst for Organic Pollutant Degradation

Affiliations

Rational Design of W-Doped Ag3PO4 as an Efficient Antibacterial Agent and Photocatalyst for Organic Pollutant Degradation

Aline B Trench et al. ACS Omega. .

Abstract

Bacterial and organic pollutants are major problems with potential adverse impacts on human health and the environment. A promising strategy to alleviate these impacts consists in designing innovative photocatalysts with a wider spectrum of application. In this paper, we report the improved photocatalytic and antibacterial activities of chemically precipitated Ag3PO4 microcrystals by the incorporation of W at doping levels 0.5, 1, and 2 mol %. The presence of W directly influences the crystallization of Ag3PO4, affecting the morphology, particle size, and surface area of the microcrystals. Also, the characterization via experimental and theoretical approaches evidenced a high density of disordered [AgO4], [PO4], and [WO4] structural clusters due to the substitution of P5+ by W6+ into the Ag3PO4 lattice. This leads to new defect-related energy states, which decreases the band gap energy of the materials (from 2.27 to 2.04 eV) and delays the recombination of e'-h pairs, leading to an enhanced degradation process. As a result of such behaviors, W-doped Ag3PO4 (Ag3PO4:W) is a better visible-light photocatalyst than Ag3PO4, demonstrated here by the photodegradation of potential environmental pollutants. The degradation of rhodamine B dye was 100% in 4 min for Ag3PO4:W 1%, and for Ag3PO4, the obtained result was 90% of degradation in 15 min of reaction. Ag3PO4:W 1% allowed the total degradation of cephalexin antibiotic in only 4 min, whereas pure Ag3PO4 took 20 min to achieve the same result. For the degradation of imidacloprid insecticide, Ag3PO4:W 1% allowed 90% of degradation, whereas Ag3PO4 allowed 40%, both in 20 min of reaction. Moreover, the presence of W-dopant results in a 16-fold improvement of bactericidal performance against methicillin-resistant Staphylococcus aureus. The outstanding results using the Ag3PO4:W material demonstrated its potential multifunctionality for the control of organic pollutants and bacteria in environmental applications.

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Conflict of interest statement

The authors declare no competing financial interest.

Figures

Figure 1
Figure 1
XRD patterns of Ag3PO4, Ag3PO4:W 0.5%, Ag3PO4:W 1%, and Ag3PO4:W 2% samples.
Figure 2
Figure 2
Schematic representation of the 2 × 2 × 2 supercell periodic models built for (a) pure Ag3PO4 and (b) Ag3PO4:W.
Figure 3
Figure 3
(a) Raman spectra and (b) A1 Raman mode of Ag3PO4, Ag3PO4:W 0.5%, Ag3PO4:W 1%, and Ag3PO4:W 2%.
Figure 4
Figure 4
(a) XPS spectra of Ag3PO4, Ag3PO4:W 0.5%, and Ag3PO4:W 1% samples and (b) W 4f high-resolution spectra of Ag3PO4:W 0.5% and Ag3PO4:W 1%.
Figure 5
Figure 5
FESEM images of (a) Ag3PO4, (b) Ag3PO4:W 0.5%, and (c) Ag3PO4:W 1%. TEM images of the Ag3PO4:W 1% sample: (d) high-angle annular dark-field (HAADF) image showing two regions comprising Ag3PO4:W 1% and Ag0 structures (yellow and red dotted circles, respectively), (e–h) EDS mapping of Ag, O, P, and W elements, (i, j) high-resolution TEM (HR-TEM) images of a border region of the Ag3PO4:W 1% crystal, and (k, l) HR-TEM images of Ag0 nanostructures.
Figure 6
Figure 6
(a) UV–visible absorption spectra and band-gap energies for Ag3PO4, Ag3PO4:W 0.5%, and Ag3PO4:W 1% samples. Calculated band structures of (b) Ag3PO4 and (c) Ag3PO4:W models.
Figure 7
Figure 7
UV–visible absorption spectra of RhB upon photodegradation in the presence of (a) Ag3PO4, (b) Ag3PO4:W 0.5%, and (c) Ag3PO4:W 1%. (d) Photocatalytic degradation of RhB (1.0 × 10–1 mol L–1) in the absence and in the presence of Ag3PO4 and Ag3PO4 doped with different amounts of W and (e) Langmuir–Hinshelwood plot for the determination of the rate constant.
Figure 8
Figure 8
(a) UV–visible absorption spectra of RhB photodegradation in the presence of Ag3PO4:W 1% collected in time less than 5 min and (b) run cycles of RhB degradation using Ag3PO4:W 1% under visible-light irradiation. (c) Influence of the scavengers on the degradation of RhB in the presence of Ag3PO4:W 1% under visible-light irradiation and (d) analysis of total organic carbon (TOC) for degradation of RhB in the presence of Ag3PO4:W 1% under 30 min of visible-light irradiation.
Figure 9
Figure 9
(a) Photocatalytic degradation of CFX in the presence of Ag3PO4 and Ag3PO4:W 1% in a linear plot and (b) analysis of total organic carbon for degradation of CFX in the presence of Ag3PO4 and Ag3PO4:W 1% under 30 min of visible-light irradiation. (c) Photocatalytic degradation of IMC in the presence of Ag3PO4 and Ag3PO4:W 1% in a linear plot and (d) analysis of total organic carbon for degradation of IMC in the presence of Ag3PO4 and Ag3PO4:W 1% under 30 min of visible-light irradiation.
Figure 10
Figure 10
Bacterial growth values (Log10) as a function of the concentrations (mg mL–1) of Ag3PO4 and Ag3PO4:W.

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