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. 2025 Jun 20;15(1):20165.
doi: 10.1038/s41598-025-05597-7.

Ag₃PO₄@ZnO kraft lignin composite for optimized photocatalytic degradation of methylene blue using response surface methodology

Affiliations

Ag₃PO₄@ZnO kraft lignin composite for optimized photocatalytic degradation of methylene blue using response surface methodology

Marwa S Abdelkader et al. Sci Rep. .

Abstract

This research explores the use of kraft lignin (KL), derived from pulping black liquor waste, as a supportive medium for Ag3PO4@ZnO (AZ-NC) p-n heterojunction and design a new cost-effective ternary KL-Ag3PO4@ZnO nanocomposite (AZKL). The aim is to improve its photocatalytic efficiency in treating textile wastewater while tackling environmental issues such as chemical stability, charge carrier separation, and the production of secondary waste during the photocatalytic process. The response surface methodology (RSM) analysis shows that AZKL is highly effective catalyst for methylene blue (MB: 10 - 25 mg/L) dye mineralization, achieving a rapid decolorization (> 98.2% within 40 min) under visible light at a near-neutral pH (7.48) with maintained high catalytic activity across four consecutive cycles. This outstanding performance is driven by the synergistic interplay of AZKL-based photocatalysis and advanced oxidation process using 0.03% H2O2 co-catalyst. Gas chromatography-mass spectrometry analysis reveals that MB dye degrades stepwise into intermediates such as N, N-dimethyl-p-phenylenediamine, hydroquinone, and formic acid, ultimately mineralizing completely into CO₂ and H₂O. The dominant reactive oxygen species driven this multi-step process are identified as hydroxyl radicals (•OH) and photogenerated holes (h⁺), with H₂O₂ and superoxide radicals (•O₂⁻) playing secondary roles. The data also highlights the multifunctional role of KL support, which enhances charge carrier separation, captures dye molecules, and prevents Zn2+/Ag+ ion leaching (less than 0.2 ppm) into the treated water during photocatalysis. This is facilitated by the electron-donating polyphenolic hydroxyl groups on the KL surface, which reduce Ag⁺ to metallic silver and stabilize AZ-NC heterojunction under light irradiation, creating Schottky junctions that improve charge transfer efficiency while reducing secondary contamination risks. A practical case study further illustrates the effectiveness of AZKL in treating real textile effluents, as evidenced by the improved biodegradability of residual organic matter, indicated by changes in chemical/biological oxygen demands (COD/BOD) ratios from 2.62 to 1.47 and inhibition tests against E. coli, meeting wastewater discharge standards. The findings emphasize that the AZKL composite could serve as an effective and adaptable photocatalyst for breaking down organic pollutants and treating intricate wastewater systems.

Keywords: Ag3PO4@ZnO p-n heterojunction; Kraft lignin; Response surface methodology; Textile wastewater treatment; Waste valorization.

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Conflict of interest statement

Declarations. Competing interests: The authors declare no competing interests.

Figures

Fig. 1
Fig. 1
The surface chemistry and textural features of the as-prepared photocatalysts (AZKL, ZnO, and AZ-NC): (a) FTIR spectra, (b) Zeta potential profiles as a function of solution pH (at 25 ± 1 °C), and (c) N2-adsorption-desorption isotherm (inset: pore size distribution curves).
Fig. 2
Fig. 2
HRTEM images of the as-prepared photocatalysts: (a) ZnO NPs, (b) AZ-NC, and (c) AZKL nanocomposite.
Fig. 3
Fig. 3
Morphological features of AZKL (compared with ZnO and AZ-NC): (a-c) SEM micrographs [(a) ZnO, (b) AZ-NC, and (c) AZKL] and (d) DLS particle size distribution profiles.
Fig. 4
Fig. 4
Response surface contour plots of MB dye removal rate by AZKL (a1, b1, c1, and d1) and AZ-NC (a2, b2, c2, and d2) as a function of 2-way interactive effects of each two operational variables (while keeping the other factors at their mid-level settings): (a)X1 × 2, (b) X1 × 3, (c) X2 × 3, and (d) X3 × 4.
Fig. 5
Fig. 5
The photocatalytic stability and applicability of AZKL nanocomposite in wastewater treatment: (a) reusability cycle against 10 and 25 mg/L MB dye removal across 4 reuse cycles under optimum conditions (pH 7.48, 0.03% H₂O₂, and 4.92 g/L of catalyst), (b) performance stability in extreme pH and saline conditions against 25 mg/L MB dye (at 0.03% H₂O₂ and 4.92 g/L of catalyst), and (C) the UV-Vis spectrum for actual wastewater before and after solar-light induced photocatalytic treatment.
Fig. 6
Fig. 6
Photocatalytic reaction mechanism of MB dye onto AZKL under light irradiation: (a) charge transfer mechanism and (b) the radical scavenging test.

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