(527e) Enhanced Stability and Activity of Series LaFexCu1-XO3 Perovskites for Ofloxacin Degradation from Wastewater: DFT Calculation, Mechanisms and Toxicity Evolution | AIChE

(527e) Enhanced Stability and Activity of Series LaFexCu1-XO3 Perovskites for Ofloxacin Degradation from Wastewater: DFT Calculation, Mechanisms and Toxicity Evolution

Authors 

Kumari, S., Durban University of Technology
Bux, F., Durban University of Technology
Introduction

In recent decades, the substantial production of wastewater by the pharmaceutical industry has prompted significant environmental apprehensions, primarily due to its detrimental impact on aquatic ecosystems and biodiversity [1]. A relevant example of pharmaceuticals detected in wastewater is ofloxacin (OFLX) (C18H20FN3O4), a member of the third generation of fluorinated quinolone antibiotics extensively prescribed for various bacterial infections. Several studies have been reported the levels of OFLX in various water settings, including sewage water (0.89 to 31.7 µg/L), hospital wastewater (35 µg/L), urban wastewater treatment plants (1.8 µg/L), and surface water (0.5 µg/L) [2,3]. Owing to potential toxicity, stable chemical structure, and low biodegradability, OFLX cannot be efficiently treat using conventional treatment methods. In the recent years, sulphate radical-based AOPs (SR-AOPs) have become more popular for degradation of emerging pollutants from aqueous media. Owing to stronger redox potential (2.5–3.1 V), higher selectivity of SO4•− radical compared to •OH radical, and longer life of (30–40 μs) SO4•− radical, SR-AOPs have demonstrated the excellent efficacy in degradation of emerging pollutants [4,5]. In order to further enhancing the efficacy of SR-AOPs, a series of perovskites were utilized and activated with peroxymonosulfate (PMS). In the present investigation, OFLX was degraded from aqueous media utilizing a series LaCuxFe1-xO3 perovskites synthesized by citric sol-gel method and activated with PMS. The synthesized perovskite was characterized by various analytical techniques e.g., FESEM/EDX, TEM, BET, FTIR, XRD, XPS and EIS. Subsequently, the effects of crucial parameters such as PMS dosage (250-1000 g/L), catalyst dosage (250-1000 g/L), solution pH (2-12), and reaction temperature (25-55 ℃) were analyzed on OFLX degradation along with PMS consumption in the LaFexCu1-xO3/PMS system. To evaluate the bio-toxicity of OFLX and their intermediate products analysis by ECOSAR prediction model. Identification of major reactive oxygen species (ROS) generated in the LaFexCu1-xO3/PMS system for ofloxacin degradation along with the economic evaluation of the treatment process. DFT calculations (e.g., Fukui function, electrostatic potential (ESP) mapping, and HOMO-LUMO structure) were evaluated to identification of strong attacking sites on ofloxacin molecule.

Methodology

All the batch experiments for OFLX degradation were conducted in 250 mL three neck glass reactor containing the 100 mL of OFLX solution maintained at 25 ℃ temperature. The total reflux condenser was fitted on the top of the reactor for preventing the vapour loss. The aqueous solution of OFLX were prepared in Milli-pore water with desired concentrations (5-20 mg/L).The concentration of OFLX was analyzed by HPLC system (Waters India, Ltd.), equipped with C-18 column and UV detector at 295 nm wavelength. The eluent was a binary mixture of methanol and pure Milli-Q water (proportion 25:75 v/v); eluent flow rate was 0.8 mL/min and injection volume of 20 mL (manually injected) in isocratic mode.

Results and conclusions

In order to assess the catalytic activity of synthesized perovskites LaFexCu1-xO3 catalysts, some initial experimental trials were conducted for OFLX degradation in aqueous solution. The maximum removal of OFLX was observed 4.65%, 5.12%, 7.82%, and 6.74% with the corresponding catalysts 0.2LFC, 0.4LFC, 0.6LFC, and 0.8LFC, without using any oxidant (PMS) as shown in Fig. 1a. Interestingly, when solely employing 1 mM of the oxidizing agent, maximum removal of OFLX was noticed 5.89% under the pH 7.2 and reaction temperature 25°C. Furthermore, while both catalyst and oxidant doses were introduced simultaneously into aqueous media, all catalysts showed remarkable catalytic efficacy in removing ofloxacin, with removal rates of 26.84%, 28.68%, 34.85%, and 29.78%, under the reaction conditions (e.g., 0.5 g/L catalyst dose, 1 mM PMS dose, pH 7.3, and 25 ℃ reaction temperature). To better understand the quantitative contribution of reactive oxygen species (ROS) generated in the LaFexCu1-xO3/PMS system, a series radical quenching experiments were conducted with various quenchers i.e., tert-butyl alcohol (TBA), L-histidine (LH), and ethanol (EtOH). Combined with intermediates analyzed by GC-MS, DFT calculation and literature survey, the possible transformation pathways of OFLX degradation were proposed systematically. To assess the economic viability of the catalyst, five consecutive cycle experiments were conducted for ofloxacin degradation under the optimum operating condition.

Key conclusions

The present study demonstrates that catalyst 0.6LFC exhibited the excellent degradation performance toward OFLX in the LaFexCu1-xO3/PMS system. The quenching experiments reveals that SO4•− radicals was dominant ROS for OFLX degradation in the LaFexCu1-xO3/PMS system. Furthermore, six potential routs of OFLX degradation were proposed based on the DFT calculation study, intermediates identified by GC-MS analysis and existing literature.

References

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