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Synergistic mineralization of ofloxacin in electro-Fenton process with BDD anode - Reactivity and mechanism

MetadataDetails
Publication Date2023-05-09
JournalSeparation and Purification Technology
AuthorsWeilu Yang, Nihal Oturan, Jialin Liang, Mehmet A. Oturan
InstitutionsZhongkai University of Agriculture and Engineering, UniversitĂŠ Gustave Eiffel
Citations24
AnalysisFull AI Review Included

This research explores the enhanced performance and mechanism of the electro-Fenton (EF) process utilizing a Boron-Doped Diamond (BDD) anode for the mineralization of the antibiotic Ofloxacin (OFLO).

  • Synergistic Mechanism: The EF-BDD system leverages the simultaneous generation of homogeneous hydroxyl radicals (•OH) in the bulk solution and highly potent heterogeneous hydroxyl radicals (BDD(•OH)) on the BDD anode surface, leading to synergistic degradation.
  • Performance Improvement: EF-BDD improved the decay kinetics of OFLO by 1.4-2.6 times compared to the standard Anodic Oxidation (AO) process.
  • Cost Efficiency: Energy consumption (EC) for OFLO removal was reduced by 28%-41% in EF-BDD compared to AO, demonstrating superior cost-effectiveness, especially under low current density conditions (4.2 mA cm-2).
  • Current Density Effects: High current densities (16.6 mA cm-2) accelerate BDD(•OH) production, causing the heterogeneous reaction pathway to dominate. This results in the synergistic factor (SF) decreasing or becoming negative (SF = -0.08 at 16.6 mA cm-2).
  • Complete Mineralization: The process achieved 100% Total Organic Carbon (TOC) removal, confirming complete mineralization of OFLO and its refractory short-chain carboxylic acid intermediates (like oxalic acid).
  • Toxicity Reduction: Acute toxicity (LC50) and bioaccumulation factors of all identified transformation products (OTPs) were significantly lower (up to 85 times less toxic) than the parent OFLO compound.
ParameterValueUnitContext
Anode MaterialBoron-Doped Diamond (BDD)N/ANon-active anode type
Cathode MaterialEEGr-CFN/AElectrochemically exfoliated graphene-based carbon felt
Initial OFLO Concentration0.1mMCorresponding to 21.6 mg L-1 TOC
Optimal Fe2+ Concentration0.2mMCatalyst concentration for EF process
Solution pH3N/AOptimized for Fenton reaction
Electrolyte Concentration50mMNa2SO4 supporting electrolyte
Anode Surface Area24cm24 x 6 cm2 effective area
Cathode Surface Area6cm22 x 3 cm2 effective area
Max Current Density Tested16.6mA cm-2Achieved 100% OFLO degradation in 10 min
Max TOC Removal (EF-BDD)100%Achieved at 16.6 mA cm-2 (240 min)
Lowest Energy Consumption (EC)0.5kWh (gTOC)-1EF-BDD process at 4.2 mA cm-2
Absolute Rate Constant (kOFLO)3.86 x 109M-1s-1Oxidation of OFLO by homogeneous •OH
Maximum Synergistic Factor (SF)0.28N/AObserved at 4.2 mA cm-2
H2O2 Accumulation Rate (Max)6.7mg h-1 cm-2Observed at 8.3 mA cm-2

The study employed the electro-Fenton (EF) process in a single-chamber electrolytic cell, comparing BDD (EF-BDD) against a Dimensionally Stable Anode (DSA) (EF-DSA) and Anodic Oxidation (AO) using BDD.

  1. Cathode Preparation (EEGr-CF): Graphene (EEGr) was synthesized via electrochemical exfoliation. EEGr and carbon black (1:4 mass ratio) were mixed with PTFE binder and solvents, coated onto carbon felt (CF), and annealed at 360 °C for 30 min under N2 atmosphere.
  2. Electrolysis Setup: Experiments were conducted in 250 mL cells using BDD as the anode and the prepared EEGr-CF as the cathode (2 cm separation). The solution was maintained at pH 3 and continuously aerated (0.75 L min-1) to ensure O2 saturation for H2O2 generation.
  3. Kinetic Analysis: Pseudo-first-order rate constants (kapp) were determined by monitoring OFLO decay via HPLC. The Synergistic Factor (SF) was calculated using the kinetic constants of EF-BDD, AO, and EF-DSA processes (Eq. 7) to quantify the combined effect of •OH and BDD(•OH).
  4. Absolute Rate Constant Determination: The second-order rate constant (kOFLO) for OFLO oxidation by •OH was determined using the competition kinetic method, employing 4-hydroxybenzonic acid (4-HBA) as the known standard competitor.
  5. Mineralization and By-product Tracking: Total Organic Carbon (TOC) removal was measured to assess mineralization efficiency. Carboxylic acids (e.g., oxalic, oxamic, formic) and inorganic ions (NH4+, NO3-, F-) were monitored using HPLC and Ion Chromatography (IC).
  6. Toxicity Assessment: Acute toxicity (LC50), developmental toxicity, and bioaccumulation factors of OFLO and its transformation products (OTPs) were predicted using quantitative structure-activity relationship (QSAR) modeling via the Toxicity Estimation Software Tool (T.E.S.T.).

The findings are highly relevant to industries requiring robust and cost-effective methods for treating refractory organic pollutants, particularly those containing pharmaceutical residues.

  • Pharmaceutical Wastewater Treatment: Direct application for the complete destruction and mineralization of persistent antibiotics (like fluoroquinolones) in effluent streams, ensuring compliance with strict environmental discharge limits.
  • Advanced Water Purification: Integration of EF-BDD technology into tertiary treatment stages for municipal or industrial wastewater to remove trace organic contaminants (TOCs) and micropollutants.
  • BDD Electrode Technology: Validation of BDD anodes as superior, non-active electrode materials for electrochemical advanced oxidation processes (EAOPs), driving demand for high-quality BDD film manufacturing.
  • Cost-Optimized Remediation: Implementation of EF-BDD at optimized low current densities (e.g., 4.2 mA cm-2) to maximize the synergistic effect and minimize energy consumption (EC), offering a competitive advantage over high-energy AO processes.
  • Environmental Safety: The demonstrated ability to reduce the toxicity and bioaccumulation potential of degradation products is crucial for environmental risk management in water reuse and discharge scenarios.
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