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Electrochemical Oxidation of Selected Micropollutants from Environment Matrices Using Boron-Doped Diamond Electrodes - Process Efficiency and Transformation Product Detection

MetadataDetails
Publication Date2024-12-11
JournalWater
AuthorsFilip GamoƄ, S. Ć»abczyƄski, MaƂgorzata SzopiƄska, Mattia Pierpaoli, Dawid Zych
InstitutionsGdaƄsk University of Technology, Silesian University of Technology
AnalysisFull AI Review Included

Technical Documentation & Analysis: Electrochemical Oxidation using 6CCVD BDD Electrodes

Section titled “Technical Documentation & Analysis: Electrochemical Oxidation using 6CCVD BDD Electrodes”

This research validates the superior performance of Boron-Doped Diamond (BDD) anodes, fabricated via Microwave Plasma-Assisted Chemical Vapour Deposition (MWPECVD), for advanced electrochemical oxidation (EO) of persistent micropollutants.

  • Exceptional Removal Efficiency: The EO-BDD process achieved removal efficiencies exceeding 99% for Bisphenol A (BPA) and >96% for Diclofenac (DCF) in complex, real-world matrices, including Landfill Leachate (LL) and Treated Wastewater (TWW-D).
  • Material Validation: The study confirms that BDD electrodes, due to their non-polar nature and broad oxygen overpotential window, exhibit exceptional resistance to fouling and enable the generation of powerful oxidizing species (hydroxyl and sulfate radicals).
  • Custom Doping Impact: Two distinct boron doping levels (0.5 k and 10 k) were tested, demonstrating that while both achieved high removal rates, precise doping control is critical for optimizing performance in specific matrices.
  • Broad Application Scope: Beyond micropollutants, the EO-BDD process effectively removed Chemical Oxygen Demand (COD) (up to 94.24%) and Ammonium Nitrogen (N-NH4+) (up to 78.25%) from LL, positioning BDD as a viable technology for quaternary wastewater treatment.
  • Fabrication Match: The electrodes were fabricated on 50-mm Niobium substrates using MWPECVD—a core capability offered by 6CCVD for custom BDD anode production.
  • Regulatory Compliance: The findings support the adoption of EO-BDD technology to meet stringent new EU Directive requirements for micropollutant removal in municipal and industrial wastewater.

The following hard data points were extracted from the experimental setup and results, highlighting the critical parameters for BDD fabrication and electrochemical performance.

ParameterValueUnitContext
Anode MaterialBoron-Doped Diamond (BDD)N/AMWPECVD on Niobium substrate
Substrate Diameter50mmNiobium
Low Boron Doping Level (0.5 k)~1.5 x 1017at/cmÂłUsed for comparison of efficiency
High Boron Doping Level (10 k)3 x 1021at/cmÂłUsed for comparison of efficiency
Anode Geometric Area10.5cmÂČUsed in 400-mL undivided electrolytic cell
Anode-Cathode Distance2.5cmMaintained during EO tests
Current Density (LL)120mA/cmÂČOptimized for Landfill Leachate matrix
Current Density (TWW)25mA/cmÂČOptimized for Treated Wastewater matrices
Maximum BPA Removal (LL)>99.85%Achieved after 4 h treatment
Maximum DCF Removal (LL)>99.23%Achieved after 4 h treatment
Maximum COD Removal (LL)94.24%Achieved after 8 h treatment (10 k BDD)
Maximum N-NH4+ Removal (LL)78.25%Achieved after 8 h treatment (10 k BDD)
Initial LL Chloride Concentration2690 ± 70mg/LHigh salinity matrix, facilitating indirect EO

The BDD electrodes were fabricated using highly controlled MPCVD processes, which are standard capabilities at 6CCVD.

  1. Substrate Preparation: 50-mm diameter Niobium substrates were prepared via sandblasting, followed by cleaning in acetone and isopropanol in an ultrasonic bath.
  2. Seeding: Substrates were seeded using a water-based diamond slurry via sonication to ensure high nucleation density.
  3. Deposition Method: Microwave Plasma-Assisted Chemical Vapour Deposition (MWPECVD) was utilized for diamond film growth.
  4. Microwave Power: Maintained at 1300 W.
  5. Total Pressure: Maintained at 50 Torr.
  6. Substrate Temperature: Set to 700 °C to control crystal quality and doping incorporation.
  7. Gas Mixture: H2, CH4, and B2H6 were used, with B2H6 flow rates precisely adjusted to achieve the two target boron doping levels (0.5 k and 10 k).
  8. Electrochemical Testing: Experiments were conducted under galvanostatic conditions in a custom 400-mL undivided electrolytic cell, using the BDD film as the anode and stainless-steel mesh as the cathode.

This research demonstrates the critical role of high-quality, custom-engineered BDD electrodes in advanced water treatment. 6CCVD is uniquely positioned to supply the materials and customization required to replicate, scale, and extend this research.

Research Requirement6CCVD Solution & CapabilityTechnical Advantage & Sales Driver
Material SpecificationHeavy Boron Doped PCD (Polycrystalline Diamond)Our MPCVD BDD films provide the necessary metallic conductivity and chemical stability for high-efficiency EO, ensuring long electrode lifetime and superior performance compared to conventional anodes (e.g., Ti/Pt).
Custom Doping LevelsPrecision BDD Doping Control6CCVD offers precise control over boron incorporation, allowing researchers to specify doping levels from 1017 at/cmÂł (0.5 k equivalent) up to 1021 at/cmÂł (10 k equivalent) to optimize radical generation and current efficiency for specific matrices (e.g., high-salinity LL vs. low-COD TWW).
Substrate CompatibilityBDD on Refractory Metals (Nb, Ta, W)The paper utilized 50-mm Niobium substrates. 6CCVD routinely deposits BDD films on Niobium, Tantalum, and Tungsten, providing robust, conductive, and chemically inert electrode foundations suitable for industrial scaling.
Scaling RequirementsLarge Area PCD PlatesWhile the study used 50-mm wafers, 6CCVD can supply custom PCD plates up to 125mm in diameter, facilitating the transition from lab-scale research to pilot-scale electrochemical reactors.
Electrode GeometryCustom Dimensions and Laser CuttingWe offer custom fabrication services, including precise laser cutting, to meet exact geometric specifications (e.g., 10.5 cmÂČ anode area) required for specific electrolytic cell designs.
Thickness ControlBDD Film Thickness (0.1 ”m - 500 ”m)6CCVD guarantees precise control over BDD film thickness, ensuring optimal electrochemical performance and cost efficiency for both thin-film anodes and thick, self-supporting structures.
Engineering SupportIn-House PhD Team Consultation6CCVD’s expert material scientists can assist researchers in selecting the optimal BDD material (doping, thickness, substrate) for advanced oxidation processes (AOPs), micropollutant degradation, and electrochemical sensing projects.

For custom specifications or material consultation regarding BDD anodes for advanced oxidation processes, visit 6ccvd.com or contact our engineering team directly.

View Original Abstract

Bisphenol A (BPA) and diclofenac (DCF) are among the most prevalent micropollutants in aquatic environments, with concentrations reaching up to several hundred ”g/L. These compounds pose significant risks to biodiversity and environmental health, necessitating the development of effective removal methods. However, both BPA and DCF can be resistant to conventional treatment technologies, highlighting the need for innovative approaches. Electrochemical oxidation (EO) has emerged as a promising solution. In this study, we assessed the effectiveness of EO using boron-doped diamond (BDD) anodes to remove BPA and DCF from two types of treated wastewater (TWW-W and TWW-D) and landfill leachate (LL). The evaluation included an analysis of the removal efficiency of BPA and DCF and the identification of transformation products generated during the process. Additionally, the feasibility of the EO-BDD process to remove ammonium nitrogen (N-NH4+) and organic compounds present in these environmental matrices was investigated. The EO-BDD treatment achieved remarkable removal efficiencies, reducing BPA and DCF concentrations by over 96% in LL and TWW-W. Transformation product analyses identified four intermediates formed from parent compounds during the oxidation process. Furthermore, the EO-BDD process effectively removed both chemical oxygen demand (COD) and ammonium nitrogen from LL, although weaker results were observed for TWWs. These findings underscore the potential of the EO-BDD process as an effective method for the removal of BPA and DCF from challenging matrices, such as wastewater containing micropollutants. It also shows promise as a complementary technology for enhancing current conventional wastewater treatment methods, especially biological degradation.

  1. 2019 - Performance of secondary wastewater treatment methods for the removal of contaminants of emerging concern implicated in crop uptake and antibiotic resistance spread: A review [Crossref]
  2. 2020 - Antimicrobial pharmaceuticals in the aquatic environment—Occurrence and environmental implications [Crossref]
  3. 2021 - Oxidative degradation and mineralisation of the endocrine-disrupting chemical bisphenol A by an eco-friendly system based on UV-solar/H2O2 with reduction of genotoxicity and cytotoxicity levels [Crossref]
  4. 2024 - Bisphenol A in dairy products: Amount, potential risks, and various analytical methods—A systematic review [Crossref]
  5. 2017 - Occurrence and effects of plastic additives on marine environments and organisms: A review [Crossref]
  6. 1998 - Xenoestrogens: The emerging story of bisphenol A [Crossref]
  7. 2019 - Assessment of bisphenol-A in the urban water cycle [Crossref]
  8. 2015 - Exploring potential contributors to endocrine disrupting activities in Taiwan’s surface waters using yeast assays and chemical analysis [Crossref]
  9. 2014 - Fate of diclofenac in municipal wastewater treatment plants—A review [Crossref]