Efficient electrochemical degradation of poly- and perfluoroalkyl substances (PFASs) from the effluents of an industrial wastewater treatment plant
At a Glance
Section titled âAt a Glanceâ| Metadata | Details |
|---|---|
| Publication Date | 2017-04-07 |
| Journal | Chemical Engineering Journal |
| Authors | Beatriz GĂłmez-Ruiz, Sonia GĂłmez-LavĂn, Nazely Diban, Virginie Boiteux, Adeline Colin |
| Institutions | Agence Nationale de SĂ©curitĂ© Sanitaire de lâAlimentation, de lâEnvironnement et du Travail, Universidad de Cantabria |
| Citations | 157 |
| Analysis | Full AI Review Included |
Technical Documentation & Analysis: High-Efficiency PFAS Degradation via BDD Electro-oxidation
Section titled âTechnical Documentation & Analysis: High-Efficiency PFAS Degradation via BDD Electro-oxidationâThis document analyzes the research paper, âEfficient electrochemical degradation of poly- and perfluoroalkyl substances (PFASs) from the effluents of an industrial wastewater treatment plant,â focusing on the application of Boron Doped Diamond (BDD) electrodes for advanced oxidation processes (AOPs).
Executive Summary
Section titled âExecutive SummaryâThis study validates the critical role of Boron Doped Diamond (BDD) anodes in achieving near-complete mineralization of highly persistent pollutants in real-world industrial effluent.
- Exceptional Removal Efficiency: A commercial BDD anode achieved 99.74% removal of total PFASs (Per- and polyfluoroalkyl substances), reducing concentrations from 1652 ”g/L to 4.22 ”g/L in industrial wastewater effluent.
- High Mineralization: The BDD electro-oxidation process resulted in a high Total Organic Carbon (TOC) removal rate of 91.1% ± 0.31%, confirming effective mineralization into CO2 and fluoride ions (F-).
- Robust Material Performance: The Si/BDD anodic material demonstrated exceptional stability, having been in operation for over 10 years and maintaining degradation efficiency after more than 4000 hours of discontinuous use.
- Mechanism Validation: Degradation was primarily driven by the BDDâs capacity to generate highly reactive hydroxyl radicals (HO·), effectively breaking down complex fluorotelomers (6:2 FTAB, 6:2 FTSA) into shorter-chain PFCAs and ultimately mineralizing them.
- Kinetic Control: Operating at a high current density (50 mA/cm2) shifted the reaction kinetics to mass transport control, accelerating the degradation rate necessary for complete PFAS elimination.
Technical Specifications
Section titled âTechnical SpecificationsâThe following hard data points were extracted from the electrochemical treatment of the industrial wastewater effluent (E sample).
| Parameter | Value | Unit | Context |
|---|---|---|---|
| Initial Total PFASs Concentration (ΣPFASs) | 1652 | ”g/L | WWTP Effluent (Feed Water) |
| Final Total PFASs Concentration | 4.22 | ”g/L | After 10 hours of treatment |
| PFASs Removal Efficiency | 99.74 | % | Achieved at 50 mA/cm2 |
| Total Organic Carbon (TOC) Removal | 91.1 ± 0.31 | % | Confirms mineralization |
| Anode Surface Area | 70 (0.0070) | cm2 (m2) | BDD electrode size |
| Applied Current Density (j) | 50 | mA/cm2 | Primary operating condition |
| Cell Voltage Range | 13.9 - 15.3 | V | Measured at 50 mA/cm2 |
| Treatment Time for 99.74% Removal | 10 | hours | Total experiment duration |
| Energy Consumption (99.74% Removal) | 256 | kWh/m3 | High energy demand noted for complete removal |
| Defluorination Factor (DF-) | 126 | % | Indicates degradation of unidentified precursors |
| Anode Operational Stability | >4000 | hours | Proven robustness of Si/BDD material |
Key Methodologies
Section titled âKey MethodologiesâThe electrochemical degradation was performed using a laboratory-scale flow-by cell under galvanostatic control.
- Anode Material Selection: Boron Doped Diamond (BDD) was selected due to its high stability, low adsorption capacity, and high overpotential for oxygen generation, maximizing hydroxyl radical (HO·) production.
- Cell Configuration: An undivided flow-by cell (Diacell 106) was utilized, consisting of two circular parallel electrodes (BDD anode and stainless steel cathode).
- Electrode Geometry: The BDD anode had a surface area of 70 cm2, with an electrode gap maintained at 5 mm.
- Operating Conditions: Experiments were performed under galvanostatic control, primarily at a high current density of 50 mA/cm2 to ensure mass transport control kinetics.
- Feed Circulation: 2 L of effluent sample was circulated from a jacketed glass tank (maintained at 20 °C) to the electro-oxidation cell at a flowrate of 3 L/min.
- Kinetic Analysis: Lower current densities (2, 5, 10 mA/cm2) were tested, showing a shift from zero-order kinetics (current control) at low current to first-order kinetics (mass transport control) at 50 mA/cm2.
- Analytical Confirmation: PFAS degradation and mineralization were confirmed by high TOC removal, progressive fluoride ion (F-) release, and UHPLC-MS/MS analysis of 29 targeted PFAS compounds.
6CCVD Solutions & Capabilities
Section titled â6CCVD Solutions & Capabilitiesâ6CCVD is uniquely positioned to supply the advanced BDD materials required to replicate, scale, and optimize this high-efficiency electrochemical PFAS degradation technology. Our expertise in MPCVD diamond synthesis ensures the delivery of robust, high-performance anodes for demanding industrial applications.
Applicable Materials for Electrochemical AOPs
Section titled âApplicable Materials for Electrochemical AOPsâTo replicate or extend this research, 6CCVD recommends the following materials:
- Heavy Boron Doped Diamond (BDD) Anodes: Essential for high mineralization efficiency. Our BDD material is optimized for high overpotential and maximum hydroxyl radical generation, directly matching the performance requirements demonstrated in this study (99.74% PFAS removal).
- Polycrystalline Diamond (PCD) Substrates: We offer robust PCD substrates up to 10 mm thick, providing the mechanical stability necessary for long-term industrial reactor operation, exceeding the 4000+ hours of stability reported.
Customization Potential
Section titled âCustomization PotentialâThe success of BDD electro-oxidation relies on precise electrode geometry and reliable electrical contact. 6CCVD offers comprehensive customization services to meet specific reactor designs:
| Research Requirement | 6CCVD Customization Capability | Engineering Advantage |
|---|---|---|
| Specific Anode Dimensions (e.g., 70 cm2 circular) | Custom Dimensions & Laser Cutting: Plates/wafers available up to 125mm. We provide precise laser cutting to match circular, rectangular, or complex flow-cell geometries. | Ensures exact fit and optimal surface area utilization for flow-by or batch reactors, facilitating direct scale-up. |
| BDD Film Thickness | SCD/PCD Thickness Control: SCD and PCD films available from 0.1 ”m up to 500 ”m. | Allows researchers to optimize BDD layer thickness for conductivity, cost efficiency, and long-term stability under high current densities (50 mA/cm2). |
| Electrical Contact & Integration | Internal Metalization Services: We apply custom metal layers (Au, Pt, Pd, Ti, W, Cu) directly to the BDD surface. | Guarantees low-resistance electrical contacts, crucial for minimizing voltage drop and controlling energy consumption (256 kWh/m3) during high-current operation. |
Engineering Support
Section titled âEngineering Supportâ6CCVDâs in-house PhD team specializes in the material science of diamond electrodes for electrochemical applications. We can assist with material selection and optimization for similar PFAS Remediation and Industrial Wastewater Treatment projects, focusing on:
- Optimizing boron doping levels for specific current density regimes.
- Designing electrode geometries for improved mass transport kinetics.
- Selecting appropriate substrate materials (Si, Ta, etc.) for maximum thermal and chemical robustness.
For custom specifications or material consultation, visit 6ccvd.com or contact our engineering team directly.
Tech Support
Section titled âTech SupportâOriginal Source
Section titled âOriginal SourceâReferences
Section titled âReferencesâ- 2009 - Monitoring of perfluorinated compounds in edible fish from the Mediterranean Sea [Crossref]
- 2005 - Synthesis of environmentally relevant fluorinated surfactants - A review [Crossref]
- 2006 - Sources, fate and transport of perfluorocarboxylates [Crossref]
- 2013 - Perfluorinated sulfonate and carboxylate compounds in eggs of seabirds breeding in the Canadian Arctic: temporal trends (1975-2011) and interspecies comparison [Crossref]
- 2009 - Perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) in sewage treatment plants [Crossref]
- 2014 - Treatment of poly- and perfluoroalkyl substances in U.S. full-scale water treatment systems [Crossref]