Feasibility of Micropollutants Treatment by Coupling Nanofiltration and Electrochemical Oxidation - Case of Hospital Wastewater
At a Glance
Section titled âAt a Glanceâ| Metadata | Details |
|---|---|
| Publication Date | 2015-04-17 |
| Journal | International Journal of Chemical Reactor Engineering |
| Authors | Yandi Lan, Clémence Coetsier, Christel Causserand, Karine Groenen Serrano |
| Institutions | Laboratoire de Génie Chimique |
| Citations | 15 |
| Analysis | Full AI Review Included |
Technical Documentation & Brief: MPCVD Diamond for Advanced Water Treatment
Section titled âTechnical Documentation & Brief: MPCVD Diamond for Advanced Water Treatmentâ6CCVD Ref: DOC-EO-HWW-03519067 Application: Electrochemical Oxidation (EO) of Refractory Micropollutants Source Paper: Feasibility of Micropollutants Treatment by Coupling Nanofiltration and Electrochemical Oxidation: Case of Hospital Wastewater
Executive Summary
Section titled âExecutive SummaryâThis research validates the use of coupled Nanofiltration (NF) and highly efficient Electrochemical Oxidation (EO) utilizing Boron-Doped Diamond (BDD) anodes for the tertiary treatment of hospital wastewater, specifically targeting the pharmaceutical pollutant Ciprofloxacin (CIP).
- Material Validation: Confirmed that MPCVD Boron-Doped Diamond (BDD) anodes provide the superior electrochemical activity necessary for high-efficiency mineralization of refractory organic compounds.
- High Removal Efficiency: Achieved complete (100%) Chemical Oxygen Demand (COD) removal and 97% Total Organic Carbon (TOC) removal in the NF retentate within 300 minutes of electrolysis.
- Target Pollutant Destruction: Ciprofloxacin (CIP) was completely eliminated in the retentate within 150 minutes, demonstrating the powerful non-selective oxidation capability of BDD-generated hydroxyl radicals (OHâą).
- Process Optimization: The NF preconcentration step successfully reduced the required treatment volume (VRF=5), mitigating mass transfer limitations inherent in dilute solutions and making the subsequent EO process economically viable.
- Energy Metrics: The total COD removal was achieved with a competitive Specific Energy Consumption (SEC) of 50 kW h kg-1 COD.
- Final Effluent Quality: The global final effluent (NF permeate and EO final tank) contained less than 5 mg L-1 of organics, meeting stringent discharge limits.
Technical Specifications
Section titled âTechnical SpecificationsâThe following table extracts critical operating parameters and performance metrics from the electrochemical oxidation (EO) phase of the study, highlighting the requirements for high-performance BDD anodes.
| Parameter | Value | Unit | Context |
|---|---|---|---|
| Anode Material Used | Boron-Doped Diamond (BDD) | - | Elaborated by CVD on Silicon (Si) substrate |
| Reactor Type | Single-compartment flow filterpress | - | Galvanostatic operating conditions |
| Anode Active Surface Area | 63 | cm2 | Two circular disc electrodes used |
| Electrode Separation | 10 | mm | Spacing within the electrochemical cell (3) |
| Electrolysis Temperature | 30 | °C | Controlled using a thermoregulated reservoir |
| Applied Current Density (MBR Effluent) | 7.9 | mA cm-2 | Operates above the limiting current density |
| Electrolyte Composition | 0.1 M K2SO4 | - | Used for conductivity enhancement |
| COD Final Concentration | 0 | mg L-1 | Achieved after 300 min electrolysis |
| TOC Final Concentration | 1.9 | mg L-1 | Achieved after 300 min electrolysis (Initial 62 mg L-1) |
| Specific Energy Consumption (SEC) | 50 | kW h kg-1 COD | Metric for total COD removal |
Key Methodologies
Section titled âKey MethodologiesâThe Electrochemical Oxidation (EO) stage was critically dependent on specific reactor design and operational parameters to maximize the generation of hydroxyl radicals (OHâą) and ensure complete mineralization.
- Feed Preparation: Nanofiltration (NF) retentate (Volume Reduction Factor, VRF = 5) was collected, resulting in a concentrated stream of micropollutants.
- Electrolyte Conditioning: The pH of the retentate was adjusted to 3.0, and 0.1 M K2SO4 was added as the supporting electrolyte to increase conductivity.
- Electrode Fabrication: The BDD anode was fabricated via Chemical Vapor Deposition (CVD) onto a conductive silicon substrate.
- Reactor Setup: A discontinuous, single-compartment flow filterpress reactor was utilized, employing two BDD disc electrodes (63 cm2 each) separated by 10 mm.
- Galvanostatic Control: Electrolyses were conducted under galvanostatic conditions (constant current density), specifically 7.9 mA cm-2 for the MBR effluent matrix.
- Oxidation Mechanism: The high applied current density ensured the kinetic regime was mass-transfer limited, maximizing the non-selective oxidation mediated by physisorbed hydroxyl radicals generated at the BDD surface.
6CCVD Solutions & Capabilities
Section titled â6CCVD Solutions & Capabilitiesâ6CCVD is an expert provider of MPCVD diamond, specializing in the custom materials required to replicate, scale, and advance high-performance electrochemical oxidation systems like the one described. Our integrated material science and engineering support ensures seamless integration of BDD into industrial or research reactors.
Applicable Materials
Section titled âApplicable MaterialsâTo replicate the high removal efficiencies demonstrated in this study, the primary material requirement is a robust, high-performance anode capable of maximizing the production of non-selective oxidants.
| Material Grade | Description | Connection to Research Requirements |
|---|---|---|
| Heavy Boron-Doped Diamond (BDD) | Polycrystalline (PCD) or Single Crystal (SCD) diamond heavily doped for conductivity and electrochemical stability. | Essential for generating high concentrations of hydroxyl radicals (OHâą) required for 100% COD mineralization and low SEC. |
| BDD on Conductive Substrates | BDD films grown directly on conductive Silicon (Si) or Tantalum (Ta) supports. | Directly meets the studyâs requirement for BDD deposited on a conductive silicium substrate for optimal electrode function. |
| High Purity Single Crystal Diamond (SCD) | SCD (Grade IIa or Optical) plates (0.1 ”m to 500 ”m thick). | While BDD is the primary electrode material, high purity SCD can be utilized for advanced sensor applications or specific optical monitoring elements within the reactor environment. |
Customization Potential
Section titled âCustomization PotentialâThe experimental setup relied on specific electrode dimensions (63 cm2 discs) and configurations. 6CCVDâs advanced MPCVD capabilities are perfectly suited to supply materials for scaling this technology.
| Requirement | 6CCVD Capability | Direct Relevance |
|---|---|---|
| Custom Electrode Dimensions | Production of plates and wafers up to 125 mm (PCD/BDD). | Allows immediate scale-up from the 63 cm2 lab discs to larger circular or rectangular flow-cell geometries. |
| Thickness Control | BDD layers available from 0.1 ”m to 500 ”m on insulating or conductive substrates. | Enables optimization of BDD film thickness for longevity, mechanical strength, and electrical resistance requirements of the reactor. |
| Substrate Integration | In-house laser cutting and machining services for complex geometries. | Provides custom BDD electrode shapes ready for integration into proprietary filterpress or plate-and-frame reactor designs. |
| Advanced Metalization | Standard and custom metalization (Au, Pt, Pd, Ti, W, Cu) for contact layers. | Necessary for creating durable, low-resistance electrical connections required for high-current galvanostatic operation. |
Engineering Support
Section titled âEngineering SupportâOur team of in-house PhD material scientists specializes in the electrochemistry of diamond and advanced water treatment applications.
- Application Expertise: We offer consultation on optimizing BDD doping levels and surface termination to maximize hydroxyl radical generation rates for similar Electrochemical Water Treatment projects.
- Scale-Up Guidance: Our experts provide technical guidance on selecting the optimal BDD substrate (e.g., Si vs. Ta) and dimensions for moving from lab-scale (1 L reservoir used in the paper) to pilot-scale reactors, focusing on minimizing SEC.
- Electrochemical Design: We assist in material selection to ensure chemical compatibility with various aggressive media (high acidity, sulfate, chloride, etc.) encountered during industrial EO processes.
For custom specifications or material consultation, visit 6ccvd.com or contact our engineering team directly.
View Original Abstract
Abstract In spite of good performances of the membrane bioreactor (MBR) process, permeate from it can still contain refractory pollutants that have to be removed before water reuse or discharge. The present study is an attempt to combine the advantages of two well-known technologies, which are nanofiltration (NF) and electrochemical oxidation (EO) to treat MBR effluent from hospital wastewater. The concept is based on a preconcentration of micropollutants with a reduction of the wastewater volume by NF and treatment of the NF retentate by oxidation. During filtration process the rejection of ciprofloxacin, as a target molecule, reached beyond 97%. Then the NF retentate was treated by EO using a boron-doped diamond anode (BDD). Galvanostatic electrolyses showed that this anode is efficient to mineralize not only ciprofloxacin but also all the micropollutants and organics contained in MBR effluent. The results demonstrated that rapid mineralization occurred: the removal of total organic carbon and chemical oxygen demand (COD) reached 97% and 100%, respectively, in our conditions in 300 min maximum. The speciïŹc energy consumption for the total removal of COD was calculated to be 50 kW h kg Ë1 COD.
Tech Support
Section titled âTech SupportâOriginal Source
Section titled âOriginal SourceâReferences
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