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Electrodeposition of Calcium Carbonate and Magnesium Carbonate from Hard Water on Stainless-Steel Electrode to Prevent Natural Scaling Phenomenon

MetadataDetails
Publication Date2021-10-05
JournalWater
AuthorsFaléstine Souiad, Yasmina Bendaoud-Boulahlib, Ana Sofia Rodrigues, Annabel Fernandes, Lurdes Ciríaco
InstitutionsUniversity of Beira Interior, Université Constantine 2
Citations11
AnalysisFull AI Review Included

Technical Documentation & Analysis: MPCVD Diamond for Electrochemical Scaling Prevention

Section titled “Technical Documentation & Analysis: MPCVD Diamond for Electrochemical Scaling Prevention”

This document analyzes the research paper “Electrodeposition of Calcium Carbonate and Magnesium Carbonate from Hard Water on Stainless-Steel Electrode to Prevent Natural Scaling Phenomenon” and outlines how 6CCVD’s advanced MPCVD diamond materials can support and extend this critical electrochemical water treatment technology.


This research successfully demonstrated the use of controlled electrodeposition on a stainless-steel cathode to remove $\text{Ca}^{2+}$ and $\text{Mg}^{2+}$ ions, effectively preventing hard water scaling.

  • BDD Superiority: Boron-Doped Diamond (BDD) anodes (commercial $\text{Si}/\text{BDD}$) were benchmarked against $\text{Ti}/\text{Pt}/\text{PbO}_2$ and proved superior in stability, exhibiting a lower current reduction (less blocking effect) during accelerated scaling tests.
  • Optimal Parameters: The best overall performance for Inorganic Carbon (IC), $\text{Ca}^{2+}$, and $\text{Mg}^{2+}$ removal was achieved at an anodic current intensity of 0.1 A, corresponding to a current density of $100 \text{ A } \text{m}^{-2}$.
  • Scale-Up Validation: The process showed excellent reproducibility, maintaining consistent IC removal rates over eight consecutive assays without requiring cleaning of the solid deposit formed on the cathode.
  • Material Influence: Increased cathode area (20 $\text{cm}^{2}$) and higher stirring speed (1000 rpm) significantly favored ion removal rates by enhancing mass transfer.
  • Energy Efficiency: Specific Energy Consumption (SEC) for IC removal using the BDD anode at 0.1 A was measured at $114 \text{ kWh } \text{kg}^{-1}$ (Table 3).
  • Composition Effect: Carbonate removal efficiency increased significantly when the $\text{Ca}/\text{Mg}$ molar ratio was greater than 1, due to the lower solubility product of calcium carbonate.

The following hard data points were extracted from the experimental results, focusing on the optimal BDD anode performance.

ParameterValueUnitContext
Optimal Anodic Current Intensity (I)0.1ABest results for $\text{Mg}^{2+}$ removal and scaling inhibition.
Optimal Current Density100$\text{A } \text{m}^{-2}$Calculated based on 0.1 A applied to 10 $\text{cm}^{2}$ cathode.
Anode Material Tested$\text{Si}/\text{BDD}$N/ACommercial Boron-Doped Diamond (20 $\text{cm}^{2}$ area).
Cathode Material TestedStainless Steel (SS)N/ASubmerged areas of 10 $\text{cm}^{2}$ and 20 $\text{cm}^{2}$.
Initial pH (Solution S)7.9 $\pm$ 0.2N/ASimulated hard water solution.
Final pH (BDD, 0.1 A)6.8N/AAfter 4 h electrolysis.
IC Removal (BDD, 0.1 A)$\approx 80$%Highest removal rate observed (Figure 3a).
$\text{Ca}^{2+}$ Removal (BDD, 0.1 A)$\approx 60$%Highest removal rate observed (Figure 3a).
Specific Energy Consumption (IC, BDD, 0.1 A)114$\text{kWh } \text{kg}^{-1}$SEC per mass of IC removed (Table 3).
Accelerated Scaling Test Potential (E)-0.96V vs. Ag/AgClChronoamperometric test condition.
Optimal Stirring Speed1000rpmMaximized mass transfer and removal rates.

The electrochemical experiments (EE) utilized a galvanostatic approach to control the electrodeposition process.

  1. Cell Setup: Undivided cylindrical glass cells (200 mL or 500 mL volume) were used in batch mode at room temperature.
  2. Anode Selection: Two anode materials were tested: a commercial $\text{Si}/\text{BDD}$ electrode (20 $\text{cm}^{2}$ immersed area) and a lab-prepared $\text{Ti}/\text{Pt}/\text{PbO}_2$ electrode (10 $\text{cm}^{2}$ area).
  3. Cathode Selection: Stainless Steel (SS) plates were used as cathodes, with submerged areas of 10 $\text{cm}^{2}$ or 20 $\text{cm}^{2}$.
  4. Power Application: A Direct Current (DC) power supply was used to apply constant anodic current intensities ranging from 0.025 A to 0.5 A.
  5. Hydrodynamics: Continuous stirring was applied at 300, 500, or 1000 rpm to control mass transport of reactants.
  6. Duration: Assays were performed for 4 h or 8 h, with samples collected hourly or bi-hourly for analysis.
  7. Scaling Test: Accelerated scaling tests were performed using chronoamperometry at a fixed potential (-0.96 V vs. Ag/AgCl) to evaluate the scaling inhibition properties of the treated water.
  8. Deposit Characterization: Solid deposits on the cathode were analyzed using X-ray Diffractometry (XRD), Energy Dispersive Spectroscopy (EDS), and Scanning Electron Microscopy (SEM).

The successful application of BDD anodes in this study highlights the material’s superior stability and electrochemical performance for water treatment applications, specifically in scale prevention. 6CCVD is uniquely positioned to supply the high-quality BDD required to replicate, optimize, and scale this research.

To replicate the high performance and stability demonstrated by the BDD anode, 6CCVD recommends:

Application Requirement6CCVD Material SolutionTechnical Advantage
Anode MaterialHeavy Boron-Doped Diamond (BDD)High conductivity, wide electrochemical window, superior stability against fouling compared to $\text{Ti}/\text{Pt}/\text{PbO}_2$. Ideal for long-term galvanostatic operation.
Electrode SubstrateBDD on Silicon (Si) or Niobium (Nb)Provides robust mechanical support and excellent electrical contact, matching the $\text{Si}/\text{BDD}$ used in the study.
Cathode SubstratesPolycrystalline Diamond (PCD)While SS was used, PCD offers superior corrosion resistance and thermal management for advanced cathode designs, available up to 125mm wafers.

The research utilized specific electrode geometries (10 $\text{cm}^{2}$ and 20 $\text{cm}^{2}$) and benchmarked against a $\text{Ti}/\text{Pt}/\text{PbO}_2$ anode. 6CCVD’s in-house capabilities allow researchers and engineers to move beyond standard geometries and materials:

  • Custom Dimensions: 6CCVD supplies BDD and PCD plates/wafers in custom dimensions, significantly exceeding the 20 $\text{cm}^{2}$ area used in the study, enabling direct scale-up to pilot or industrial systems (up to 125mm diameter).
  • Thickness Control: We offer precise control over BDD film thickness (0.1 ”m to 500 ”m), allowing optimization of conductivity and cost for specific current density requirements.
  • Advanced Metalization: The study utilized $\text{Ti}/\text{Pt}$ layers in the benchmark anode. 6CCVD offers internal metalization services (Au, Pt, Pd, Ti, W, Cu) for creating robust, low-resistance electrical contacts on BDD electrodes, crucial for high-current density applications.
  • Polishing: For applications requiring ultra-smooth surfaces (e.g., flow cells or micro-electrodes), 6CCVD provides polishing services achieving $\text{Ra} < 1 \text{ nm}$ for SCD and $\text{Ra} < 5 \text{ nm}$ for inch-size PCD.

6CCVD’s in-house PhD team specializes in diamond material science and electrochemical engineering. We offer comprehensive support for projects focused on Electrochemical Water Softening and Scale Prevention. Our expertise ensures optimal material selection, substrate choice, and electrode design to maximize efficiency and longevity in demanding applications.

For custom specifications or material consultation, visit 6ccvd.com or contact our engineering team directly.

View Original Abstract

This study focuses on preventing scale formation in hard waters by controlled electrode-position of Ca2+ and Mg2+ on a stainless-steel cathode at constant applied current intensity. The influence of the anode material, BDD or Ti/Pt/PbO2, cathode active area, stirring speed, and applied anodic current intensity on the inorganic carbon (IC), Ca2+, and Mg2+ removal was investigated. Assays were performed with model hard water solutions, simulating Bounouara (Algeria) water. The scaling inhibiting properties of the treated water were followed by measuring IC, calcium, and magnesium concentrations and chronoamperometric characterization of the treated solutions. The influence of the Ca/Mg molar ratio on the inorganic carbon removal by electrolysis was also evaluated, utilizing model solutions with different compositions. It was found that an increase in stirring speed or cathode geometric area favors IC and Ca2+ and Mg2+ removal rates. The applied current intensity was varied from 0.025 to 0.5 A, and the best results were obtained for 0.1 A, either in IC and Ca2+ and Mg2+ removals or by the accelerated scaling tests. However, energy costs increase with applied current. The deposit formed over the cathode does not seem to influence posterior deposition rate, and after eight consecutive assays, the solid deposition rate was kept constant. Ca/Mg ratio influences IC removal rate that increases with it. The results showed that hard-water scaling phenomena can be prevented by solid electrodeposition on the cathode at applied constant current.

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