<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd">
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article">
 <front>
  <journal-meta>
   <journal-id journal-id-type="publisher-id">
    aces
   </journal-id>
   <journal-title-group>
    <journal-title>
     Advances in Chemical Engineering and Science
    </journal-title>
   </journal-title-group>
   <issn pub-type="epub">
    2160-0392
   </issn>
   <issn publication-format="print">
    2160-0406
   </issn>
   <publisher>
    <publisher-name>
     Scientific Research Publishing
    </publisher-name>
   </publisher>
  </journal-meta>
  <article-meta>
   <article-id pub-id-type="doi">
    10.4236/aces.2024.144011
   </article-id>
   <article-id pub-id-type="publisher-id">
    aces-135729
   </article-id>
   <article-categories>
    <subj-group subj-group-type="heading">
     <subject>
      Articles
     </subject>
    </subj-group>
    <subj-group subj-group-type="Discipline-v2">
     <subject>
      Chemistry 
     </subject>
     <subject>
       Materials Science
     </subject>
    </subj-group>
   </article-categories>
   <title-group>
    Detection of Oxidants Such as Hydroxyl Radicals and Chlorine Electrogenerated on a BDD Electrode by Simple Methods
   </title-group>
   <contrib-group>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Konan Sylvestre
      </surname>
      <given-names>
       Koffi
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Konan Martin
      </surname>
      <given-names>
       Koffi
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff2"> 
      <sup>2</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Foffié Thiery Auguste
      </surname>
      <given-names>
       Appia
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Sahi Placide
      </surname>
      <given-names>
       Sadia
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff2"> 
      <sup>2</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Kouakou Jocelin
      </surname>
      <given-names>
       Kimou
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Souleymane
      </surname>
      <given-names>
       Kone
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Lassiné
      </surname>
      <given-names>
       Ouattara
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
   </contrib-group> 
   <aff id="aff1">
    <addr-line>
     aLaboratoire de Constitution et de Réaction de la Matière, UFR SSMT, Université Félix Houphouët Boiguy, Abidjan, Côte d’Ivoire
    </addr-line> 
   </aff> 
   <aff id="aff2">
    <addr-line>
     aUFR Environnement, Université Jean Lorougnon Guédé, Daloa, Côte d’Ivoire
    </addr-line> 
   </aff> 
   <pub-date pub-type="epub">
    <day>
     02
    </day> 
    <month>
     09
    </month>
    <year>
     2024
    </year>
   </pub-date> 
   <volume>
    14
   </volume> 
   <issue>
    04
   </issue>
   <fpage>
    173
   </fpage>
   <lpage>
    187
   </lpage>
   <history>
    <date date-type="received">
     <day>
      27,
     </day>
     <month>
      June
     </month>
     <year>
      2024
     </year>
    </date>
    <date date-type="published">
     <day>
      30,
     </day>
     <month>
      June
     </month>
     <year>
      2024
     </year> 
    </date> 
    <date date-type="accepted">
     <day>
      30,
     </day>
     <month>
      August
     </month>
     <year>
      2024
     </year> 
    </date>
   </history>
   <permissions>
    <copyright-statement>
     © Copyright 2014 by authors and Scientific Research Publishing Inc. 
    </copyright-statement>
    <copyright-year>
     2014
    </copyright-year>
    <license>
     <license-p>
      This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/
     </license-p>
    </license>
   </permissions>
   <abstract>
    The aim of this work is to detect electrogenerated hydroxyl radicals and chlorine by simple and less expensive methods. Preparative electrolyses of perchloric acid (HClO
    <sub>4</sub>) and sodium chloride (NaCl) were performed on a boron-doped diamond (BDD) electrode. The hydroxyl radicals were quantified indirectly by assaying the samples from the HClO
    <sub>4</sub> (0.1 M) electrolysis with a 10
    <sup>−4</sup> M potassium permanganate solution. The investigations showed that the amount of hydroxyl radicals depends on the concentration of HClO
    <sub>4</sub> and the current density. As for chlorine, a qualitative determination was carried out. A mixture of the electrolyte solution of HClO
    <sub>4</sub> (0.1 M) + NaI (0.2 M) + 2 mL of hexane, taken in this order, leads to a purplish-pink coloration attesting to the presence of Cl
    <sub>2</sub>. The same test was carried out with NaBr and NaI giving pale and very pale pink colourations, respectively, showing that the intensity of the colouration depends on the strength of the oxidant present. In addition, oxidants were detected during the electrooxidation of metronidazole (MNZ). The results showed the participation of electrogenerated hydroxyl radicals. The generation of chlorine has also been proven. Furthermore, the degradation leads to a chemical oxygen demand (COD) removal rate of 83.48% and the process is diffusion-controlled.
   </abstract>
   <kwd-group> 
    <kwd>
     Electrooxidation
    </kwd> 
    <kwd>
      Hydroxyl Radicals
    </kwd> 
    <kwd>
      Chlorine
    </kwd> 
    <kwd>
      Detection
    </kwd>
   </kwd-group>
  </article-meta>
 </front>
 <body>
  <sec id="s1">
   <title>1. Introduction</title>
   <p>Like most countries in the world, Côte d’Ivoire is faced with a real problem of wastewater before it is discharged. Wastewater of various types, including from hospitals, is discharged as such into the environment <xref ref-type="bibr" rid="scirp.135729-1">
     [1]
    </xref> <xref ref-type="bibr" rid="scirp.135729-2">
     [2]
    </xref>. Wastewater from hospitals can contain heavy metals (mercury, silver, chromium, nickel, cobalt, etc.) and organic molecules, some of which, such as antibiotics, are difficult to biodegrade <xref ref-type="bibr" rid="scirp.135729-3">
     [3]
    </xref>-<xref ref-type="bibr" rid="scirp.135729-5">
     [5]
    </xref>. This constitutes a danger to the environment and humans <xref ref-type="bibr" rid="scirp.135729-6">
     [6]
    </xref> <xref ref-type="bibr" rid="scirp.135729-7">
     [7]
    </xref>.</p>
   <p>To treat wastewater containing compounds that are difficult to biodegrade, several processes are used. Among these treatment processes, there are the electrochemical advanced oxidation processes. Indeed, advanced oxidation processes are based on the in-situ generation of very powerful oxidising agents: hydroxyl radicals. These oxidative species are non-selective and capable of degrading very complex aromatic compounds and non-biodegradable pollutants. Its generation and reactivity for the degradation of persistent pollutants depend essentially on the type of electrode used at the anode. Indeed, for so-called “active” electrodes, the bonds between the electrode surface and the hydroxyl radicals are very strong. Hydroxyl radicals are chemisorbed on the surface of this type of electrode. As a result, they do not participate effectively in the degradation of organic compounds. On the other hand, for non-active anodes, hydroxyl radicals are physisorbed on the surface of the anode, and are therefore very labile. With this type of electrode, hydroxyl radicals are available and participate significantly in the degradation of pollutants of all kinds. Previous work in our laboratory has shown that the degradation of organic pollutants on a BDD electrode led to its mineralisation, while a conversion of the parent compound was achieved on DSA electrodes <xref ref-type="bibr" rid="scirp.135729-8">
     [8]
    </xref>-<xref ref-type="bibr" rid="scirp.135729-12">
     [12]
    </xref>.</p>
   <p>Hydroxyl radicals are very reactive with organic compounds and have a very short lifetime in the nanosecond range <xref ref-type="bibr" rid="scirp.135729-13">
     [13]
    </xref> <xref ref-type="bibr" rid="scirp.135729-14">
     [14]
    </xref>. This makes their detection very difficult. In addition, due to their high reactivity, they can easily destroy or disrupt the sensing elements of detection devices, preventing them from generating and transducing trustworthy signals <xref ref-type="bibr" rid="scirp.135729-15">
     [15]
    </xref> <xref ref-type="bibr" rid="scirp.135729-16">
     [16]
    </xref>. In recent years, several techniques have been used for the detection of hydroxyl radicals. These include electron spin resonance spectroscopy <xref ref-type="bibr" rid="scirp.135729-17">
     [17]
    </xref> <xref ref-type="bibr" rid="scirp.135729-18">
     [18]
    </xref>, electrochemical sensors <xref ref-type="bibr" rid="scirp.135729-19">
     [19]
    </xref>, fluorescent detectors <xref ref-type="bibr" rid="scirp.135729-20">
     [20]
    </xref> <xref ref-type="bibr" rid="scirp.135729-21">
     [21]
    </xref> and hydroxylation of aromatic compounds <xref ref-type="bibr" rid="scirp.135729-22">
     [22]
    </xref>. All these methods are very accurate but have some inherent disadvantages such as cost and complexity.</p>
   <p>The environment contains many ions including chloride ions. The effect of chloride ions on the efficiency of electrooxidation of organic compounds has been extensively studied in our previous work <xref ref-type="bibr" rid="scirp.135729-8">
     [8]
    </xref>-<xref ref-type="bibr" rid="scirp.135729-11">
     [11]
    </xref>. The results obtained showed that the presence of chloride ions had a significant positive impact on the degradation of organic compounds. This is the case for the degradation of amoxicillin on RuO<sub>2</sub>, IrO<sub>2</sub> and Pt-RuO<sub>2</sub>-IrO<sub>2</sub> electrodes. The rate of chemical oxygen demand abatement (∆(COD)) determined after 10 hours of electrolysis for each of the DSA electrodes mentioned is 4.53% (RuO<sub>2</sub>), 2.47% (IrO<sub>2</sub>) and 0.83% (Pt-RuO<sub>2</sub>-IrO<sub>2</sub>) in the absence of NaCl and 40.71%, 71.65% and 73.79% in the presence of NaCl on RuO<sub>2</sub>, IrO<sub>2</sub> and Pt-RuO<sub>2</sub>-IrO<sub>2</sub> respectively <xref ref-type="bibr" rid="scirp.135729-8">
     [8]
    </xref> <xref ref-type="bibr" rid="scirp.135729-9">
     [9]
    </xref> <xref ref-type="bibr" rid="scirp.135729-11">
     [11]
    </xref>. These different results show that chloride ions are powerful oxidising agents. In solution, chloride ions can take various forms depending on the pH of the medium. We can have Cl<sub>2</sub> (Ph &lt; 3), Cl<sub>2</sub> (pH &lt; 3), HClO (3 &lt; pH &lt; 8) and ClO<sup>−</sup> (pH &gt; 8) according to Equations (1) to (3) <xref ref-type="bibr" rid="scirp.135729-23">
     [23]
    </xref>:</p>
   <p>
    <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
      <mn>
        2 
      </mn> 
      <msup> 
       <mrow> 
        <mtext>
          Cl 
        </mtext> 
       </mrow> 
       <mo>
         − 
       </mo> 
      </msup> 
      <mo>
        → 
      </mo> 
      <msub> 
       <mrow> 
        <mtext>
          Cl 
        </mtext> 
       </mrow> 
       <mn>
         2 
       </mn> 
      </msub> 
      <mo>
        + 
      </mo> 
      <mn>
        2 
      </mn> 
      <msup> 
       <mtext>
         e 
       </mtext> 
       <mo>
         − 
       </mo> 
      </msup> 
     </mrow> 
    </math> (1)</p>
   <p>
    <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
      <msub> 
       <mrow> 
        <mtext>
          Cl 
        </mtext> 
       </mrow> 
       <mn>
         2 
       </mn> 
      </msub> 
      <mo>
        + 
      </mo> 
      <msub> 
       <mtext>
         H 
       </mtext> 
       <mn>
         2 
       </mn> 
      </msub> 
      <mtext>
        O 
      </mtext> 
      <mo>
        → 
      </mo> 
      <mtext>
        HClO 
      </mtext> 
      <mo>
        + 
      </mo> 
      <msup> 
       <mrow> 
        <mtext>
          Cl 
        </mtext> 
       </mrow> 
       <mo>
         − 
       </mo> 
      </msup> 
      <mo>
        + 
      </mo> 
      <msup> 
       <mtext>
         H 
       </mtext> 
       <mo>
         + 
       </mo> 
      </msup> 
     </mrow> 
    </math> (2)</p>
   <p>
    <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
      <mtext>
        HClO 
      </mtext> 
      <mo>
        ↔ 
      </mo> 
      <msup> 
       <mrow> 
        <mtext>
          ClO 
        </mtext> 
       </mrow> 
       <mo>
         − 
       </mo> 
      </msup> 
      <mo>
        + 
      </mo> 
      <msup> 
       <mtext>
         H 
       </mtext> 
       <mo>
         + 
       </mo> 
      </msup> 
     </mrow> 
    </math> (3)</p>
   <p>Techniques for the qualitative detection of oxidative chlorine species generally include iodometry, colorimetric, amperometric and electrochemical methods <xref ref-type="bibr" rid="scirp.135729-24">
     [24]
    </xref>-<xref ref-type="bibr" rid="scirp.135729-27">
     [27]
    </xref>. Generally, many detection methods have some disadvantages related to the use of many types of reagents that may produce higher toxicity, high detection limit, difficulty of operation, and cost of equipment.</p>
   <p>In this work, the aim is to determine hydroxyl radicals and chlorine by alternative, simple and less expensive methods. For this purpose, an indirect quantitative determination of hydroxyl radicals will be carried out by volumetric determination of hydrogen peroxide during the preparative electrolysis of perchloric acid. In addition, a qualitative determination will be carried out to detect chlorine during the preparative electrolysis of sodium chloride. Subsequently, the in-situ generation of hydroxide radicals and chlorine will be demonstrated during the electrolysis of metronidazole (MNZ) in perchloric acid. The qualitative test for the detection of the oxidants Br<sub>2</sub> and I<sub>2</sub> will also be performed during the electrolysis of NaBr and NaI, respectively.</p>
  </sec><sec id="s2">
   <title>2. Experimental Method</title>
   <sec id="s2_1">
    <title>2.1. Chemicals</title>
    <p>Perchloric acid (Panreac) and sodium chloride (Problabo) were used as supporting electrolyte and prepared with distilled water. Hydrogen peroxide 35% (Sharlau) was determined by potassium permanganate (Panreac) for the monitoring of hydroxyl radicals at Scharlau. Sodium iodide (99.5%) and hexane (95% - 97%) were manufactured by Sigma-Aldrich and Ensure respectively. Metronidazole, manufactured by Exphar SA of Belgium, was purchased from a pharmacy in Abidjan in tablet form. The pH was adjusted using H<sub>2</sub>SO<sub>4</sub> (Sigma-Aldrich) and NaOH (Panreac). The sodium bromide was manufactured by Panreac.</p>
   </sec>
   <sec id="s2_2">
    <title>2.2. Electrochemical System for Anodic Oxidation</title>
    <p>A volume of 250 mL under magnetic stirring and at laboratory temperature, covered with aluminum foil, was introduced into an electrochemical cell. Boron-doped diamond electrode was used at the anode and zirconium at the cathode. Both electrodes have a surface area of 16 cm<sup>2</sup>. Concentrations of 0.1 M HClO<sub>4</sub>, and NaCl were electrolysed individually for the in-situ determination of hydroxyl radicals and chlorine. Subsequently, preparative electrolysis of 0.1 M HClO<sub>4</sub> + 0.1 g/L metronidazole (MNZ) was performed for COD monitoring as well as oxidant detection. The experimental setup for the preparative electrolysis is shown in <xref ref-type="fig" rid="fig1">
      Figure 1
     </xref>.</p>
    <fig id="fig1" position="float">
     <label>Figure 1</label>
     <caption>
      <title>Figure 1. Experimental set-up for preparative electrolysis (A: peristaltic pump; B: magnetic stirrer; C: solution tank; D: beaker containing solution; E: solution recirculation pipe; F: electrochemical cell; G: generator; H: multiparameter).</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId20.jpeg?20240902034859" />
    </fig>
   </sec>
   <sec id="s2_3">
    <title>2.3. Quantitative and Qualitative Detection of Oxidants</title>
    <p>For the detection of hydroxyl radicals, several detection methods, both direct and indirect, can be used. In our work, an indirect and simple method for the detection of <sup>−</sup>OH was considered: the volumetric determination of hydrogen peroxide by potassium permanganate (KMnO<sub>4</sub>). For this purpose, 10 mL of the samples, taken at well-defined times, were dosed with 0.1 M KMnO<sub>4</sub> in the presence of 10 mL 0.1 M H<sub>2</sub>SO<sub>4</sub>. The turn is reached when the initially colourless solution turns pink. Furthermore, a calibration curve for H<sub>2</sub>O<sub>2</sub> concentrations ranging from 0 to 1 mM as a function of the volume of KMnO<sub>4</sub> poured in was established before the preparative electrolysis. The curve obtained is a straight line of equation [H<sub>2</sub>O<sub>2</sub>] = 0.0473V<sub>KMnO4</sub> − 0.0386, with a correlation coefficient R<sup>2</sup> of 0.9961 which is close to 1 attesting to the good linearity of the method.</p>
    <p>The aim of this work is also to determine the presence of chlorine during the electrolysis of a sodium chloride solution (0.1 M) in order to identify chlorine in an unknown medium. The experiment was carried out at an acidic pH because according to the probaix diagram for chlorine, chlorine exists in the following pH range [0, 4.5].</p>
    <p>The initial pH of the sodium chloride solution is 6.833. A 1 M sulphuric acid solution was used to adjust the pH to 2. The electrolysis of the sodium chloride solution is very suffocating due to the release of chlorine which is toxic. Thus, the detection of chlorine was done by taking a certain volume of NaCl samples to which 1 mL of NaI (0.2 M) and 2 to 5 mL of the hexane solution were added. After strong agitation of the mixture, the appearance of a pink coloration of the hexane proves the presence of active chlorine (Cl<sub>2</sub>). The same test was performed during the preparative electrolysis of NaI and NaBr.</p>
   </sec>
   <sec id="s2_4">
    <title>2.4. Monitoring of Degradation by Chemical Oxygen Demand (COD)</title>
    <p>The COD of the samples was determined in our experiments using HACH COD tubes. To determine it, 2 mL of sample is taken and put into a COD tube and heated in a digester (HACH) at 150˚C for 120 minutes. After cooling, the COD value is read directly with the DR/6000 spectrophotometer (HACH). The COD reduction rate is determined using this formula:</p>
    <p>
     <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
       <mi>
         Δ 
       </mi> 
       <mrow> 
        <mo>
          ( 
        </mo> 
        <mrow> 
         <mtext>
           COD 
         </mtext> 
        </mrow> 
        <mo>
          ) 
        </mo> 
       </mrow> 
       <mo>
         = 
       </mo> 
       <mrow> 
        <mo>
          ( 
        </mo> 
        <mrow> 
         <mrow> 
          <mrow> 
           <mrow> 
            <mo>
              ( 
            </mo> 
            <mrow> 
             <msub> 
              <mrow> 
               <mtext>
                 COD 
               </mtext> 
              </mrow> 
              <mn>
                0 
              </mn> 
             </msub> 
             <mo>
               − 
             </mo> 
             <msub> 
              <mrow> 
               <mtext>
                 COD 
               </mtext> 
              </mrow> 
              <mtext>
                t 
              </mtext> 
             </msub> 
            </mrow> 
            <mo>
              ) 
            </mo> 
           </mrow> 
          </mrow> 
          <mo>
            / 
          </mo> 
          <mrow> 
           <msub> 
            <mrow> 
             <mtext>
               COD 
             </mtext> 
            </mrow> 
            <mn>
              0 
            </mn> 
           </msub> 
          </mrow> 
         </mrow> 
        </mrow> 
        <mo>
          ) 
        </mo> 
       </mrow> 
       <mo>
         * 
       </mo> 
       <mn>
         100 
       </mn> 
      </mrow> 
     </math> (4)</p>
    <p>where COD<sub>0</sub> and COD<sub>t</sub> are respectively the COD at time 0 and t in mgO<sub>2</sub>/L.</p>
   </sec>
  </sec><sec id="s3">
   <title>3. Results and Discussion</title>
   <sec id="s3_1">
    <title>3.1. In-Situ Determination of Hydroxyl Radicals</title>
    <p>In order to demonstrate the in-situ production of hydroxyl radicals, the electrolysis of perchloric acid was carried out under constant stirring for 180 minutes at laboratory temperature (25˚C) and a density of 10 mA/cm<sup>2</sup>. 10 mL of HClO<sub>4</sub> samples taken at defined time intervals t were determined by 10<sup>−</sup><sup>4</sup> M KMnO<sub>4</sub> during the electrolysis. The concentration of H<sub>2</sub>O<sub>2</sub> at time t is determined from the relation:</p>
    <p>
     <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
       <msub> 
        <mtext>
          N 
        </mtext> 
        <mrow> 
         <msub> 
          <mtext>
            H 
          </mtext> 
          <mn>
            2 
          </mn> 
         </msub> 
         <msub> 
          <mtext>
            O 
          </mtext> 
          <mn>
            2 
          </mn> 
         </msub> 
        </mrow> 
       </msub> 
       <msub> 
        <mtext>
          V 
        </mtext> 
        <mrow> 
         <msub> 
          <mtext>
            H 
          </mtext> 
          <mn>
            2 
          </mn> 
         </msub> 
         <msub> 
          <mtext>
            O 
          </mtext> 
          <mn>
            2 
          </mn> 
         </msub> 
        </mrow> 
       </msub> 
       <mo>
         = 
       </mo> 
       <msub> 
        <mtext>
          N 
        </mtext> 
        <mrow> 
         <msub> 
          <mrow> 
           <mtext>
             KMnO 
           </mtext> 
          </mrow> 
          <mn>
            4 
          </mn> 
         </msub> 
        </mrow> 
       </msub> 
       <msub> 
        <mtext>
          V 
        </mtext> 
        <mrow> 
         <msub> 
          <mrow> 
           <mtext>
             KMnO 
           </mtext> 
          </mrow> 
          <mn>
            4 
          </mn> 
         </msub> 
        </mrow> 
       </msub> 
      </mrow> 
     </math> (5)</p>
    <p>where N is normality and V is volume.</p>
    <p>
     <xref ref-type="fig" rid="fig2">
      Figure 2
     </xref> shows the evolution of the concentration of hydroxyl radicals generated in-situ during the electrolysis of 0.1M HClO<sub>4</sub>. In <xref ref-type="fig" rid="fig2">
      Figure 2
     </xref>, the concentration of hydrogen peroxide increases during HClO<sub>4</sub> electrolysis from 0 mM at t = 0 min to 1.5 mM after 180 min. The electrolysis of HClO<sub>4</sub> thus leads to the production of hydrogen peroxide and thus of hydroxyl radicals.</p>
    <fig id="fig2" position="float">
     <label>Figure 2</label>
     <caption>
      <title>Figure 2. Electrolysis of 0.1 M HClO<sub>4</sub> at a current density of j = 10 mA/cm<sup>2</sup>.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId25.jpeg?20240902034904" />
    </fig>
    <p>
     <xref ref-type="fig" rid="fig3">
      Figure 3
     </xref> shows the absorbances of 0.5 M, 1 mM hydrogen peroxide from a 35% commercial hydrogen peroxide solution and a HClO<sub>4</sub> sample after 1 hour of electrolysis. A perfect superposition of the absorption curves in the wavelength range from 190 nm to 1100 nm is shown. This shows that the electrolysis of HClO<sub>4</sub> leads to the formation of hydrogen peroxide and therefore hydroxyl radicals.</p>
    <p>Indeed, during the electrolysis of the supporting electrolyte, water is oxidised. The oxidation of H<sub>2</sub>O leads to the formation of hydroxyl radicals (Equation (6)). In the absence of an organic compound, the hydroxyl radicals can only react with each other and form hydrogen peroxide (Equation (7)).</p>
    <p>
     <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
       <mn>
         2 
       </mn> 
       <msub> 
        <mtext>
          H 
        </mtext> 
        <mn>
          2 
        </mn> 
       </msub> 
       <mtext>
         O 
       </mtext> 
       <mo>
         → 
       </mo> 
       <mo>
         ⋅ 
       </mo> 
       <mtext>
         OH 
       </mtext> 
       <mo>
         + 
       </mo> 
       <msup> 
        <mrow> 
         <mtext>
           OH 
         </mtext> 
        </mrow> 
        <mo>
          − 
        </mo> 
       </msup> 
       <mo>
         + 
       </mo> 
       <mn>
         2 
       </mn> 
       <msup> 
        <mtext>
          H 
        </mtext> 
        <mo>
          + 
        </mo> 
       </msup> 
       <mo>
         + 
       </mo> 
       <msup> 
        <mtext>
          e 
        </mtext> 
        <mo>
          − 
        </mo> 
       </msup> 
      </mrow> 
     </math> (6)</p>
    <p>
     <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
       <mo>
         ⋅ 
       </mo> 
       <mtext>
         OH 
       </mtext> 
       <mo>
         + 
       </mo> 
       <mo>
         ⋅ 
       </mo> 
       <mtext>
         OH 
       </mtext> 
       <mo>
         → 
       </mo> 
       <msub> 
        <mtext>
          H 
        </mtext> 
        <mn>
          2 
        </mn> 
       </msub> 
       <msub> 
        <mtext>
          O 
        </mtext> 
        <mn>
          2 
        </mn> 
       </msub> 
      </mrow> 
     </math> (7)</p>
    <fig id="fig3" position="float">
     <label>Figure 3</label>
     <caption>
      <title>Figure 3. Absorption spectrum of hydrogen peroxide and HClO<sub>4</sub>.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId30.jpeg?20240902034903" />
    </fig>
    <p>The amount of hydroxyl radicals generated can be influenced by various parameters including the applied current density. The influence of the applied current (current density 3.125, 5 and 10 mA/cm<sup>2</sup> respectively) on the production of hydroxyl radicals was investigated by monitoring the concentration of hydrogen peroxide during the electrolysis of 0.1 M HClO<sub>4</sub>. The results obtained are presented in <xref ref-type="fig" rid="fig4">
      Figure 4
     </xref>.</p>
    <p>It can be seen from this figure that the production of hydroxyl radicals becomes important with the applied current. For an applied current, the production of hydrogen peroxide, and therefore of hydroxyl radicals, increases with the duration of the electrolysis. Indeed, Gnamba et al showed that the rate of degradation of amoxicillin on the boron-doped diamond electrode (BDD) increased with the imposed current density. This is related to the hydroxyl radicals formed, the amount of which depends on the imposed current.</p>
    <p>The generation of hydroxyl radicals on the BDD occurs as follows:</p>
    <p>
     <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
       <mtext>
         BDD 
       </mtext> 
       <mo>
         + 
       </mo> 
       <msub> 
        <mtext>
          H 
        </mtext> 
        <mn>
          2 
        </mn> 
       </msub> 
       <mtext>
         O 
       </mtext> 
       <mo>
         → 
       </mo> 
       <mtext>
         BDD 
       </mtext> 
       <mrow> 
        <mo>
          ( 
        </mo> 
        <mrow> 
         <mo>
           ⋅ 
         </mo> 
         <mtext>
           OH 
         </mtext> 
        </mrow> 
        <mo>
          ) 
        </mo> 
       </mrow> 
       <mo>
         + 
       </mo> 
       <msup> 
        <mtext>
          H 
        </mtext> 
        <mo>
          + 
        </mo> 
       </msup> 
       <mo>
         + 
       </mo> 
       <msup> 
        <mtext>
          e 
        </mtext> 
        <mo>
          − 
        </mo> 
       </msup> 
      </mrow> 
     </math> (8)</p>
    <fig id="fig4" position="float">
     <label>Figure 4</label>
     <caption>
      <title>Figure 4. Influence of current (0.05 A, 0.08 A, 0.16 A) on H<sub>2</sub>O<sub>2</sub> production for 0.1 M HClO<sub>4</sub>.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId33.jpeg?20240902034904" />
    </fig>
    <p>Electrolysis of several concentrations (0.1 M, 0.2 M, 0.4 M) of perchloric acid was performed on the BDD at a current density of 5 mA/cm² for 180 min. <xref ref-type="fig" rid="fig5">
      Figure 5
     </xref> shows the hydrogen peroxide concentration versus time curves. In <xref ref-type="fig" rid="fig5">
      Figure 5
     </xref>, it can be seen that the concentration of H<sub>2</sub>O<sub>2</sub>, initially zero for all investigated concentrations, increases to 0.723, 1.10 and 1.915 mM after 180 min of electrolysis for 0.1, 0.2 and 0.4 M 0.1 M HClO<sub>4</sub> respectively. This shows that the initial concentration of HClO<sub>4</sub> plays an important role in the production of hydroxyl radicals.</p>
    <fig id="fig5" position="float">
     <label>Figure 5</label>
     <caption>
      <title>Figure 5. Influence of HClO<sub>4</sub> (0.1 M, 0.2 M, 0.4 M) on hydrogen peroxide production at 5 mA/cm<sup>2</sup>.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId34.jpeg?20240902034905" />
    </fig>
   </sec>
   <sec id="s3_2">
    <title>3.2. In-Situ Determination of Chlorine</title>
    <p>Chlorine detection was investigated by degradation of a sodium chloride solution (0.1 M) under a current density of 10 mA/cm². In order to promote chlorine generation, the initial pH (6.833) was reduced and maintained at 2 using 1 M HClO<sub>4</sub>. The electrode used at the anode for NaCl electrolysis was boron-doped diamond (BDD). After 15 minutes of electrolysis, a suffocating and very unpleasant odour characteristic of chlorine release was noted. After 30 min of electrolysis, NaCl samples were taken and tested for Cl<sub>2</sub>. NaI and hexane were added to the NaCl electrolysis samples. The photo in <xref ref-type="fig" rid="fig6">
      Figure 6
     </xref> shows the photo of the NaCl sample after 30 minutes of electrolysis (tube A), the tube containing the NaCl (30 minutes) + NaI sample (tube B). The third tube C contains a mixture of NaI + NaCl (30 minutes) + 1 mL of hexane and tube D, NaI+ NaCl (30 minutes) + 2 - 5 mL of hexane.</p>
    <fig id="fig6" position="float">
     <label>Figure 6</label>
     <caption>
      <title>Figure 6. Photo of Cl<sub>2</sub> test.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId35.jpeg?20240902034906" />
    </fig>
    <p>According to this picture, the addition of NaI to the NaCl sample gives a yellow coloration indicating the presence of an oxidant. The addition of hexane (2 - 5 mL) to the NaCl + NaI mixture gives a pinkish-purple colouration. This would indicate the presence of the oxidant Cl<sub>2</sub>. It should be noted that a very suffocating odour is given off during the electrolysis of NaCl. To confirm that chlorine is responsible for the pinkish-purple colouration observed, the same test was carried out during the electrolysis of some solutions containing halogens (NaI and NaBr).</p>
    <p>Electrolysis of NaBr concentration (0.1 M) under a current density of 10 mA/cm<sup>2</sup> was performed. The electrode used was boron-doped diamond (BDD). During this electrolysis, a 5 mL sample was taken after 30 minutes of electrolysis. In order to highlight the purplish-pink coloration of the hexane, NaI (0.2 M) and hexane were added to the samples of the NaBr electrolysis. The result obtained is shown in <xref ref-type="fig" rid="fig7">
      Figure 7
     </xref>.</p>
    <p>The colour of the NaBr electrolyte solution is pale green (<xref ref-type="fig" rid="fig7(a)">
      Figure 7(a)
     </xref>). The addition of NaI (0.2 M) (<xref ref-type="fig" rid="fig7(b)">
      Figure 7(b)
     </xref>) to this solution transforms this green colour (bromine water colour) into yellow, indicating the presence of an oxidant, in this case Br<sub>2</sub>. The addition of hexane to the mixture (NaBr + NaI) (<xref ref-type="fig" rid="fig7(c)">
      Figure 7(c)
     </xref>) leads to a very pale pink colouration on the surface of the mixture (<xref ref-type="fig" rid="fig7(c)">
      Figure 7(c)
     </xref>). This could be characteristic of the presence of a weak oxidant (Br<sub>2</sub>) in the reaction medium.</p>
    <fig id="fig7" position="float">
     <label>Figure 7</label>
     <caption>
      <title>Figure 7. (a) Staining of the NaBr (0.1 M) electrolyte solution after 1 hour of electrolysis; (b) Staining of NaBr (0.1 M) electrolyte solution after 30 minutes of electrolysis; (c) Electrolyte solution mixture of 5 mL 0.1 M NaBr + 1 mL 0.2 M NaI + 2 mL hexane.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId36.jpeg?20240902034906" />
    </fig>
    <p>The electrolysis of NaI concentration (0.1 M) was carried out under a current density of 10 mA/cm<sup>2</sup>. The electrode used was boron-doped diamond (BDD). A sample of the NaI solution was taken after 30 minutes of electrolysis. To highlight the purplish-pink coloration of the hexane; NaI (0.2 M) and hexane were added to the sample taken from the NaI electrolysis. The result obtained is shown in <xref ref-type="fig" rid="fig8">
      Figure 8
     </xref>.</p>
    <fig id="fig8" position="float">
     <label>Figure 8</label>
     <caption>
      <title>Figure 8. (a) Coloration of the NaI (0.1 M) electrolyte solution after 1 hour of electrolysis; (b) Coloration of NaI (0.1 M) electrolyte solution after 30 minutes of electrolysis; (c) Electrolyte solution mixture of 5 mL 0.1 M + NaI 1 mL 0.2 M + NaI 2 mL hexane.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId37.jpeg?20240902034906" />
    </fig>
    <p>The coloration of the NaI solution after 30 minutes of electrolysis is orange-yellow (<xref ref-type="fig" rid="fig8(a)">
      Figure 8(a)
     </xref>) characteristic of the presence of I<sub>2</sub>. This colouration is maintained with the addition of NaI (<xref ref-type="fig" rid="fig8(b)">
      Figure 8(b)
     </xref>), attesting to the presence of an oxidant, I<sub>2</sub>. The addition of hexane leads to a very pale pink coloration on the surface of the mixture (<xref ref-type="fig" rid="fig8(c)">
      Figure 8(c)
     </xref>). This could be characteristic of the presence of a weak oxidant (I<sub>2</sub>) in the reaction medium.</p>
    <p>The chlorine detection test was carried out on the electrolytic solutions of NaCl, NaBr and NaI. From these investigations, it appears that the test is positive with all these solutions indicating the formation of oxidants during preparative electrolysis. However, the vivid purplish-pink colouration obtained in the NaCl case, highlighting the electrogeneration of chlorine, in contrast to the very pale pink colouration obtained in the case of NaBr and NaI would show a selectivity of this method. This technique can therefore be applied to the detection of chlorine.</p>
    <p>The electrolysis of 0.1 M HClO<sub>4</sub> was performed on the DDB electrode at a current density of 10 mA/cm<sup>2</sup>.</p>
    <p>In order to demonstrate the presence of chlorine during the electrolysis of perchloric acid, 10 mL of the reaction mixture was taken and 1 mL of NaI (0.2 M) and 2 mL of hexane were added. The mixture was stirred vigorously and then left to stand to allow decantation. The photo in <xref ref-type="fig" rid="fig9">
      Figure 9
     </xref> shows the mixture of the electrolyte solution, NaI and hexane.</p>
    <fig id="fig9" position="float">
     <label>Figure 9</label>
     <caption>
      <title>Figure 9. (a) Electrolyte solution mixture of 10 mL 0.1 M HClO<sub>4</sub> + 1 mL 0.2 M NaI; (b) 10 mL 0.1 M + HClO<sub>4</sub> electrolyte solution mixture 1 mL 0.2 M + NaI 2 mL hexane.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId38.jpeg?20240902034906" />
    </fig>
    <p>In <xref ref-type="fig" rid="fig9(a)">
      Figure 9(a)
     </xref>, mixing the 0.1 M HClO<sub>4</sub> and 0.2 M NaI electrolyte solution gives a yellow coloration. The addition of hexane leads to a purplish-pink coloration on the surface of the mixture (<xref ref-type="fig" rid="fig9(b)">
      Figure 9(b)
     </xref>). This is characteristic of the presence of Cl<sub>2</sub> in the mixture. Indeed, the initial pH of the reaction medium was 0.865 and was maintained below 2.5 throughout the electrolysis. This confirms the formation of Cl<sub>2</sub> during the electrolysis of 0.1 M HClO<sub>4</sub>. Compared to NaCl electrolysis, 0.1 M HClO<sub>4</sub> electrolysis does not cause a suffocating odour to be released.</p>
    <p>The formation of chlorine can be summarised as follows (Equation (9)):</p>
    <p>
     <math display="inline" xmlns="http://www.w3.org/1998/Math/MathML"> <mrow> 
       <mn>
         4 
       </mn> 
       <msub> 
        <mrow> 
         <mtext>
           HClO 
         </mtext> 
        </mrow> 
        <mn>
          4 
        </mn> 
       </msub> 
       <mo>
         → 
       </mo> 
       <mn>
         2 
       </mn> 
       <msub> 
        <mrow> 
         <mtext>
           Cl 
         </mtext> 
        </mrow> 
        <mn>
          2 
        </mn> 
       </msub> 
       <mo>
         + 
       </mo> 
       <mn>
         7 
       </mn> 
       <msub> 
        <mtext>
          O 
        </mtext> 
        <mn>
          2 
        </mn> 
       </msub> 
       <mo>
         + 
       </mo> 
       <mn>
         2 
       </mn> 
       <msub> 
        <mtext>
          H 
        </mtext> 
        <mn>
          2 
        </mn> 
       </msub> 
       <mtext>
         O 
       </mtext> 
      </mrow> 
     </math> (9)</p>
   </sec>
   <sec id="s3_3">
    <title>3.3. Degradation of MNZ: Identification of Hydroxyl Radicals and Chlorine</title>
    <p>In-situ detection of hydroxyl radicals and chlorine was investigated during electrolysis of HClO4 (0.1 M) containing 0.1 g/L metronidazole (MNZ) under a current density of 10 mA/cm<sup>2</sup>.</p>
    <p>To detect the hydroxyl radicals, 10 mL of the sample mixture (KClO<sub>4</sub> + MNZ) was assayed at different times with KMnO<sub>4</sub> of 10<sup>−</sup><sup>4</sup> M concentration. The results are shown in <xref ref-type="fig" rid="fig10">
      Figure 10
     </xref>.</p>
    <fig id="fig10" position="float">
     <label>Figure 10</label>
     <caption>
      <title>Figure 10. Comparison between electrolysed HClO<sub>4</sub> and electrolysed (HClO<sub>4</sub> + MNZ). Inset: Evolution of hydrogen peroxide during electrolysis of MNZ in HClO<sub>4</sub>.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId41.jpeg?20240902034907" />
    </fig>
    <p>According to this figure, the concentration of hydrogen peroxide increases from 0 to 0.13 mM after 120 minutes of electrolysis and then remains almost constant until 150 minutes (inset in <xref ref-type="fig" rid="fig10">
      Figure 10
     </xref>). This shows that hydroxyl radicals are formed during the degradation of MNZ on boron-doped diamond. However, the amount of hydroxyl radicals detected during the degradation of MNZ is much lower than that detected during the electrolysis of HClO<sub>4</sub>.</p>
    <p>For example, for 60 minutes of electrolysis, the amount of radicals detected in HClO<sub>4</sub> alone is almost 9 times that detected in the case (MNZ + HClO<sub>4</sub>). This difference could be explained by the fact that the hydroxyl radicals generated during the electrolysis of MNZ participate significantly in the degradation of the organic compound (metronidazole).</p>
    <p>The degradation of MNZ (0.1 g/L) in a 0.1 M HClO<sub>4</sub> solution on the DDB at a density of 10 mA/cm<sup>2</sup> was monitored by measuring the COD. The results obtained are shown in <xref ref-type="fig" rid="fig11">
      Figure 11
     </xref>.</p>
    <p>The COD evolution curve obtained decreases exponentially. The decrease in COD during electrolysis implies that the MNZ is degraded on the BDD below 10 mA/cm<sup>2</sup>. This degradation leads to a COD removal rate of 83.48% after 180 minutes of electrolysis.</p>
    <p>The limiting current density, determined by Equation (6), for the degradation of MNZ is 0.473 mA/cm<sup>2</sup>, which is lower than 10 mA/cm<sup>2</sup>. The degradation of MNZ was essentially controlled by mass transfer, i.e. limited by diffusion. This can explain the exponential curve of the COD.</p>
    <p>J<sub>lim</sub> = 4Fk<sub>d</sub>COD (10)</p>
    <p>where F is faraday constant (96458 C/mol); k<sub>d</sub> is mass transfer coefficient (cm/s) and COD in mol O<sub>2</sub>/L.</p>
    <fig id="fig11" position="float">
     <label>Figure 11</label>
     <caption>
      <title>Figure 11. Evolution of COD during degradation of 0.1 g/L MNZ under a current density of 10 mA/cm<sup>2</sup>. Supporting electrolyte HClO<sub>4</sub> 0.1 M, T = 25˚C.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId42.jpeg?20240902034907" />
    </fig>
    <p>In <xref ref-type="fig" rid="fig12">
      Figure 12
     </xref>, mixing the solution of electrolysed MNZ in 0.1 M HClO<sub>4</sub> and 0.2 M NaI gives a yellow coloration. The addition of hexane leads to a purplish-pink coloration on the surface of the mixture. This is characteristic of the presence of Cl<sub>2</sub> in the mixture. Indeed, the initial pH of the reaction medium was kept below 2.5 throughout the electrolysis. The purplish-pink colouration is characteristic of the presence of Cl<sub>2</sub> in the reaction medium during the electrolysis of MNZ in 0.1 M HClO<sub>4</sub>.</p>
    <fig id="fig12" position="float">
     <label>Figure 12</label>
     <caption>
      <title>Figure 12. Electrolyte solution + a quantity of NaI + hexane at T = 25˚C.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/3701293-rId43.jpeg?20240902034907" />
    </fig>
   </sec>
  </sec><sec id="s4">
   <title>4. Conclusions</title>
   <p>The objective of our work was to establish alternative methods for the in-situ detection and quantification of the oxidants <sup>•</sup>OH and Cl<sub>2</sub>. To achieve our objective, these oxidants were detected in the absence and presence of metronidazole. The in-situ determination of hydroxyl radicals during the electrolysis of a 0.1 M perchloric acid (HClO<sub>4</sub>) solution was performed. The results obtained show that the electrolysis of HClO<sub>4</sub> leads to the production of hydroxyl radicals. The quantification of hydroxyl radicals was done by dosing the electrolysed solution with a KMnO<sub>4</sub> solution. The amount of hydroxyl radicals produced depends on some parameters such as the current density and the initial concentration of HClO<sub>4</sub>. This amount of <sup>•</sup>OH increases with a current density ranging from 3.125 to 10 mA/cm<sup>2</sup> and then with the increase of the initial HClO<sub>4</sub> concentration.</p>
   <p>Chlorine was detected by colorimetric determination. The results obtained showed that the presence of chlorine is proven by a purplish-pink coloration of the hexane. The formation of Cl<sub>2</sub> was also demonstrated during the electrolysis of 0.1 M HClO<sub>4</sub>. We also carried out the electrooxidation of metronidazole (0.1 g/L) in a 0.1 M HClO<sub>4</sub> solution on the DDB at a density of 10 mA/cm<sup>2</sup> and monitored it by measuring the COD. The electrolysis of metronidazole showed that hydroxyl radicals and chlorine were produced and contributed to its degradation.</p>
  </sec>
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