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  <front>
    <journal-meta>
      <journal-id journal-id-type="publisher-id">jep</journal-id>
      <journal-title-group>
        <journal-title>Journal of Environmental Protection</journal-title>
      </journal-title-group>
      <issn pub-type="epub">2152-2219</issn>
      <issn pub-type="ppub">2152-2197</issn>
      <publisher>
        <publisher-name>Scientific Research Publishing</publisher-name>
      </publisher>
    </journal-meta>
    <article-meta>
      <article-id pub-id-type="doi">10.4236/jep.2026.179050</article-id>
      <article-id pub-id-type="publisher-id">jep-153932</article-id>
      <article-categories>
        <subj-group>
          <subject>Article</subject>
        </subj-group>
        <subj-group>
          <subject>Earth</subject>
          <subject>Environmental Sciences</subject>
        </subj-group>
      </article-categories>
      <title-group>
        <article-title>Characterization of Well Water, Borehole Water and Wastewater in the Port Zone of Lomé: Physicochemical, Microbiological and Bioassay Approach</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <name name-style="western">
            <surname>Abi</surname>
            <given-names>Hazou</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <name name-style="western">
            <surname>Badjabaissi</surname>
            <given-names>Essotolom</given-names>
          </name>
          <xref ref-type="aff" rid="aff2">2</xref>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
        <contrib contrib-type="author">
          <name name-style="western">
            <surname>Dossou-Yovo</surname>
            <given-names>Komlan Mawubédjro</given-names>
          </name>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
        <contrib contrib-type="author">
          <name name-style="western">
            <surname>Koriko</surname>
            <given-names>Moursalou</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <name name-style="western">
            <surname>Diallo</surname>
            <given-names>Aboudoulatif</given-names>
          </name>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
      </contrib-group>
      <aff id="aff1"><label>1</label> Laboratory of Waste Management, Treatment and Valorization, University of Lome, Lome, Togo </aff>
      <aff id="aff2"><label>2</label> Laboratory of Water, Food and Miscellaneous Products Chemistry, University of Lome, Lome, Togo </aff>
      <aff id="aff3"><label>3</label> Toxicology Laboratory, Faculty of Health Sciences (FSS), University of Lome, Lome, Togo </aff>
      <author-notes>
        <fn fn-type="conflict" id="fn-conflict">
          <p>The authors declare no conflicts of interest regarding the publication of this paper.</p>
        </fn>
      </author-notes>
      <pub-date pub-type="epub">
        <day>07</day>
        <month>09</month>
        <year>2026</year>
      </pub-date>
      <pub-date pub-type="collection">
        <month>09</month>
        <year>2026</year>
      </pub-date>
      <volume>17</volume>
      <issue>09</issue>
      <fpage>970</fpage>
      <lpage>988</lpage>
      <history>
        <date date-type="received">
          <day>09</day>
          <month>08</month>
          <year>2026</year>
        </date>
        <date date-type="accepted">
          <day>15</day>
          <month>09</month>
          <year>2026</year>
        </date>
        <date date-type="published">
          <day>18</day>
          <month>09</month>
          <year>2026</year>
        </date>
      </history>
      <permissions>
        <copyright-statement>© 2026 by the authors and Scientific Research Publishing Inc.</copyright-statement>
        <copyright-year>2026</copyright-year>
        <license license-type="open-access">
          <license-p> This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license ( <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">https://creativecommons.org/licenses/by/4.0/</ext-link> ). </license-p>
        </license>
      </permissions>
      <self-uri content-type="doi" xlink:href="https://doi.org/10.4236/jep.2026.179050">https://doi.org/10.4236/jep.2026.179050</self-uri>
      <abstract>
        <p>This study characterizes the physicochemical and microbiological quality of well water, borehole water, wastewater and water of the 4<sup>th</sup> lake in the port zone of Lomé. Fourteen (14) water samples were collected following usual sampling standards. Physicochemical analyses covered turbidity, conductivity, pH, nitrogen compounds, and trace metal elements, and biodegradability. Microbiological analyses targeted heterotrophic bacteria, thermotolerant coliforms, salmonella, and clostridia and performed according to the standardized methods of the French Association for Standardization. A bioassay using the larvae of <italic>Artemia salina</italic> was carried out in order to assess the toxicity of the samples. Physicochemical analyses revealed a high conductivity in almost all the samples tested (&gt;400 µS/cm). Ammonium concentration was very high in one of the borehole waters 1 (12 mg <inline-formula><mml:math></mml:math></inline-formula></p>
        <p>NH</p>
        <p>4</p>
        <p>+</p>
        <p>/L). Nitrate concentration was high (&gt;50 mg <inline-formula><mml:math></mml:math></inline-formula></p>
        <p>NO</p>
        <p>3</p>
        <p>−</p>
        <p>/L) in well water 1, 2, 4, and borehole water 1. Biodegradability index was high (&gt;3) in wastewater 1, 2, 3 and 4. Trace metal elements like arsenic (As) showed very high concentrations, above 10 µg/L, in wastewater 4. Microbiological parameters, of various well water and borehole water samples contained heterotrophic bacteria and thermotolerant coliforms (TC) at very high values. Clostridium (Clost) were found in the surface water samples while salmonella (Sal) was found only in wastewater 2, 3 and 5. The mortality rate of the larvae of <italic>Artemia salina</italic>was mainly high in the wastewater samples. Water samples of the port zone of Lomé, whether they come from wells, boreholes or wastewater, show clear signs of contamination. Groundwater use for domestic, hygiene and food purposes should be subject to prior treatment in order to improve its quality and to reduce health risks and wastewater’s heavy contamination underlines the urgent need for its appropriate management and treatment.</p>
      </abstract>
      <kwd-group kwd-group-type="author-generated" xml:lang="en">
        <kwd>Port</kwd>
        <kwd>Wastewater</kwd>
        <kwd>Boreholes</kwd>
        <kwd>Wells</kwd>
        <kwd>Pollution</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec1">
      <title>1. Introduction</title>
      <p>Water, a vital resource for all living beings, is a fundamental need of Man and is involved in domestic, hygiene and food use [<xref ref-type="bibr" rid="B1">1</xref>]. When it is taken as a drink, water must be potable. It must therefore meet the quality requirements set by the relevant standards concerning microbiological, chemical, radiological and aesthetic aspects [<xref ref-type="bibr" rid="B1">1</xref>]. Whether it is surface water (river, stream, lake or pond water) or groundwater (well, borehole, tap water), its quality is a determining factor for health [<xref ref-type="bibr" rid="B2">2</xref>]. Water quality is strongly influenced by anthropogenic pressures such as urbanization, industrialization, agriculture, port activities and shortcomings in sanitation. These human activities would therefore contribute to a deterioration of water quality through the production of pollutants that may end up in water [<xref ref-type="bibr" rid="B3">3</xref>]. Among these activities are those linked to ports and to mining. In Togo, previous work has highlighted the link between mining activities and cases of water pollution by heavy metals [<xref ref-type="bibr" rid="B4">4</xref>]. As regards port activities, they can lead to water pollution [<xref ref-type="bibr" rid="B5">5</xref>] through the accidental or deliberate discharge of hydrocarbons and waste by ships, and through run-off water which carries organic waste, heavy metals and particles towards water sources. In the port zone of Lomé, also classified as a free zone, the high concentration of industrial activities increases the risks of pollution. Indeed, this port free zone is heavily industrialized with nearly 36 industries, operating in the cosmetics, chemical, plastics, food, metal and pharmaceutical sectors [<xref ref-type="bibr" rid="B6">6</xref>]. These industries could also generate pollutants. In addition to these toxic substances, the presence of pathogenic microorganisms or bacteria can also alter water quality, thus contributing to water pollution [<xref ref-type="bibr" rid="B7">7</xref>]. Water pollution corresponds to its degradation or contamination through the introduction of toxic substances. These substances would affect the natural characteristics of water, in particular the biological and physicochemical characteristics, thus constituting a health risk in the event of consumption by the population. In 2019, water pollution was the cause of 1 - 4 million premature deaths throughout the world [<xref ref-type="bibr" rid="B8">8</xref>]. In Togo, previous studies carried out in certain localities of the country, in particular in Lomé [<xref ref-type="bibr" rid="B7">7</xref>], Tsévié [<xref ref-type="bibr" rid="B9">9</xref>], Tchaoudjo [<xref ref-type="bibr" rid="B10">10</xref>] and in the mining area of Bangéli [<xref ref-type="bibr" rid="B4">4</xref>] have made it possible to assess water quality in these areas. However, despite the high population density and the industrial concentration in the port zone of Lomé [<xref ref-type="bibr" rid="B8">8</xref>], no scientific data exist on the impact of port activities on the quality of the environment. This work therefore falls within the framework of the physicochemical and microbiological characterization of pollution in an industrial and urban setting with a view to assessing the water quality in the port zone of Lomé. </p>
    </sec>
    <sec id="sec2">
      <title>2. Material and Methods</title>
      <sec id="sec2dot1">
        <title>2.1. Collection of the Water Samples</title>
        <fig id="fig1">
          <label>Figure 1</label>
          <graphic xlink:href="https://html.scirp.org/file/6705772-rId17.jpeg?20260918095039" />
        </fig>
        <p><bold>Figure 1</bold><bold>.</bold> Map indicating the position of the sampling sites.</p>
        <p>Fourteen (14) water samples were collected: four (04) from wells (W1-W4), five (05) from boreholes (BH1-BH5), four (04) from wastewater (WW1-WW4) and one (01) from the 4<sup>th</sup> lake (WW5). The sampling campaign was carried out in August 2025, corresponding to the short dry season in the south of Togo. The sampling points were geo-referenced using a Garmin 700 GPS. <xref ref-type="fig" rid="fig1">Figure 1</xref> indicate the position of the sampling sites. The samples were collected according to the standard sampling and preservation standards within port zone of Lomé. This zone includes industrial activities area, business activities area and housing area. </p>
        <p>The samples for the physicochemical analyses were collected in polyethylene bottles (1.5 L), while those intended for the microbiological analyses were taken in sterile borosilicate bottles [<xref ref-type="bibr" rid="B11">11</xref>]. </p>
        <p>After collection, the samples were kept in insulated cool boxes with cold accumulators, at a temperature of 5 ± 3˚C, in order to limit microbial activity and to preserve the integrity of the analyses [<xref ref-type="bibr" rid="B12">12</xref>]. The samples intended for the determination of cations and trace metal elements were acidified with nitric acid in order to prevent any precipitation. </p>
      </sec>
      <sec id="sec2dot2">
        <title>2.2. Laboratory Analyses</title>
        <p>The samples taken were subjected to physicochemical and microbiological analyses and to a bioassay.</p>
        <p>2.2.1. Physicochemical Analyses</p>
        <p>The physicochemical analyses covered the measurement of pH, turbidity, conductivity, temperature, nitrogen compounds (nitrates, nitrites, ammonium), phosphorus compounds (<inline-formula><mml:math><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> PO </mml:mtext></mml:mrow><mml:mtext> 4 </mml:mtext><mml:mrow><mml:mn> 3 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ), alkaline elements and trace metal elements (Hg, As, Pb, Cd, Zn, Ni, Cu). </p>
        <p>For the wastewater and the water of the 4<sup>th</sup> lake, the chemical oxygen demand (COD) and the five-day biochemical oxygen demand (BOD<sub>5</sub>) were determined. The COD and the BOD<sub>5</sub> made it possible to determine the degree of biodegradability of the wastewater. These analyses were conducted according to the analytical methods of the French Association for Standardization (AFNOR) as shown in <bold>T</bold><bold>able 1</bold> [<xref ref-type="bibr" rid="B11">11</xref>]. </p>
        <p><bold>Table 1</bold><bold>.</bold> Materials and methods.</p>
        <table-wrap id="tbl1">
          <label>Table 1</label>
          <table>
            <tbody>
              <tr>
                <td colspan="2">
                  <bold>Physicochemical parameters</bold>
                </td>
                <td>
                  <bold>Equipment</bold>
                </td>
                <td>
                  <bold>Method</bold>
                </td>
                <td>
                  <bold>Standards</bold>
                </td>
              </tr>
              <tr>
                <td colspan="2">Temperature</td>
                <td>Thermometer</td>
                <td>Thermometer</td>
                <td>Manufacturer’s method</td>
              </tr>
              <tr>
                <td rowspan="4">Alkalinity</td>
                <td>Phenolphthalein alkalinity (TA)</td>
                <td>Graduated burette</td>
                <td>Titrimetry</td>
                <td>
                  ISO 9963-1/-2 1
                  <sup>st</sup>
                  ed 1994
                </td>
              </tr>
              <tr>
                <td>Total alkalinity (TAC)</td>
                <td>Total alkalinity (TAC)</td>
                <td>Graduated burette</td>
                <td>Titrimetry</td>
              </tr>
              <tr>
                <td>
                  CO
                  <sub>3</sub>
                </td>
                <td>Graduated burette</td>
                <td>Titrimetry</td>
                <td>
                  ISO 9963-1/-2 1
                  <sup>st</sup>
                  ed 1994
                </td>
              </tr>
              <tr>
                <td>
                  HCO
                  <sub>3</sub>
                </td>
                <td>Graduated burette</td>
                <td>Titrimetry</td>
                <td>
                  ISO 9963-1/-2 1
                  <sup>st</sup>
                  ed 1994
                </td>
              </tr>
              <tr>
                <td colspan="2">Ph</td>
                <td>WTW pH 330i pH meter</td>
                <td>Electrometry</td>
                <td>AFNOR NFT 90-008</td>
              </tr>
              <tr>
                <td colspan="2">Conductivity</td>
                <td>WTW Cond 330i conductivity meter</td>
                <td>Conductimetry</td>
                <td>AFNOR 90-031</td>
              </tr>
              <tr>
                <td colspan="2">Nitrates</td>
                <td>Digitron Elvi 675 spectrophotometer</td>
                <td>Molecular absorption spectrometry</td>
                <td>AFNOR NFT 90-012</td>
              </tr>
              <tr>
                <td colspan="2">Nitrites</td>
                <td>Digitron Elvi 675 spectrophotometer</td>
                <td>Molecular absorption spectrometry</td>
                <td>AFNOR NFT 90-012</td>
              </tr>
              <tr>
                <td colspan="2">Ammonium</td>
                <td>Digitron Elvi 675 spectrophotometer</td>
                <td>Molecular absorption spectrophotometer</td>
                <td>AFNOR NFT 90-015</td>
              </tr>
              <tr>
                <td colspan="2">Phosphates</td>
                <td>Molecular absorption spectrophotometer</td>
                <td>Spectrometry</td>
                <td>ISO 6878/2nd ed 2004</td>
              </tr>
              <tr>
                <td colspan="2">Sulfates</td>
                <td>Digitron Elvi 675 spectrophotometer</td>
                <td>Nephelometry</td>
                <td>AFNOR NFT 90-009</td>
              </tr>
              <tr>
                <td colspan="2">COD</td>
                <td>Reflux digestion block</td>
                <td>Acidimetry</td>
                <td>ISO 6060</td>
              </tr>
              <tr>
                <td colspan="2">
                  BOD
                  <sub>5</sub>
                </td>
                <td>Incubation bottles Glassware</td>
                <td>Dilution method</td>
                <td>ISO 5815-1 &amp; 2:</td>
              </tr>
              <tr>
                <td colspan="2">Trace metal elements (cadmium, lead, zinc)</td>
                <td>Flame atomic absorption spectrometer</td>
                <td>Atomic absorption spectrophotometry</td>
                <td>
                </td>
              </tr>
              <tr>
                <td colspan="2">Trace metal elements (arsenic)</td>
                <td>Atomic absorption spectrometer + Hydride Generation module</td>
                <td>Atomic absorption spectrophotometry</td>
                <td>
                </td>
              </tr>
              <tr>
                <td colspan="2">Trace metal elements (mercury)</td>
                <td>Atomic absorption spectrometer + Cold vapor module</td>
                <td>Atomic absorption spectrophotometry</td>
                <td>
                </td>
              </tr>
              <tr>
                <td rowspan="3">Hardness</td>
                <td>Total hardness (TH)</td>
                <td>Graduated burette</td>
                <td>Complexometry</td>
                <td>T 90-003 AFNOR-R-9th ed</td>
              </tr>
              <tr>
                <td>Mg</td>
                <td>Graduated burette</td>
                <td>EDTA complexometry</td>
                <td>AFNOR NFT 90-016</td>
              </tr>
              <tr>
                <td>Ca</td>
                <td>Graduated burette</td>
                <td>EDTA complexometry</td>
                <td>AFNOR NFT 90-016</td>
              </tr>
              <tr>
                <td rowspan="2">Salinity</td>
                <td>Na</td>
                <td>Perkin Elmer model 2380 spectrophotometer</td>
                <td>Atomic absorption spectrophotometer</td>
                <td>AFNOR NFT 90-20</td>
              </tr>
              <tr>
                <td>Cl</td>
                <td>Graduated burette</td>
                <td>Argentometry</td>
                <td>AFNOR NFT 90-014</td>
              </tr>
              <tr>
                <td colspan="2">K</td>
                <td>Perkin Elmer model 2380 spectrophotometer</td>
                <td>Atomic absorption spectrophotometer</td>
                <td>AFNOR NFT 90-20</td>
              </tr>
              <tr>
                <td colspan="2">F</td>
                <td>
                </td>
                <td>Spectrophotometry (colorimetry)</td>
                <td>Water analysis methods according to Rodier</td>
              </tr>
              <tr>
                <td colspan="2">
                  KMnO
                  <sub>4</sub>
                </td>
                <td>Graduated burette</td>
                <td>Hot acid method</td>
                <td>ISO 8467/2nd ed 1993</td>
              </tr>
              <tr>
                <td rowspan="2">Organoleptic</td>
                <td>Odour</td>
                <td>
                </td>
                <td>Olfactory</td>
                <td>ISO 8586</td>
              </tr>
              <tr>
                <td>Colour</td>
                <td>Molecular absorption spectrophotometer</td>
                <td>Cobalt-platinum</td>
                <td>Manufacturer’s method.</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p>ISO: International Organization for Standardization, BOD<sub>5</sub>: Five-day biochemical oxygen demand, COD: Chemical oxygen demand, AFNOR: French Association for Standardization.</p>
        <p>2.2.2. Microbiological Analyses</p>
        <p>These analyses were carried out in accordance with the recommendations in force for the microbiological analyses of food and water samples as shown in <bold>T</bold><bold>able 2</bold> [<xref ref-type="bibr" rid="B12">12</xref>].</p>
        <p><bold>Table 2</bold><bold>.</bold> Equipment and standards used for the microbiological analyses.</p>
        <table-wrap id="tbl2">
          <label>Table 2</label>
          <table>
            <tbody>
              <tr>
                <td>Target microorganisms</td>
                <td>Equipment/culture media</td>
                <td>Standards</td>
              </tr>
              <tr>
                <td>Total aerobic mesophilic flora (TAMF) and heterotrophic microorganisms</td>
                <td>Plate count agar for water (PCA)</td>
                <td>EN ISO6222</td>
              </tr>
              <tr>
                <td>Thermotolerant coliforms</td>
                <td>Chromogenic coliform agar (CCA)</td>
                <td>EN ISO 9308-1</td>
              </tr>
              <tr>
                <td>Faecal enterococci or faecal streptococci in drinking water</td>
                <td>Slanetz-Bartley agar and bile esculin agar</td>
                <td>EN-ISO 7899-2</td>
              </tr>
              <tr>
                <td>Clostridium</td>
                <td>Tryptose sulfite cycloserine agar (TSC)</td>
                <td>EN 26461-2</td>
              </tr>
              <tr>
                <td>Salmonella</td>
                <td>XLD (xylose lysine deoxycholate) agar and Hektoen agar</td>
                <td>ISO 6579</td>
              </tr>
              <tr>
                <td>Faecal enterococci in wastewater</td>
                <td>Rothe broth</td>
                <td rowspan="3">EN ISO 7899-1</td>
              </tr>
              <tr>
                <td>Coliforms in wastewater</td>
                <td rowspan="2">2% brilliant green bile lactose broth</td>
              </tr>
              <tr>
                <td>
                  <italic>E</italic>
                  .
                  <italic>coli in wastewater</italic>
                </td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><italic>E</italic>.<italic>coli: Escherichia coli</italic><italic>;</italic> ISO: International Organization for Standardization.</p>
        <p>2.2.3. Bioassay</p>
        <p>In the framework of this study, the larvae of <italic>Artemia salina</italic>(crustacean) were used as biological material to assess the toxicity of the water samples of the port zone according to the methods of Lu <italic>et al</italic>. [<xref ref-type="bibr" rid="B13">13</xref>] and of Dossou-Yovo <italic>et al</italic>. [<xref ref-type="bibr" rid="B14">14</xref>], slightly modified. For each sample and control, 6 replicate were done and the average number of dead larvae was determined and the mortality rate calculated by applying Abbott’s correction formula (% Toxicity = [(treated mortality - control mortality)/(100 -control mortality)] × 100).</p>
        <p>The test was validated only if the mortality rate of the larvae did not exceed 10% in the control batches.</p>
      </sec>
    </sec>
    <sec id="sec3">
      <title>3. Results</title>
      <p>The results were presented by type of water (well water, borehole water and wastewater) and by group of parameters (physicochemical and microbiological parameters), as well as the bioassays.</p>
      <sec id="sec3dot1">
        <title>3.1. Physicochemical Parameters</title>
        <p><bold>Tables 3</bold><bold>-</bold><bold>5</bold> present the main physicochemical parameters as well as the organoleptic characteristics of the groundwater (wells and boreholes) and of the surface water (wastewater and 4<sup>th</sup> lake). Parameters such as taste, odour, pH, turbidity and temperature were normal in the groundwater samples. In contrast, conductivity exceeded the values recommended by the European Union guidelines. Likewise, the ammonium concentration was particularly high in sample BH1. </p>
        <p>Concerning the surface water, only one sample out of five was odourless. Some showed a high turbidity (WW3 and WW4). The conductivity of these surface water samples was also high (WW1 and WW4). </p>
        <p>Furthermore, some samples showed high contents of alkaline elements such as Na, K, Fe and Cl (W1, W2 and BH1).</p>
        <p><bold>Table 3</bold><bold>.</bold> Physicochemical parameters of well water.</p>
        <table-wrap id="tbl3">
          <label>Table 3</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="4">
                  <bold>Well water</bold>
                </td>
                <td rowspan="2">
                  <bold>Permissible conc</bold>
                  <bold>(RF* UE**)</bold>
                </td>
                <td rowspan="2">
                  <bold>WHO</bold>
                  <bold>guidelines</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>W1</bold>
                </td>
                <td>
                  <bold>W2</bold>
                </td>
                <td>
                  <bold>W3</bold>
                </td>
                <td>
                  <bold>W4</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Odour</bold>
                </td>
                <td>Odourless</td>
                <td>Odourless</td>
                <td>Odourless</td>
                <td>Odourless</td>
                <td>None</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>Taste</bold>
                </td>
                <td>Tasteless</td>
                <td>Tasteless</td>
                <td>Tasteless</td>
                <td>Tasteless</td>
                <td>None</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>Turbidity-NTU</bold>
                </td>
                <td>0.1</td>
                <td>0.87</td>
                <td>0.18</td>
                <td>0.14</td>
                <td>-</td>
                <td>&lt;5</td>
              </tr>
              <tr>
                <td>
                  <bold>Temperature (</bold>
                  <bold>˚C</bold>
                  <bold>)</bold>
                </td>
                <td>27.4</td>
                <td>27.4</td>
                <td>27.4</td>
                <td>27.4</td>
                <td>&lt;25</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>pH</bold>
                </td>
                <td>7.05</td>
                <td>7.01</td>
                <td>7.12</td>
                <td>7.39</td>
                <td>6.5 - 8.5 (*)</td>
                <td>6.5 - 9.5</td>
              </tr>
              <tr>
                <td>
                  <bold>Conductivity at 25</bold>
                  <bold>˚C</bold>
                  <bold>µs/cm</bold>
                </td>
                <td>1598</td>
                <td>1693</td>
                <td>656</td>
                <td>1039</td>
                <td>400 (**)</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>TA</bold>
                  <bold>(</bold>
                  <bold>mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>-</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>TAC</bold>
                  <bold>(mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>225</td>
                <td>275</td>
                <td>140</td>
                <td>240</td>
                <td>-</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>CO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>
                </td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>HCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>274.5</td>
                <td>335.5</td>
                <td>170.8</td>
                <td>292.8</td>
                <td>
                </td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>TH (mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>400</td>
                <td>330</td>
                <td>158</td>
                <td>272</td>
                <td>150 - 500 (*)</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Ca (mg/L)</bold>
                </td>
                <td>140</td>
                <td>96</td>
                <td>55.2</td>
                <td>76</td>
                <td>
                </td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Mg (mg/L)</bold>
                </td>
                <td>12</td>
                <td>21.6</td>
                <td>4.8</td>
                <td>19.68</td>
                <td>
                </td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Na (mg/L)</bold>
                </td>
                <td>170</td>
                <td>224</td>
                <td>80</td>
                <td>126</td>
                <td>≤150 (*)</td>
                <td>≤200</td>
              </tr>
              <tr>
                <td>
                  <bold>K (mg/L)</bold>
                </td>
                <td>32.3</td>
                <td>9.4</td>
                <td>12.6</td>
                <td>17.8</td>
                <td>≤12 (*)</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>Fe (mg/L)</bold>
                </td>
                <td>&lt;0.05</td>
                <td>1.76</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>≤0.2 (*)</td>
                <td>≤0.3</td>
              </tr>
              <tr>
                <td>
                  <bold>Mn (mg/L)</bold>
                </td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>≤0.05 (*)</td>
                <td>0.4</td>
              </tr>
              <tr>
                <td>
                  <bold>Cl (mg/L)</bold>
                </td>
                <td>200</td>
                <td>210.23</td>
                <td>66.1</td>
                <td>130.1</td>
                <td>≤200 (*)</td>
                <td>≤250</td>
              </tr>
              <tr>
                <td>
                  <bold>SO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>120.88</td>
                <td>180</td>
                <td>47.37</td>
                <td>74.56</td>
                <td>≤250 (*)</td>
                <td>≤400</td>
              </tr>
              <tr>
                <td>
                  <bold>PO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mgP/L)</bold>
                </td>
                <td>&lt;0.2</td>
                <td>&lt;0.2</td>
                <td>&lt;0.2</td>
                <td>&lt;0.2</td>
                <td>≤5 (*)</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>F (mg/L)</bold>
                </td>
                <td>&lt;1</td>
                <td>1.25</td>
                <td>&lt;1</td>
                <td>&lt;1</td>
                <td>
                </td>
                <td>1.5</td>
              </tr>
              <tr>
                <td>
                  <bold>KMnO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mgO</bold>
                  <bold>
                    <sub>2</sub>
                  </bold>
                  <bold>/L)</bold>
                </td>
                <td>2</td>
                <td>3</td>
                <td>1.1</td>
                <td>0.6</td>
                <td>&lt;5</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>H</mml:mi>
                          <mml:mn>4</mml:mn>
                          <mml:mo>+</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>(mg/L)</bold>
                </td>
                <td>&lt;0.1</td>
                <td>&lt;0.1</td>
                <td>&lt;0.1</td>
                <td>&lt;0.1</td>
                <td>
                </td>
                <td>≤1.5</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>W</bold>: Well water, (<bold>*</bold>) French Regulations (RF), (<bold>**</bold>) European Union (EU) Directive.</p>
        <p><bold>Table 4</bold><bold>.</bold> Physicochemical parameters of borehole water.</p>
        <table-wrap id="tbl4">
          <label>Table 4</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="7">
                  <bold>Borehole water</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>BH1</bold>
                </td>
                <td>
                  <bold>BH2</bold>
                </td>
                <td>
                  <bold>BH3</bold>
                </td>
                <td>
                  <bold>BH4</bold>
                </td>
                <td>
                  <bold>BH5</bold>
                </td>
                <td>Permissible conc(RF* UE**)</td>
                <td>WHO GUIDELINES</td>
              </tr>
              <tr>
                <td>
                  <bold>Odour</bold>
                </td>
                <td>Odourless</td>
                <td>Odourless</td>
                <td>Odourless</td>
                <td>Odourless</td>
                <td>Odourless</td>
                <td>None</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>Taste</bold>
                </td>
                <td>Tasteless</td>
                <td>Tasteless</td>
                <td>Tasteless</td>
                <td>Tasteless</td>
                <td>Tasteless</td>
                <td>None</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>Turbidity-NTU</bold>
                </td>
                <td>0.22</td>
                <td>0.27</td>
                <td>0.33</td>
                <td>0.24</td>
                <td>0.11</td>
                <td>-</td>
                <td>&lt;5</td>
              </tr>
              <tr>
                <td>
                  <bold>Temperature (</bold>
                  <bold>˚C</bold>
                  <bold>)</bold>
                </td>
                <td>25.3</td>
                <td>25.5</td>
                <td>25.3</td>
                <td>25.2</td>
                <td>25.7</td>
                <td>&lt;25</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>pH</bold>
                </td>
                <td>7.01</td>
                <td>7.64</td>
                <td>7.49</td>
                <td>6.92</td>
                <td>7.36</td>
                <td>6.5 - 8.5 (*)</td>
                <td>6.5 - 9.5</td>
              </tr>
              <tr>
                <td>
                  <bold>Conductivity at 25</bold>
                  <bold>˚C</bold>
                  <bold>µS/cm</bold>
                </td>
                <td>1448</td>
                <td>1231</td>
                <td>1098</td>
                <td>356</td>
                <td>1123</td>
                <td>400 (**)</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>TA (mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>-</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>TAC</bold>
                  <bold>(mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>265</td>
                <td>270</td>
                <td>250</td>
                <td>85</td>
                <td>125</td>
                <td>-</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>CO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>
                </td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>HCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>323.3</td>
                <td>329.4</td>
                <td>305</td>
                <td>103.7</td>
                <td>152.5</td>
                <td>
                </td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>TH (mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>340</td>
                <td>150</td>
                <td>160</td>
                <td>95</td>
                <td>146</td>
                <td>150 - 500 (*)</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Ca (mg/L)</bold>
                </td>
                <td>100</td>
                <td>32</td>
                <td>36</td>
                <td>26.8</td>
                <td>28</td>
                <td>
                </td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Mg (mg/L)</bold>
                </td>
                <td>21.6</td>
                <td>16.8</td>
                <td>16.8</td>
                <td>6.72</td>
                <td>18.2</td>
                <td>
                </td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Na (mg/L)</bold>
                </td>
                <td>204</td>
                <td>192</td>
                <td>156</td>
                <td>28.8</td>
                <td>160</td>
                <td>≤150 (*)</td>
                <td>≤200</td>
              </tr>
              <tr>
                <td>
                  <bold>K (mg/L)</bold>
                </td>
                <td>7.3</td>
                <td>25.3</td>
                <td>25.6</td>
                <td>12.6</td>
                <td>24.4</td>
                <td>≤12 (*)</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>Fe (mg/L)</bold>
                </td>
                <td>0.25</td>
                <td>0.06</td>
                <td>0.12</td>
                <td>0.48</td>
                <td>&lt;0.05</td>
                <td>≤0.2 (*)</td>
                <td>≤0.3</td>
              </tr>
              <tr>
                <td>
                  <bold>Mn (mg/L)</bold>
                </td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>≤0.05 (*)</td>
                <td>0.40</td>
              </tr>
              <tr>
                <td>
                  <bold>Cl (mg/L)</bold>
                </td>
                <td>160.17</td>
                <td>210.26</td>
                <td>200.23</td>
                <td>20</td>
                <td>239.23</td>
                <td>≤200 (*)</td>
                <td>≤250</td>
              </tr>
              <tr>
                <td>
                  <bold>SO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>170</td>
                <td>12.2</td>
                <td>10</td>
                <td>32.63</td>
                <td>29.8</td>
                <td>≤250 (*)</td>
                <td>≤400</td>
              </tr>
              <tr>
                <td>
                  <bold>PO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mgP/L)</bold>
                </td>
                <td>0.44</td>
                <td>&lt;0.2</td>
                <td>&lt;0.2</td>
                <td>&lt;0.2</td>
                <td>&lt;0.2</td>
                <td>≤5 (*)</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <bold>F (mg/L)</bold>
                </td>
                <td>1.01</td>
                <td>1.49</td>
                <td>1.57</td>
                <td>&lt;1</td>
                <td>1.82</td>
                <td>
                </td>
                <td>1.5</td>
              </tr>
              <tr>
                <td>
                  <bold>KMnO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mgO</bold>
                  <bold>
                    <sub>2</sub>
                  </bold>
                  <bold>/L)</bold>
                </td>
                <td>1.7</td>
                <td>0.1</td>
                <td>0.1</td>
                <td>0.6</td>
                <td>0.4</td>
                <td>&lt;5</td>
                <td>-</td>
              </tr>
              <tr>
                <td>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>H</mml:mi>
                          <mml:mn>4</mml:mn>
                          <mml:mo>+</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>(mg/L)</bold>
                </td>
                <td>12</td>
                <td>&lt;0.1</td>
                <td>3.4</td>
                <td>0.27</td>
                <td>&lt;0.1</td>
                <td>
                </td>
                <td>≤1.5</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>BH</bold>: Borehole water, (<bold>*</bold>) French Regulations (RF), (<bold>**</bold>) European Union (EU) Directive.</p>
        <p><bold>Table 5</bold><bold>.</bold> Physicochemical parameters of wastewater.</p>
        <table-wrap id="tbl5">
          <label>Table 5</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="6">
                  <bold>Wastewater and water of the 4</bold>
                  <bold>
                    <sup>th</sup>
                  </bold>
                  <bold>lake</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>WW1</bold>
                </td>
                <td>
                  <bold>WW2</bold>
                </td>
                <td>
                  <bold>WW3</bold>
                </td>
                <td>
                  <bold>WW4</bold>
                </td>
                <td>
                  <bold>WW5</bold>
                  <bold>(4</bold>
                  <bold>
                    <sup>th</sup>
                  </bold>
                  <bold>Lake)</bold>
                </td>
                <td>
                  <bold>Interministerial order: MER/MS/MERF</bold>
                  <bold>No. 010 of 30 March 2015</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Odour</bold>
                </td>
                <td>Odourless</td>
                <td>Yes</td>
                <td>Yes</td>
                <td>Yes</td>
                <td>Yes</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Taste</bold>
                </td>
                <td>Salty</td>
                <td>-</td>
                <td>-</td>
                <td>-</td>
                <td>-</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Turbidity-NTU</bold>
                </td>
                <td>1.15</td>
                <td>1.63</td>
                <td>101.25</td>
                <td>43.7</td>
                <td>1.47</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Colour</bold>
                </td>
                <td>&lt;5</td>
                <td>&gt;100</td>
                <td>&gt;100</td>
                <td>&gt;100</td>
                <td>15</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Temperature (</bold>
                  <bold>˚C</bold>
                  <bold>)</bold>
                </td>
                <td>25.2</td>
                <td>25.5</td>
                <td>25.7</td>
                <td>25.4</td>
                <td>27.5</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>pH</bold>
                </td>
                <td>7.74</td>
                <td>5.08</td>
                <td>7.48</td>
                <td>4.35</td>
                <td>7.99</td>
                <td>5.5 - 9</td>
              </tr>
              <tr>
                <td>
                  <bold>Conductivity at 25</bold>
                  <bold>˚C</bold>
                  <bold>µS/cm</bold>
                </td>
                <td>2660</td>
                <td>2360</td>
                <td>2010</td>
                <td>8590</td>
                <td>1457</td>
                <td>≤2500</td>
              </tr>
              <tr>
                <td>
                  <bold>TA (mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>TAC</bold>
                  <bold>(mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>330</td>
                <td>40</td>
                <td>310</td>
                <td>0</td>
                <td>255</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>CO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>0</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>HCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>402</td>
                <td>48.8</td>
                <td>378.2</td>
                <td>0</td>
                <td>311.1</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>TH (mg/L of CaCO</bold>
                  <bold>
                    <sub>3</sub>
                  </bold>
                  <bold>)</bold>
                </td>
                <td>220</td>
                <td>180</td>
                <td>230</td>
                <td>200</td>
                <td>204</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Ca (mg/L)</bold>
                </td>
                <td>40.4</td>
                <td>45</td>
                <td>48</td>
                <td>40.1</td>
                <td>48</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Mg (mg/L)</bold>
                </td>
                <td>28.4</td>
                <td>21.0</td>
                <td>26.4</td>
                <td>21.15</td>
                <td>20.16</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Na (mg/L)</bold>
                </td>
                <td>377</td>
                <td>375</td>
                <td>302</td>
                <td>3560</td>
                <td>228</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>K (mg/L)</bold>
                </td>
                <td>58.5</td>
                <td>8</td>
                <td>51</td>
                <td>10</td>
                <td>22.6</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Fe (mg/L)</bold>
                </td>
                <td>0</td>
                <td>&lt;0.05</td>
                <td>37.6</td>
                <td>18.46</td>
                <td>&lt;0.05</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Mn (mg/L)</bold>
                </td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>≤1</td>
              </tr>
              <tr>
                <td>
                  <bold>Cl (mg/L)</bold>
                </td>
                <td>540.59</td>
                <td>560.62</td>
                <td>260.28</td>
                <td>700.77</td>
                <td>270.3</td>
                <td>≤1200</td>
              </tr>
              <tr>
                <td>
                  <bold>SO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mg/L)</bold>
                </td>
                <td>20.18</td>
                <td>249.1</td>
                <td>245.6</td>
                <td>245.6</td>
                <td>48.3</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>PO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mgP/L)</bold>
                </td>
                <td>0.25</td>
                <td>2.5</td>
                <td>4.25</td>
                <td>0.63</td>
                <td>0.6</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>F (mg/L)</bold>
                </td>
                <td>1.88</td>
                <td>7.84</td>
                <td>&lt;1</td>
                <td>2.57</td>
                <td>&lt;1</td>
                <td>≤15</td>
              </tr>
              <tr>
                <td>
                  <bold>KMnO</bold>
                  <bold>
                    <sub>4</sub>
                  </bold>
                  <bold>(mgO</bold>
                  <bold>
                    <sub>2</sub>
                  </bold>
                  <bold>/L)</bold>
                </td>
                <td>0.5</td>
                <td>70</td>
                <td>280</td>
                <td>180</td>
                <td>2.8</td>
                <td>
                </td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>WW</bold>: Wastewater.</p>
      </sec>
      <sec id="sec3dot2">
        <title>3.2. Nitrate, Nitrite and Phosphorus Concentrations</title>
        <p>The results recorded in <bold>Table 6</bold> and <bold>Table 7</bold> indicate that in some groundwater samples (W1, W2, W4 and BH1) the nitrate concentration was high compared with the WHO guidelines. The nitrite concentrations were also above the standards in some samples (W1 and BH1). </p>
        <p>Concerning phosphorus, high contents were observed in some groundwater samples (W2 and BH1), compared with the WHO guidelines.</p>
        <p><bold>Table 6</bold><bold>.</bold> Nitrate and nitrite concentrations in well water.</p>
        <table-wrap id="tbl6">
          <label>Table 6</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="4">
                  <bold>Well water</bold>
                </td>
                <td rowspan="2">
                  <bold>Permissible conc</bold>
                  <bold>(RF* UE**)</bold>
                </td>
                <td rowspan="2">
                  <bold>WHO guidelines</bold>
                  <bold>(mg/L)</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>W1</bold>
                </td>
                <td>
                  <bold>W2</bold>
                </td>
                <td>
                  <bold>W3</bold>
                </td>
                <td>
                  <bold>W4</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mn>3</mml:mn>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>(mg</bold>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mn>3</mml:mn>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>/L)</bold>
                </td>
                <td>63</td>
                <td>81.3</td>
                <td>26.2</td>
                <td>144.25</td>
                <td>≤50 (*)</td>
                <td>≤50</td>
              </tr>
              <tr>
                <td>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mtext>2</mml:mtext>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>(mg</bold>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mtext>2</mml:mtext>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>/L)</bold>
                </td>
                <td>3.7</td>
                <td>0.6</td>
                <td>0.18</td>
                <td>0.10</td>
                <td>≤0.1 (*)</td>
                <td>≤3</td>
              </tr>
              <tr>
                <td>
                  <bold>P (mg/L)</bold>
                </td>
                <td>0.49</td>
                <td>1.06</td>
                <td>0.09</td>
                <td>0.06</td>
                <td>-</td>
                <td>1</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p>W: Well water.</p>
        <p><bold>Table 7</bold><bold>.</bold> Nitrate and nitrite concentrations in borehole water.</p>
        <table-wrap id="tbl7">
          <label>Table 7</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="7">
                  <bold>Borehole water</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>BH1</bold>
                </td>
                <td>
                  <bold>BH2</bold>
                </td>
                <td>
                  <bold>BH3</bold>
                </td>
                <td>
                  <bold>BH4</bold>
                </td>
                <td>
                  <bold>BH5</bold>
                </td>
                <td>
                  <bold>Permissible conc</bold>
                  <bold>(RF* UE**)</bold>
                </td>
                <td>
                  <bold>WHO guidelines</bold>
                  <bold>(mg/L)</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mn>3</mml:mn>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>(mg</bold>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mn>3</mml:mn>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>/L)</bold>
                </td>
                <td>103.75</td>
                <td>&lt;0.5</td>
                <td>&lt;0.5</td>
                <td>24.5</td>
                <td>8.86</td>
                <td>≤50 (*)</td>
                <td>
                  <bold>≤50</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mtext>2</mml:mtext>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>(mg</bold>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mtext>2</mml:mtext>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>/L)</bold>
                </td>
                <td>3.24</td>
                <td>&lt;0.02</td>
                <td>&lt;0.025</td>
                <td>0.04</td>
                <td>&lt;0.02</td>
                <td>≤0.1 (*)</td>
                <td>
                  <bold>≤3</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>P (mg/L)</bold>
                </td>
                <td>1.04</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>-</td>
                <td>1</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>BH</bold>: Borehole water.</p>
      </sec>
      <sec id="sec3dot3">
        <title>
          3.3. Determination of Suspended Solids (SS), Five-Day Biochemical Oxygen Demand (BOD
          <sub>5</sub>
          ), Chemical Oxygen Demand (COD) and Nitrate Concentration (
          <inline-formula>
            <mml:math>
              <mml:mrow>
                <mml:mi>N</mml:mi>
                <mml:msubsup>
                  <mml:mi>O</mml:mi>
                  <mml:mn>3</mml:mn>
                  <mml:mo>−</mml:mo>
                </mml:msubsup>
              </mml:mrow>
            </mml:math>
          </inline-formula>
          ) in Wastewater
        </title>
        <p><bold>Table 8</bold><bold>.</bold> SS, BOD<sub>5</sub>, COD, P and <inline-formula><mml:math display="inline"><mml:mrow><mml:mi> N </mml:mi><mml:msubsup><mml:mi> O </mml:mi><mml:mn> 3 </mml:mn><mml:mo> − </mml:mo></mml:msubsup></mml:mrow></mml:math></inline-formula> in wastewater.</p>
        <table-wrap id="tbl8">
          <label>Table 8</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">Parameters analysed</td>
                <td colspan="6">
                  <bold>Wastewater</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>WW1</bold>
                </td>
                <td>
                  <bold>WW2</bold>
                </td>
                <td>
                  <bold>WW3</bold>
                </td>
                <td>
                  <bold>WW4</bold>
                </td>
                <td>
                  <bold>WW5</bold>
                </td>
                <td>
                  <bold>Interministerial order: MER/MS/MERF</bold>
                  <bold>No. 010 of 30 March 2015</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>SS (mg/L)</bold>
                </td>
                <td>17.33</td>
                <td>266.7</td>
                <td>871.25</td>
                <td>734.82</td>
                <td>22.44</td>
                <td>≤50</td>
              </tr>
              <tr>
                <td>
                  <bold>BOD</bold>
                  <bold>
                    <sub>5</sub>
                  </bold>
                  <bold>(mg O</bold>
                  <bold>
                    <sub>2</sub>
                  </bold>
                  <bold>/L)</bold>
                </td>
                <td>8</td>
                <td>235.0</td>
                <td>68</td>
                <td>3410</td>
                <td>30</td>
                <td>≤100</td>
              </tr>
              <tr>
                <td>
                  <bold>COD (mg O</bold>
                  <bold>
                    <sub>2</sub>
                  </bold>
                  <bold>/L)</bold>
                </td>
                <td>67.2</td>
                <td>1400</td>
                <td>340.8</td>
                <td>16,448</td>
                <td>48</td>
                <td>≤300</td>
              </tr>
              <tr>
                <td>
                  <bold>COD/BOD</bold>
                  <bold>
                    <sub>5</sub>
                  </bold>
                </td>
                <td>8.4</td>
                <td>5.96</td>
                <td>5</td>
                <td>4.82</td>
                <td>1.6</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mn>3</mml:mn>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>(mg</bold>
                  <inline-formula>
                    <mml:math>
                      <mml:mrow>
                        <mml:mi>N</mml:mi>
                        <mml:msubsup>
                          <mml:mi>O</mml:mi>
                          <mml:mn>3</mml:mn>
                          <mml:mo>−</mml:mo>
                        </mml:msubsup>
                      </mml:mrow>
                    </mml:math>
                  </inline-formula>
                  <bold>/L)</bold>
                </td>
                <td>&lt;0.5</td>
                <td>&lt;1.4</td>
                <td>86</td>
                <td>&lt;0.5</td>
                <td>&lt;0.5</td>
                <td>≤20</td>
              </tr>
              <tr>
                <td>
                  <bold>P (mg/L)</bold>
                </td>
                <td>&lt;0.29</td>
                <td>&lt;0.05</td>
                <td>7.3</td>
                <td>0.1</td>
                <td>0.42</td>
                <td>≤10</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>WW</bold>: Wastewater.</p>
        <p><bold>Table 8</bold> summarizes the results of the COD and of the BOD<sub>5</sub> for the surface water sampless (wastewater and water of the 4<sup>th</sup> lake) as well as their nitrate concentration and the degree of biodegradability. SS and COD were high in three of the 5 samples (WW2, WW3 and WW4). BOD<sub>5</sub> showed significant values in WW2 and WW4, while the nitrate concentration was high in WW3. The degree of biodegradability was above the thresholds in WW1, WW2, WW3 and WW4.</p>
      </sec>
      <sec id="sec3dot4">
        <title>3.4. Trace Metal Elements</title>
        <p><bold>Table 9</bold> and <bold>Table 10</bold> summarize the values of certain trace metal elements, namely Cadmium (Cd), Lead (Pb), Mercury (Hg) and Arsenic (As), in the groundwater (well water, borehole water).</p>
        <p><bold>Table 9</bold><bold>.</bold> Content of trace metal elements (Cd, Pb, As and Hg) in well water.</p>
        <table-wrap id="tbl9">
          <label>Table 9</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="5">
                  <bold>Well water</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>W1</bold>
                </td>
                <td>
                  <bold>W2</bold>
                </td>
                <td>
                  <bold>W3</bold>
                </td>
                <td>
                  <bold>W4</bold>
                </td>
                <td>
                  <bold>WHO guidelines in 2006 (</bold>
                  <bold>µg</bold>
                  <bold>/L)</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Cd (µg/L)</bold>
                </td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>3</td>
              </tr>
              <tr>
                <td>
                  <bold>Pb (µg/L)</bold>
                </td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>10</td>
              </tr>
              <tr>
                <td>
                  <bold>As (µg/L)</bold>
                </td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>10</td>
              </tr>
              <tr>
                <td>
                  <bold>Hg (µg/L)</bold>
                </td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>6</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>W</bold>: Well water.</p>
        <p><bold>Table 10</bold><bold>.</bold> Content of trace metal elements (Cd, Pb, As and Hg) in borehole water.</p>
        <table-wrap id="tbl10">
          <label>Table 10</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters</bold>
                  <bold>analysed</bold>
                </td>
                <td colspan="6">
                  <bold>Borehole water</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>BH1</bold>
                </td>
                <td>
                  <bold>BH2</bold>
                </td>
                <td>
                  <bold>BH3</bold>
                </td>
                <td>
                  <bold>BH4</bold>
                </td>
                <td>
                  <bold>BH5</bold>
                </td>
                <td>
                  <bold>WHO guidelines 2006 (</bold>
                  <bold>µg</bold>
                  <bold>/L)</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Cd (µg/L)</bold>
                </td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>3</td>
              </tr>
              <tr>
                <td>
                  <bold>Pb (µg/L)</bold>
                </td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>10</td>
              </tr>
              <tr>
                <td>
                  <bold>As (µg/L)</bold>
                </td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>10</td>
              </tr>
              <tr>
                <td>
                  <bold>Hg (µg/L)</bold>
                </td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>6</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>BH</bold>: Borehole water.</p>
        <p><bold>Table 11</bold><bold>.</bold>Heavy metal content (Cd, Pb, As and Hg) of wastewater.</p>
        <table-wrap id="tbl11">
          <label>Table 11</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters</bold>
                  <bold>analysed</bold>
                </td>
                <td colspan="6">
                  <bold>Wastewater</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>WW1</bold>
                </td>
                <td>
                  <bold>WW2</bold>
                </td>
                <td>
                  <bold>WW3</bold>
                </td>
                <td>
                  <bold>WW4</bold>
                </td>
                <td>
                  <bold>WW5</bold>
                  <bold>(4</bold>
                  <bold>
                    <sup>th</sup>
                  </bold>
                  <bold>Lake)</bold>
                </td>
                <td>
                  <bold>Interministerial order: MER/MS/MERF</bold>
                  <bold>No. 010 of 30 March 2015 (</bold>
                  <bold>µg</bold>
                  <bold>/L)</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Cd (µg/L)</bold>
                </td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>&lt;2.8</td>
                <td>≤200</td>
              </tr>
              <tr>
                <td>
                  <bold>Pb (µg/L)</bold>
                </td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>&lt;10</td>
                <td>≤500</td>
              </tr>
              <tr>
                <td>
                  <bold>As (µg/L)</bold>
                </td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>&lt;0.05</td>
                <td>65</td>
                <td>&lt;0.05</td>
                <td>≤10</td>
              </tr>
              <tr>
                <td>
                  <bold>Hg (µg/L)</bold>
                </td>
                <td>&lt;0.15</td>
                <td>&lt;0.15</td>
                <td>0.15</td>
                <td>15.0</td>
                <td>&lt;0.15</td>
                <td>≤50</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>WW</bold>: Wastewater.</p>
        <p><bold>Table 11</bold>, for its part, indicates the content of trace metal elements in the surface water (wastewater and water of the 4<sup>th</sup> lake). For sample WW4, the As and Hg contents were detected at particularly high concentrations. Likewise, sample WW3 showed a high Hg concentration.</p>
        <p><bold>Tables 12</bold><bold>-</bold><bold>14</bold> record the values of the content of trace metal elements such as Zn, Cu and Ni detected in the various samples of well water, borehole water, wastewater and water of the 4<sup>th</sup> lake. </p>
        <p>In the groundwater (well water, borehole water), the contents found are below the detection threshold. In wastewater, Zn content is high in the sample 3 (WW3).</p>
        <p><bold>Table 12</bold><bold>.</bold>Content of trace metal elements in well water.</p>
        <table-wrap id="tbl12">
          <label>Table 12</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="5">
                  <bold>Well water</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>W1</bold>
                </td>
                <td>
                  <bold>W2</bold>
                </td>
                <td>
                  <bold>W3</bold>
                </td>
                <td>
                  <bold>W4</bold>
                </td>
                <td>
                  <bold>WHO guidelines in 2006 (mg/L)</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Zn (mg/L)</bold>
                </td>
                <td>&lt;0.0033</td>
                <td>&lt;0.0033</td>
                <td>&lt;0.0033</td>
                <td>&lt;0.0033</td>
                <td>3</td>
              </tr>
              <tr>
                <td>
                  <bold>Cu (mg/L)</bold>
                </td>
                <td>&lt;0.004</td>
                <td>&lt;0.004</td>
                <td>&lt;0.004</td>
                <td>&lt;0.004</td>
                <td>2.0</td>
              </tr>
              <tr>
                <td>
                  <bold>Ni (mg/L)</bold>
                </td>
                <td>&lt;0.0054</td>
                <td>&lt;0.0054</td>
                <td>&lt;0.0054</td>
                <td>&lt;0.0054</td>
                <td>0.07</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>W</bold>: Well water.</p>
        <p><bold>Table 13</bold><bold>.</bold> Content of trace metal elements in borehole water.</p>
        <table-wrap id="tbl13">
          <label>Table 13</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="6">
                  <bold>Borehole water</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>BH1</bold>
                </td>
                <td>
                  <bold>BH2</bold>
                </td>
                <td>
                  <bold>BH3</bold>
                </td>
                <td>
                  <bold>BH4</bold>
                </td>
                <td>
                  <bold>BH5</bold>
                </td>
                <td>
                  <bold>WHO guidelines (mg/L) 2006</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Zn (mg/L)</bold>
                </td>
                <td>&lt;0.0033</td>
                <td>&lt;0.0033</td>
                <td>&lt;0.035</td>
                <td>&lt;0.0033</td>
                <td>&lt;0.0033</td>
                <td>3</td>
              </tr>
              <tr>
                <td>
                  <bold>Cu (mg/L)</bold>
                </td>
                <td>&lt;0.004</td>
                <td>&lt;0.004</td>
                <td>&lt;0.004</td>
                <td>&lt;0/004</td>
                <td>&lt;0.004</td>
                <td>2</td>
              </tr>
              <tr>
                <td>
                  <bold>Ni (mg/L)</bold>
                </td>
                <td>&lt;0.0054</td>
                <td>&lt;0.0054</td>
                <td>&lt;0.0054</td>
                <td>&lt;0.0054</td>
                <td>&lt;0.0054</td>
                <td>0.07</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>BH</bold>: Borehole water.</p>
        <p><bold>Table 14</bold><bold>.</bold> Content of trace metal elements in wastewater.</p>
        <table-wrap id="tbl14">
          <label>Table 14</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters</bold>
                  <bold>analysed</bold>
                </td>
                <td colspan="6">
                  <bold>Wastewater and 4</bold>
                  <bold>
                    <sup>th</sup>
                  </bold>
                  <bold>Lake</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>WW1</bold>
                </td>
                <td>
                  <bold>WW2</bold>
                </td>
                <td>
                  <bold>WW3</bold>
                </td>
                <td>
                  <bold>WW4</bold>
                </td>
                <td>
                  <bold>WW5 (4</bold>
                  <bold>
                    <sup>th</sup>
                  </bold>
                  <bold>Lake)</bold>
                </td>
                <td>
                  <bold>Interministerial order: MER/MS/MERF</bold>
                  <bold>No. 010 of 30 March 2015</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>Zn (mg/L)</bold>
                </td>
                <td>&lt;0.0033</td>
                <td>0.0033</td>
                <td>3.20</td>
                <td>1.45</td>
                <td>&lt;0.035</td>
                <td>≤2</td>
              </tr>
              <tr>
                <td>
                  <bold>Cu (mg/L)</bold>
                </td>
                <td>&lt;0.004</td>
                <td>&lt;0.004</td>
                <td>&lt;0.25</td>
                <td>&lt;0.004</td>
                <td>&lt;0.004</td>
                <td>≤0.5</td>
              </tr>
              <tr>
                <td>
                  <bold>Ni (mg/L)</bold>
                </td>
                <td>&lt;0.0054</td>
                <td>&lt;0.0054</td>
                <td>&lt;0.07</td>
                <td>&lt;0.12</td>
                <td>&lt;0.0054</td>
                <td>≤0.5</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>WW</bold>: Wastewater.</p>
      </sec>
      <sec id="sec3dot5">
        <title>3.5. Microbiological Data</title>
        <p><bold>Table 15</bold> and <bold>Table 16</bold> present the microbiological parameters of the groundwater (well water and borehole water). Heterotrophic Plate Count (HPC) and thermotolerant coliforms (TC) were detected in the well water and borehole water samples. The well samples showed high loads HPC bacteria and TC. The borehole samples also showed high values in the majority of cases.</p>
        <p><bold>Table 17</bold>, for its part, presents the results of the microbiological parameters in the surface water (wastewater and water of the 4<sup>th</sup> lake). Samples WW2, WW3, WW4 and WW5 showed high TC concentrations. Likewise, the enterococci (ENT) concentration was high for samples WW2, WW3 and WW4. Clostridium (Clost) were detected in the surface water samples. In contrast, salmonella (Salm) was detected only in WW2, WW3 and WW5.</p>
        <p><bold>Table 15</bold><bold>.</bold> Essential microbiological parameters of well water.</p>
        <table-wrap id="tbl15">
          <label>Table 15</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="4">
                  <bold>Well water</bold>
                </td>
                <td rowspan="2">
                  <bold>WHO guidelines</bold>
                  <bold>(CFU</bold>
                  /
                  <bold>mL) 2006</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>W1</bold>
                </td>
                <td>
                  <bold>W2</bold>
                </td>
                <td>
                  <bold>W3</bold>
                </td>
                <td>
                  <bold>W4</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>HPC at 37</bold>
                  <bold>˚</bold>
                  <bold>CFU/mL</bold>
                </td>
                <td>&gt;3000</td>
                <td>&gt;2600</td>
                <td>&gt;3000</td>
                <td>&gt;3000</td>
                <td>≤10</td>
              </tr>
              <tr>
                <td>
                  <bold>TC CFU/100 mL</bold>
                </td>
                <td>&gt;1500</td>
                <td>&gt;1500</td>
                <td>&gt;1500</td>
                <td>&gt;1500</td>
                <td>&lt;1</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>W</bold>: Well water, <bold>HPC</bold>: Heterotrophic Plate Count, <bold>TC</bold>: Thermotolerant coliforms.</p>
        <p><bold>Table 16</bold><bold>.</bold> Essential microbiological parameters of borehole water.</p>
        <table-wrap id="tbl16">
          <label>Table 16</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>Parameters analysed</bold>
                </td>
                <td colspan="6">
                  <bold>Borehole water</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>BH1</bold>
                </td>
                <td>
                  <bold>BH2</bold>
                </td>
                <td>
                  <bold>BH3</bold>
                </td>
                <td>
                  <bold>BH4</bold>
                </td>
                <td>
                  <bold>BH5</bold>
                </td>
                <td>
                  <bold>WHO guidelines</bold>
                  <bold>(CFU</bold>
                  <bold>/</bold>
                  <bold>mL) 2006</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>HPC at 37</bold>
                  <bold>˚</bold>
                  <bold>CFU/mL</bold>
                </td>
                <td>68</td>
                <td>20</td>
                <td>5900</td>
                <td>830</td>
                <td>150</td>
                <td>≤10</td>
              </tr>
              <tr>
                <td>
                  <bold>TC CFU/100 mL</bold>
                </td>
                <td>30</td>
                <td>&lt;1</td>
                <td>1600</td>
                <td>90</td>
                <td>180</td>
                <td>&lt;1</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p>BH: Borehole water HPC: Heterotrophic Plate Count, TC: Thermotolerant coliforms.</p>
        <p><bold>Table 17</bold><bold>.</bold> Essential microbiological parameters of surface water (wastewater and water of the 4<sup>th</sup> lake).</p>
        <table-wrap id="tbl17">
          <label>Table 17</label>
          <table>
            <tbody>
              <tr>
                <td rowspan="2">
                  <bold>PARAMETERS</bold>
                  <bold>ANALYSED</bold>
                </td>
                <td colspan="6">
                  <bold>Wastewater</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>WW1</bold>
                </td>
                <td>
                  <bold>WW2</bold>
                </td>
                <td>
                  <bold>WW3</bold>
                </td>
                <td>
                  <bold>WW4</bold>
                </td>
                <td>
                  <bold>WW5</bold>
                  <bold>(4</bold>
                  <bold>
                    <sup>th</sup>
                  </bold>
                  <bold>Lake)</bold>
                </td>
                <td>
                  <bold>Interministerial order: MER/MS/MERF</bold>
                  <bold>No. 010 of 30 March 2015</bold>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>TC CFU/100</bold>
                  <bold>mL</bold>
                </td>
                <td>70</td>
                <td>&gt;9000</td>
                <td>&gt;15,000</td>
                <td>&gt;15,000</td>
                <td>3500</td>
                <td>≤2000</td>
              </tr>
              <tr>
                <td>
                  <bold>ENT MPN/100 mL</bold>
                </td>
                <td>&lt;0.5</td>
                <td>230,000</td>
                <td>5,600,000</td>
                <td>56,000</td>
                <td>43</td>
                <td>≤1000</td>
              </tr>
              <tr>
                <td>
                  <bold>Clost</bold>
                  <bold>CFU/100</bold>
                  <bold>mL</bold>
                </td>
                <td>210</td>
                <td>700</td>
                <td>15,000</td>
                <td>18</td>
                <td>1000</td>
                <td>
                </td>
              </tr>
              <tr>
                <td>
                  <bold>SALM in 100</bold>
                  <bold>mL</bold>
                </td>
                <td>Not detected</td>
                <td>Detected</td>
                <td>Detected</td>
                <td>Not detected</td>
                <td>Detected</td>
                <td>
                </td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p><bold>WW</bold>: Wastewater, <bold>CT</bold>: Thermotolerant coliforms at 44˚C; <bold>ENT</bold>: Enterococci; <bold>Clost</bold>: Clostridium, <bold>SALM</bold>: Salmonella spp.</p>
      </sec>
      <sec id="sec3dot6">
        <title>3.6. Bioassay Data</title>
        <fig id="fig2">
          <label>Figure 2</label>
          <graphic xlink:href="https://html.scirp.org/file/6705772-rId40.jpeg?20260918095041" />
        </fig>
        <p><bold>Figure 2</bold><bold>.</bold> Mortality rate of the larvae of <italic>Artemia salina</italic>in well water.</p>
        <p><xref ref-type="fig" rid="fig2">Figures 2-4</xref> represent the mortality rates of the larvae of <italic>Artemia salina</italic>in the various water samples. The mortality rate was high in W1, W2, W3, W4 and W5. </p>
        <fig id="fig3">
          <label>Figure 3</label>
          <graphic xlink:href="https://html.scirp.org/file/6705772-rId41.jpeg?20260918095041" />
        </fig>
        <p><bold>Figure 3</bold><bold>.</bold> Mortality rate of the larvae of <italic>Artemia salina</italic>in borehole water.</p>
        <fig id="fig4">
          <label>Figure 4</label>
          <graphic xlink:href="https://html.scirp.org/file/6705772-rId42.jpeg?20260918095041" />
        </fig>
        <p><bold>Figure 4</bold><bold>.</bold> Mortality rate of the larvae of <italic>Artemia salina</italic>in wastewater and of the 4<sup>th</sup> lake.</p>
      </sec>
    </sec>
    <sec id="sec4">
      <title>4. Discussion</title>
      <p>Water quality is influenced by various factors, in particular anthropogenic activities [<xref ref-type="bibr" rid="B14">14</xref>], and can be assessed through physicochemical and microbiological parameters. Among these parameters, mention may be made of physicochemical parameters such as turbidity, temperature, conductivity, pH, the concentration of mineral elements (ammonium ion, calcium, magnesium, chloride, sodium, nitrates) [<xref ref-type="bibr" rid="B10">10</xref>] or organoleptic characteristics such as taste and odour [<xref ref-type="bibr" rid="B1">1</xref>]. </p>
      <p>Turbidity is a parameter that makes it possible to measure the cloudiness of water. It is due to suspended particles such as sediments, organic matter and microorganisms [<xref ref-type="bibr" rid="B15">15</xref>]. A high turbidity reflects potential pollution, the suspended particles being able to constitute vectors of heavy metals and microorganisms. The results of this study on the groundwater samples (well water, borehole water) made it possible to record a turbidity below the limits recommended by the WHO (≤5 NTU) [<xref ref-type="bibr" rid="B15">15</xref>]. This result is similar to that of Ouéda <italic>et al</italic>. [<xref ref-type="bibr" rid="B10">10</xref>] who detected a turbidity complying with the WHO standards in the water samples of the Didaourè agglomeration (Tchaoudjo 1). In contrast, our results differ from those of Tampo <italic>et al</italic>. [<xref ref-type="bibr" rid="B16">16</xref>], who recorded a turbidity above the standard in well water during their work in Démakpoé and Agbalépédogan (Lomé) [<xref ref-type="bibr" rid="B16">16</xref>]. In contrast, in the surface water (wastewater 3 and 4), turbidity was high, indicating possible pollution of these waters. The high turbidity observed in these samples would therefore be linked to the presence of insoluble solid particles in suspension. This result as regards wastewater is similar to those of Ayah <italic>et al</italic>. [<xref ref-type="bibr" rid="B3">3</xref>] who recorded a high turbidity (35 NTU) during a study on the lagoon system of Lomé [<xref ref-type="bibr" rid="B3">3</xref>]. </p>
      <p>The SS values of these two samples were also high, far exceeding the regulatory value set by interministerial order MER/MS/MERF No. 010 of 30 March 2015 (≤50 mg/L) [<xref ref-type="bibr" rid="B17">17</xref>]. This result is also similar to those of Ayah <italic>et al</italic>. [<xref ref-type="bibr" rid="B3">3</xref>] who indicated an SS of 77 mg/L in the lagoon system of Lomé [<xref ref-type="bibr" rid="B3">3</xref>].</p>
      <p>According to the WHO, water temperature should not exceed 25˚C. In this study, some well waters and one wastewater sample exceeded this limit, which could favour microbial proliferation. Indeed, a high water temperature would favour the proliferation of bacteria [<xref ref-type="bibr" rid="B18">18</xref>]. This result is similar to those of Ouéda <italic>et al</italic>. [<xref ref-type="bibr" rid="B10">10</xref>] who, during their work in the Tchaoudjo 1 area, recorded an average water temperature of 26.17˚C, therefore above the WHO standard. Likewise, the work of Fambi <italic>et al</italic>. [<xref ref-type="bibr" rid="B19">19</xref>] in Togo, like that of Dégbey <italic>et al</italic>. [<xref ref-type="bibr" rid="B20">20</xref>] in Benin, also recorded temperatures above the WHO standards.</p>
      <p>As regards pH, a physicochemical parameter which provides information on the acidity or the basicity of an aqueous solution, drinking water, according to the WHO, has an optimum pH between 6.5 - 9.5 [<xref ref-type="bibr" rid="B21">21</xref>][<xref ref-type="bibr" rid="B22">22</xref>]. The various well water and borehole water samples had a pH complying with the WHO standards. Our results are similar to those of Ouéda <italic>et al</italic>. [<xref ref-type="bibr" rid="B10">10</xref>] who during their work recorded pH values complying with the WHO standards. However, our results differ from those of Fambi <italic>et al</italic>. [<xref ref-type="bibr" rid="B19">19</xref>] who noted, during a study in 2021 on the borehole water of Légbassito and Vakpossito, two localities in the south of Togo, that 70 % of the waters had an acidic pH. These pH values were between 4.94 and 5.9 [<xref ref-type="bibr" rid="B19">19</xref>]. As regards wastewater, one sample had a pH not complying with the standard defined by interministerial order MER/MS/MERF No. 010 of 30 March 2015. Indeed, according to this order, the pH of wastewater should lie between 5.5 - 9 [<xref ref-type="bibr" rid="B17">17</xref>]. Wastewater sample 4 (WW4), which shows an acidic pH (4.35), and wastewater sample 2 (WW2) do not comply with the national regulations on wastewater. Thus, apart from wastewater sample 4 and, to a lesser extent, wastewater sample 2, the results of our study are similar to those obtained in Morocco by Boutayeb <italic>et al</italic>. [<xref ref-type="bibr" rid="B23">23</xref>], who recorded pH values between 7.05 and 8.2 for various wastewater samples.</p>
      <p>Conductivity, which reflects the mineralization of water, expresses its capacity to carry the electric current. It was high both in the groundwater (well and borehole water) and in the surface water (wastewater and water of the 4<sup>th</sup> lake). This result is different from that of Gnazou <italic>et al</italic>. [<xref ref-type="bibr" rid="B24">24</xref>] who obtained a conductivity ranging from 70.5 µS/cm to 1756 µS/cm<bold>.</bold> In contrast, our result is similar to that of Talhaoui <italic>et al</italic>. [<xref ref-type="bibr" rid="B25">25</xref>] who recorded conductivities, with a maximum of 2240 µS/cm during their work in Morocco. According to the European Union (EU) standards, conductivity should be less than or equal to 2500 µS/cm, but permissible value is 400 µS/cm for drinking water. A high conductivity would indicate natural pollution (erosion of rocks) or anthropogenic pollution (agriculture, industries or domestic discharges) [<xref ref-type="bibr" rid="B15">15</xref>].</p>
      <p>Our study also revealed, in some well water samples (W1, W2 and W4), borehole water samples (BH1) and wastewater samples (WW3), the presence of nitrogen compounds such as nitrates at concentrations above the EU and WHO standards. As regards well water, our results are similar to those of Gnazou <italic>et al</italic>. [<xref ref-type="bibr" rid="B24">24</xref>] who had also recorded high nitrate concentrations in well water in the Zio area. Likewise, the work of Ouéda <italic>et al</italic>. [<xref ref-type="bibr" rid="B10">10</xref>], indicated that 66.67% of the water samples studied in the Didaourè agglomeration had a nitrate concentration above the WHO standards. Ahoudi <italic>et al</italic>. [<xref ref-type="bibr" rid="B22">22</xref>] during their work in the Agoè Zongo area, also recorded high nitrate contents in the various water samples. High nitrate concentrations reflect contamination linked to the leaching of agricultural soils or to urban and industrial discharges. </p>
      <p>The ammonium ion, another nitrogen compound, was present at a high concentration in borehole sample 1 (BH1). This result associated to nitrite and nitrate high level in BHI, indicate a possible punctual source of contamination, mainly a possible domestic contamination (human discharges) [<xref ref-type="bibr" rid="B10">10</xref>]. This result is similar to that of Ouéda <italic>et al</italic>. [<xref ref-type="bibr" rid="B10">10</xref>], who recorded a high level of ammonium ion in one of their water samples.</p>
      <p>The COD of some wastewater samples (WW2, WW4) was high compared with the standard set by interministerial order MER/MS/MERF No. 010 of 30 March 2015 [<xref ref-type="bibr" rid="B17">17</xref>]. These results reveal a heavy contamination by refractory pollutants of organic and mineral origin [<xref ref-type="bibr" rid="B23">23</xref>]. Indeed, the chemical oxygen demand provides information on possible organic pollution of water [<xref ref-type="bibr" rid="B26">26</xref>]. Our results are similar to those of Sema <italic>et al</italic>. [<xref ref-type="bibr" rid="B27">27</xref>] who, during their work in Kara, also recorded high COD values. However, these COD values were high only in the mornings, owing to the discharge of wastewater by the industries [<xref ref-type="bibr" rid="B27">27</xref>].</p>
      <p>As for the biochemical oxygen demand over 5 days (BOD<sub>5</sub>), its value in the wastewater samples (WW2 and WW4) did not comply with the standards in force in Togo. Moreover, the biodegradability index of the wastewater (WW1-WW4) was above 3, thus confirming the presence of non-biodegradable refractory pollutants [<xref ref-type="bibr" rid="B28">28</xref>]. Indeed, the biodegradability index makes it possible to assess the biodegradability of organic matter [<xref ref-type="bibr" rid="B28">28</xref>] while giving indications on the origin of the pollution [<xref ref-type="bibr" rid="B29">29</xref>].</p>
      <p>Finally, as regards the concentrations of trace metal elements, the contents found in well water and borehole water were generally in compliance with the WHO Guidelines in 2006. In contrast, in some wastewater samples, the content of trace metal elements such as As did not comply with the Togolese regulations in this field. These results are similar to those of Kpiagou <italic>et al</italic>. [<xref ref-type="bibr" rid="B30">30</xref>] who had also detected high levels of As in the water resources of the Didagou catchment. These results underline the need for an appropriate treatment of wastewater. Indeed, trace metal elements are non-biodegradable toxic pollutants which accumulate in the environment with negative impacts on health [<xref ref-type="bibr" rid="B31">31</xref>].</p>
      <p>Most of the wastewater also had an odour, testifying to the alteration of the organoleptic characteristics.</p>
      <p>Biological assessment, in particular microbiological analysis, constitutes another component of the study of water quality. </p>
      <p>In the groundwater and surface water samples, the presence of heterotrophic bacteria at values clearly above the WHO guidelines would indicate a contamination of the water following exposure to overall pollution. </p>
      <p>Thermotolerant coliforms (TC) were also found in the groundwater samples at abnormal values, indicating suspected faecal contamination [<xref ref-type="bibr" rid="B7">7</xref>]. The heterotrophic plate count and TC values in well water are clearly higher than those found in borehole water (except those of BH2). This difference would be linked to the fact that boreholes are generally deeper and less exposed than wells [<xref ref-type="bibr" rid="B11">11</xref>]. The results obtained in this study as regards HPC bacteria and TC in well water and borehole water are similar to those of previous work carried out in Adakpamé [<xref ref-type="bibr" rid="B11">11</xref>] and Lomé [<xref ref-type="bibr" rid="B7">7</xref>]. This work indeed also recorded the presence of HPC bacteria and faecal coliforms in well water and borehole water. As regards wastewater, only one sample showed TC and enterococci values below the national standards. </p>
      <p>Salmonella and clostridia were also found in most of the wastewater. These pathogenic bacteria are indeed often found in wastewater [<xref ref-type="bibr" rid="B32">32</xref>].</p>
      <p>Just like the physicochemical and microbiological analyses, bioassays also make it possible to assess water pollution [<xref ref-type="bibr" rid="B13">13</xref>]. The bioassay with the larvae of <italic>Artemia salina</italic> indeed makes it possible to obtain indications on possible toxicity and on the ecological quality of the water. The high mortality rates observed in the majority of the wastewater and in one well sample can reveal probable toxicity. </p>
      <p>The larvae of <italic>A salina</italic>therefore made it possible to obtain indications on the toxicity of the various water samples of the port zone, by serving as bioassay material.</p>
    </sec>
    <sec id="sec5">
      <title>5. Conclusion</title>
      <p>The physicochemical analysis highlighted several anomalies, particularly in the wastewater. From the microbiological point of view, the well water, borehole water and wastewater were contaminated by heterotrophic bacteria and by pathogenic germs. To this is added the high mortality observed during the bioassay on the larvae of <italic>Artemia salina</italic>, particularly in the wastewater. These results reflect a probable pollution of the waters in the port zone of Lomé. Further researches must be conducted to determine rather contaminations are due to Lomé’s port activities or not.</p>
    </sec>
  </body>
  <back>
    <ref-list>
      <title>References</title>
      <ref id="B1">
        <label>1.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Kouame, P.N., Gbagbo, G.A.T., Yapi, E.A.M., <italic>et al</italic>. (2024) Household Perception of the Quality of Tap Water in the Adjouffou, Gonzagueville and Anani Neighbourhoods in the Municipality of Port-Bouët in Côte d’Ivoire. <italic>International Journal of Biological and Chemical Sciences</italic>, 18, 289‑302. (In French)</mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Kouame, P.N.</string-name>
              <string-name>Gbagbo, G.A.T.</string-name>
              <string-name>Yapi, E.A.M.</string-name>
              <string-name>Adjouffou, G</string-name>
            </person-group>
            <year>2024</year>
            <article-title>Household Perception of the Quality of Tap Water in the Adjouffou, Gonzagueville and Anani Neighbourhoods in the Municipality of Port-Bouët in Côte d’Ivoire</article-title>
            <source>International Journal of Biological and Chemical Sciences</source>
            <volume>18</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B2">
        <label>2.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Diaby, V., Koffi, N., Valéry, P., Kamou, K., <italic>et al</italic>. (2025) Health Survey of the Quality of Well Water in the New Neighbourhoods of San-Pedro in Côte d’Ivoire: The Case of the Digboué Neighbourhood. <italic>Journal of Chemical</italic>, <italic>Biological and Physical Science</italic>, 16, 93-103. (In French)</mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Diaby, V.</string-name>
              <string-name>Koffi, N.</string-name>
              <string-name>Kamou, K.</string-name>
              <string-name>Chemical, B</string-name>
            </person-group>
            <year>2025</year>
            <article-title>Health Survey of the Quality of Well Water in the New Neighbourhoods of San-Pedro in Côte d’Ivoire: The Case of the Digboué Neighbourhood</article-title>
            <source>Journal of Chemical</source>
            <volume>16</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B3">
        <label>3.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Ayah, M., Grybos, M., Tampo, L., Bawa, L.M., Bril, H. and Djaneye-Boundjou, G. (2015) Water Quality and Pollution of a Tropical Coastal Hydrosystem: The Case of the Lagoon System of Lomé, TOGO. <italic>European Scientific Journal</italic>, 11, 95-119. (In French)</mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Ayah, M.</string-name>
              <string-name>Grybos, M.</string-name>
              <string-name>Tampo, L.</string-name>
              <string-name>Bawa, L.M.</string-name>
              <string-name>Bril, H.</string-name>
              <string-name>Djaneye-Boundjou, G.</string-name>
            </person-group>
            <year>2015</year>
            <article-title>Water Quality and Pollution of a Tropical Coastal Hydrosystem: The Case of the Lagoon System of Lomé, TOGO</article-title>
            <source>European Scientific Journal</source>
            <volume>11</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B4">
        <label>4.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Toi Bissang, B., Aragón-Barroso, A.J., Baba, G., González-López, J. and Osorio, F. (2024) Integrated Assessment of Heavy Metal Pollution and Human Health Risks in Waters from a Former Iron Mining Site: A Case Study of the Canton of Bangeli, Togo. <italic>Water</italic>, 16, Article 471. https://doi.org/10.3390/w16030471 <pub-id pub-id-type="doi">10.3390/w16030471</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3390/w16030471">https://doi.org/10.3390/w16030471</ext-link></mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Bissang, B.</string-name>
              <string-name>Barroso, A.J.</string-name>
              <string-name>Baba, G.</string-name>
              <string-name>Osorio, F.</string-name>
              <string-name>Bangeli, T</string-name>
            </person-group>
            <year>2024</year>
            <article-title>Integrated Assessment of Heavy Metal Pollution and Human Health Risks in Waters from a Former Iron Mining Site: A Case Study of the Canton of Bangeli, Togo</article-title>
            <source>Water</source>
            <volume>16</volume>
            <elocation-id>471</elocation-id>
            <pub-id pub-id-type="doi">10.3390/w16030471</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B5">
        <label>5.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Roberts, T., Williams, I., Preston, J., Clarke, N., Odum, M. and O’Gorman, S. (2023) Ports in a Storm: Port-City Environmental Challenges and Solutions. <italic>Sustainability</italic>, 15, Article 9722. https://doi.org/10.3390/su15129722 <pub-id pub-id-type="doi">10.3390/su15129722</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3390/su15129722">https://doi.org/10.3390/su15129722</ext-link></mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Roberts, T.</string-name>
              <string-name>Williams, I.</string-name>
              <string-name>Preston, J.</string-name>
              <string-name>Clarke, N.</string-name>
              <string-name>Odum, M.</string-name>
              <string-name>Gorman, S.</string-name>
            </person-group>
            <year>2023</year>
            <article-title>Ports in a Storm: Port-City Environmental Challenges and Solutions</article-title>
            <source>Sustainability</source>
            <volume>15</volume>
            <elocation-id>9722</elocation-id>
            <pub-id pub-id-type="doi">10.3390/su15129722</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B6">
        <label>6.</label>
        <citation-alternatives>
          <mixed-citation publication-type="thesis">Agbemadon, A.K. (2024) Development of Ports and Dynamics of Port Cities on the West African Coast: The Case of the Port and the City of Lomé in Togo. Doctoral Dissertation, Université Panthéon-Sorbonne-Paris I. (In French)</mixed-citation>
          <element-citation publication-type="thesis">
            <person-group person-group-type="author">
              <string-name>Agbemadon, A.K.</string-name>
              <string-name>Dissertation, U</string-name>
            </person-group>
            <year>2024</year>
            <article-title>Development of Ports and Dynamics of Port Cities on the West African Coast: The Case of the Port and the City of Lomé in Togo</article-title>
            <source>Doctoral Dissertation</source>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B7">
        <label>7.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Soncy, K., Djeri, B., Anani, K., Eklou-Lawson, M., Adjrah, Y., Karou, D., <italic>et al</italic>. (2015) Assessment of the Bacteriological Quality of Well Water and Borehole Water in Lomé, Togo. <italic>Journal</italic><italic>of</italic><italic>Applied</italic><italic>Biosciences</italic>, 91, Article 8464. (In French) https://doi.org/10.4314/jab.v91i1.6 <pub-id pub-id-type="doi">10.4314/jab.v91i1.6</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.4314/jab.v91i1.6">https://doi.org/10.4314/jab.v91i1.6</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Soncy, K.</string-name>
              <string-name>Djeri, B.</string-name>
              <string-name>Anani, K.</string-name>
              <string-name>Eklou-Lawson, M.</string-name>
              <string-name>Adjrah, Y.</string-name>
              <string-name>Karou, D.</string-name>
            </person-group>
            <year>2015</year>
            <article-title>Assessment of the Bacteriological Quality of Well Water and Borehole Water in Lomé, Togo</article-title>
            <source>Journal of Applied Biosciences</source>
            <volume>91</volume>
            <elocation-id>8464</elocation-id>
            <pub-id pub-id-type="doi">10.4314/jab.v91i1.6</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B8">
        <label>8.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Fuller, R., Landrigan, P.J., Balakrishnan, K., Bathan, G., Bose-O’Reilly, S., Brauer, M., <italic>et al</italic>. (2022) Pollution and Health: A Progress Update. <italic>The Lancet Planetary Health</italic>, 6, e535-e547. https://doi.org/10.1016/s2542-5196(22)00090-0 <pub-id pub-id-type="doi">10.1016/s2542-5196(22)00090-0</pub-id><pub-id pub-id-type="pmid">35594895</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1016/s2542-5196(22)00090-0">https://doi.org/10.1016/s2542-5196(22)00090-0</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Fuller, R.</string-name>
              <string-name>Landrigan, P.J.</string-name>
              <string-name>Balakrishnan, K.</string-name>
              <string-name>Bathan, G.</string-name>
              <string-name>Reilly, S.</string-name>
              <string-name>Brauer, M.</string-name>
            </person-group>
            <year>2022</year>
            <article-title>Pollution and Health: A Progress Update</article-title>
            <source>The Lancet Planetary Health</source>
            <volume>5196</volume>
            <issue>22</issue>
            <pub-id pub-id-type="doi">10.1016/s2542-5196(22)00090-0</pub-id>
            <pub-id pub-id-type="pmid">35594895</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B9">
        <label>9.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Génésio Amesitor, K., Tchakala, I., Djeri, B., Boguido, G., Kodom, T. and Limam Bawa, M. (2025) Bacteriological Quality of Drinking Water in Tsévié and Its Surroundings, Togo. <italic>Journal of Environment Pollution and Human Health</italic>, 13, 1-7. https://doi.org/10.12691/jephh-13-1-1 <pub-id pub-id-type="doi">10.12691/jephh-13-1-1</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.12691/jephh-13-1-1">https://doi.org/10.12691/jephh-13-1-1</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Amesitor, K.</string-name>
              <string-name>Tchakala, I.</string-name>
              <string-name>Djeri, B.</string-name>
              <string-name>Boguido, G.</string-name>
              <string-name>Kodom, T.</string-name>
              <string-name>Bawa, M.</string-name>
              <string-name>Surroundings, T</string-name>
            </person-group>
            <year>2025</year>
            <article-title>Bacteriological Quality of Drinking Water in Tsévié and Its Surroundings, Togo</article-title>
            <source>Journal of Environment Pollution and Human Health</source>
            <volume>13</volume>
            <pub-id pub-id-type="doi">10.12691/jephh-13-1-1</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B10">
        <label>10.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Ouéda, N., Gandi, F.O., Tchakala, I. and Bawa, M.L. (2025) Assessment of the Quality of Drinking Water from Wells and Boreholes in the Municipality of Tchaoudjo 1 (Didaourè agglomeration) in the Central Region of Togo. <italic>Journal de la Société Ouest-Africaine de Chimie</italic>, 54, 35-46. (In French)</mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Gandi, F.O.</string-name>
              <string-name>Tchakala, I.</string-name>
              <string-name>Bawa, M.L.</string-name>
            </person-group>
            <year>2025</year>
            <article-title>Assessment of the Quality of Drinking Water from Wells and Boreholes in the Municipality of Tchaoudjo 1 (Didaourè agglomeration) in the Central Region of Togo</article-title>
            <source>Journal de la Société Ouest-Africaine de Chimie</source>
            <volume>54</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B11">
        <label>11.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Sokegbe, O.Y., Djeri, B., Kogno, E., Kangnidossou, M., <italic>et al</italic>. (2018) Health Risks Linked to Drinking Water Sources in District No. 2 of Lomé-Commune: The Case of the Adakpamé Neighbourhood. <italic>International</italic><italic>Journal</italic><italic>of</italic><italic>Biological</italic><italic>and</italic><italic>Chemical</italic><italic>Sciences</italic>, 11, Article 2341. (In French) https://doi.org/10.4314/ijbcs.v11i5.31 <pub-id pub-id-type="doi">10.4314/ijbcs.v11i5.31</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.4314/ijbcs.v11i5.31">https://doi.org/10.4314/ijbcs.v11i5.31</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Sokegbe, O.Y.</string-name>
              <string-name>Djeri, B.</string-name>
              <string-name>Kogno, E.</string-name>
              <string-name>Kangnidossou, M.</string-name>
            </person-group>
            <year>2018</year>
            <article-title>Health Risks Linked to Drinking Water Sources in District No</article-title>
            <source>2 of Lomé-Commune: The Case of the Adakpamé Neighbourhood. International Journal of Biological and Chemical Sciences</source>
            <volume>11</volume>
            <elocation-id>2341</elocation-id>
            <pub-id pub-id-type="doi">10.4314/ijbcs.v11i5.31</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B12">
        <label>12.</label>
        <citation-alternatives>
          <mixed-citation publication-type="book">da Silva, N., Taniwaki, M.H., Junqueira, V.C., <italic>et al</italic>. (2018) Microbiological Examination Methods of Food and Water: A Laboratory Manual. 2nd Edition, CRC Press.</mixed-citation>
          <element-citation publication-type="book">
            <person-group person-group-type="author">
              <string-name>Silva, N.</string-name>
              <string-name>Taniwaki, M.H.</string-name>
              <string-name>Junqueira, V.C.</string-name>
              <string-name>Edition, C</string-name>
            </person-group>
            <year>2018</year>
            <article-title>Microbiological Examination Methods of Food and Water: A Laboratory Manual</article-title>
            <source>2nd Edition</source>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B13">
        <label>13.</label>
        <citation-alternatives>
          <mixed-citation publication-type="confproc">Lu, Y., Xu, X., Li, T., Chen, Z., Huang, Q., Huang, Y., <italic>et al</italic>. (2010) Artemia Salina as a Bioassay Organism for Testing Water Quality in Hangzhou Section of Beijing-Hangzhou Grand Canal. 2010 4 <italic>th International Conference on Bioinformatics and Biomedical Engineering</italic>, Chengdu, 18-20 June 2010, 1-3. https://doi.org/10.1109/icbbe.2010.5517735 <pub-id pub-id-type="doi">10.1109/icbbe.2010.5517735</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1109/icbbe.2010.5517735">https://doi.org/10.1109/icbbe.2010.5517735</ext-link></mixed-citation>
          <element-citation publication-type="confproc">
            <person-group person-group-type="author">
              <string-name>Lu, Y.</string-name>
              <string-name>Xu, X.</string-name>
              <string-name>Li, T.</string-name>
              <string-name>Chen, Z.</string-name>
              <string-name>Huang, Q.</string-name>
              <string-name>Huang, Y.</string-name>
              <string-name>Engineering, C</string-name>
            </person-group>
            <year>2010</year>
            <article-title>Artemia Salina as a Bioassay Organism for Testing Water Quality in Hangzhou Section of Beijing-Hangzhou Grand Canal</article-title>
            <source>2010 4th International Conference on Bioinformatics and Biomedical Engineering</source>
            <volume>18</volume>
            <pub-id pub-id-type="doi">10.1109/icbbe.2010.5517735</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B14">
        <label>14.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Dossou-Yovo, K.M., Diallo, A., Lawson-Evi, P., Kantati, Y.T., Darré, T., Bakoma, B., <italic>et al</italic>. (2021) A 90-Day Oral Toxicity of Hydroethanolic Root Extract of Carissa Spinarum in Wistar Rats. <italic>Journal of Toxicology</italic>, 2021, 1-6. https://doi.org/10.1155/2021/5570206 <pub-id pub-id-type="doi">10.1155/2021/5570206</pub-id><pub-id pub-id-type="pmid">33986798</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1155/2021/5570206">https://doi.org/10.1155/2021/5570206</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Dossou-Yovo, K.M.</string-name>
              <string-name>Diallo, A.</string-name>
              <string-name>Lawson-Evi, P.</string-name>
              <string-name>Kantati, Y.T.</string-name>
              <string-name>Bakoma, B.</string-name>
            </person-group>
            <year>2021</year>
            <article-title>A 90-Day Oral Toxicity of Hydroethanolic Root Extract of Carissa Spinarum in Wistar Rats</article-title>
            <source>Journal of Toxicology</source>
            <volume>2021</volume>
            <pub-id pub-id-type="doi">10.1155/2021/5570206</pub-id>
            <pub-id pub-id-type="pmid">33986798</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B15">
        <label>15.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Pascaline, L.L., Kandanda, T., Kibwega, F., Kalenga, K., Mulumba, K. and Sifa, A. (2025) Comparative Study of the Pollution Level of the Angombode and Mayi ya chumvi Watercourses at Masako in DR Congo. <italic>International Journal of Engineering Development and Research</italic>, 13, 228-242. (In French)</mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Pascaline, L.L.</string-name>
              <string-name>Kandanda, T.</string-name>
              <string-name>Kibwega, F.</string-name>
              <string-name>Kalenga, K.</string-name>
              <string-name>Mulumba, K.</string-name>
              <string-name>Sifa, A.</string-name>
            </person-group>
            <year>2025</year>
            <article-title>Comparative Study of the Pollution Level of the Angombode and Mayi ya chumvi Watercourses at Masako in DR Congo</article-title>
            <source>International Journal of Engineering Development and Research</source>
            <volume>13</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B16">
        <label>16.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Tampo, L., Ayah, M., Kodom, T., Tchakakla, I., <italic>et al</italic>. (2014) Impact of Chlorine Demand and of Chlorination on the Disinfection of Well Water in the Neighbourhoods of Lomé: The Case of the Démakpoé and Agbalépédogan Neighbourhoods (Togo). <italic>Journal of Applied Biosciences</italic>, 75, Article 6272. (In French). https://doi.org/10.4314/jab.v75i1.12 <pub-id pub-id-type="doi">10.4314/jab.v75i1.12</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.4314/jab.v75i1.12">https://doi.org/10.4314/jab.v75i1.12</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Tampo, L.</string-name>
              <string-name>Ayah, M.</string-name>
              <string-name>Kodom, T.</string-name>
              <string-name>Tchakakla, I.</string-name>
            </person-group>
            <year>2014</year>
            <article-title>Impact of Chlorine Demand and of Chlorination on the Disinfection of Well Water in the Neighbourhoods of Lomé: The Case of the Démakpoé and Agbalépédogan Neighbourhoods (Togo)</article-title>
            <source>Journal of Applied Biosciences</source>
            <volume>75</volume>
            <elocation-id>6272</elocation-id>
            <pub-id pub-id-type="doi">10.4314/jab.v75i1.12</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B17">
        <label>17.</label>
        <citation-alternatives>
          <mixed-citation publication-type="report">Antea Group, JAT Consulting SARL (2022) Environmental and Social Impact Assessment of the Adétikopé Industrial Platform Project—Addendum to Phase I of the ESIA. Report No. 113972/F, Antea Group, Antony, France. https://pia-togo.com/wp-content/uploads/2023/10/EIES-TOGO-PIA_IFC_Phase-I_Addendum_French-1.pdf</mixed-citation>
          <element-citation publication-type="report">
            <person-group person-group-type="author">
              <string-name>Group, J</string-name>
              <string-name>Group, A</string-name>
            </person-group>
            <year>2022</year>
            <article-title>Environmental and Social Impact Assessment of the Adétikopé Industrial Platform Project—Addendum to Phase I of the ESIA</article-title>
            <source>Report No. 113972/F</source>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B18">
        <label>18.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Calero Preciado, C., Boxall, J., Soria-Carrasco, V., Martínez, S. and Douterelo, I. (2021) Implications of Climate Change: How Does Increased Water Temperature Influence Biofilm and Water Quality of Chlorinated Drinking Water Distribution Systems? <italic>Frontiers in Microbiology</italic>, 12, Article 658927. https://doi.org/10.3389/fmicb.2021.658927 <pub-id pub-id-type="doi">10.3389/fmicb.2021.658927</pub-id><pub-id pub-id-type="pmid">34168627</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3389/fmicb.2021.658927">https://doi.org/10.3389/fmicb.2021.658927</ext-link></mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Preciado, C.</string-name>
              <string-name>Boxall, J.</string-name>
              <string-name>Soria-Carrasco, V.</string-name>
              <string-name>Douterelo, I.</string-name>
            </person-group>
            <year>2021</year>
            <article-title>Implications of Climate Change: How Does Increased Water Temperature Influence Biofilm and Water Quality of Chlorinated Drinking Water Distribution Systems? Frontiers in Microbiology, 12, Article 658927</article-title>
            <elocation-id>658927</elocation-id>
            <pub-id pub-id-type="doi">10.3389/fmicb.2021.658927</pub-id>
            <pub-id pub-id-type="pmid">34168627</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B19">
        <label>19.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Fambi, K., Ayah, M., Sossou, K.S., Boguido, G., <italic>et al</italic>. (2021) Water Quality and Water Treatment Trials in a Peri-Urban Environment: The Case of the Borehole Water of the Légbassito and Vakpossito Cantons (Togo). <italic>International Journal of Biological and Chemical Sciences</italic>, 15, 317‑337. (In French) https://doi.org/10.4314/ijbcs.v15i1.28 <pub-id pub-id-type="doi">10.4314/ijbcs.v15i1.28</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.4314/ijbcs.v15i1.28">https://doi.org/10.4314/ijbcs.v15i1.28</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Fambi, K.</string-name>
              <string-name>Ayah, M.</string-name>
              <string-name>Sossou, K.S.</string-name>
              <string-name>Boguido, G.</string-name>
            </person-group>
            <year>2021</year>
            <article-title>Water Quality and Water Treatment Trials in a Peri-Urban Environment: The Case of the Borehole Water of the Légbassito and Vakpossito Cantons (Togo)</article-title>
            <source>International Journal of Biological and Chemical Sciences</source>
            <volume>15</volume>
            <pub-id pub-id-type="doi">10.4314/ijbcs.v15i1.28</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B20">
        <label>20.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Dégbey, C., Makoutode, M., Ouendo, E.M., Fayomi, B. and Brouwer, C.D. (2008) The Quality of Well Water in the Municipality of Abomey-Calavi in Benin. (In French)</mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Makoutode, M.</string-name>
              <string-name>Ouendo, E.M.</string-name>
              <string-name>Fayomi, B.</string-name>
              <string-name>Brouwer, C.D.</string-name>
            </person-group>
            <year>2008</year>
            <article-title>The Quality of Well Water in the Municipality of Abomey-Calavi in Benin</article-title>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B21">
        <label>21.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Balitte, A.G., Pascal, D.D.M., Camille, N.I., <italic>et al</italic>. (2025) Physicochemical and Microbiological Assessment of the Surface Water of the Talatala and Mulundu Streams Consumed by the Population of the Village of KIBOBA KWENGE Sector in DR Congo. <italic>Revue Internationale de la Recherche Scientifique</italic>, 3, 3574‑3594. (In French)</mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Balitte, A.G.</string-name>
              <string-name>Pascal, D.D.M.</string-name>
              <string-name>Camille, N.I.</string-name>
            </person-group>
            <year>2025</year>
            <article-title>Physicochemical and Microbiological Assessment of the Surface Water of the Talatala and Mulundu Streams Consumed by the Population of the Village of KIBOBA KWENGE Sector in DR Congo</article-title>
            <source>Revue Internationale de la Recherche Scientifique</source>
            <volume>3</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B22">
        <label>22.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Ahoudi, H., Gnandi, K., Tanouayi, G. and Ouro-Sama, K. (2015) Physicochemical Characterization and State of Pollution by Trace Metal Elements of the Groundwater of Lome (Southern Togo): The Case of the AGOE ZONGO Neighborhood. <italic>L</italic><italic>ARHYSS</italic><italic>Journal</italic>, 12, 41‑56. (In French) https://asjp.cerist.dz/en/article/55290</mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Ahoudi, H.</string-name>
              <string-name>Gnandi, K.</string-name>
              <string-name>Tanouayi, G.</string-name>
              <string-name>Ouro-Sama, K.</string-name>
            </person-group>
            <year>2015</year>
            <article-title>Physicochemical Characterization and State of Pollution by Trace Metal Elements of the Groundwater of Lome (Southern Togo): The Case of the AGOE ZONGO Neighborhood</article-title>
            <source>LARHYSS Journal</source>
            <volume>12</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B23">
        <label>23.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Boutayeb, M., Bouzidi, A. and Fekhaoui, M. (2012) Study of the Physicochemical Quality of Raw Wastewater from Five Towns of the Chaouia—Ouardigha Region (Morocco). <italic>Bulletin de</italic><italic>l</italic>’ <italic>Institut</italic><italic>Scientifique</italic>, 2012, 145-150. (In French)</mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Boutayeb, M.</string-name>
              <string-name>Bouzidi, A.</string-name>
              <string-name>Fekhaoui, M.</string-name>
            </person-group>
            <year>2012</year>
            <article-title>Study of the Physicochemical Quality of Raw Wastewater from Five Towns of the Chaouia—Ouardigha Region (Morocco)</article-title>
            <source>Bulletin de l’Institut Scientifique</source>
            <volume>2012</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B24">
        <label>24.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Gnazou, M., Assogba, K., Sabi, B. and Bawa, L. (2015) Physicochemical and Bacteriological Quality of the Water Used in the Schools of the Zio Prefecture (Togo). <italic>International Journal of Biological and Chemical Sciences</italic>, 9, Article 504. (In French) https://doi.org/10.4314/ijbcs.v9i1.43 <pub-id pub-id-type="doi">10.4314/ijbcs.v9i1.43</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.4314/ijbcs.v9i1.43">https://doi.org/10.4314/ijbcs.v9i1.43</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Gnazou, M.</string-name>
              <string-name>Assogba, K.</string-name>
              <string-name>Sabi, B.</string-name>
              <string-name>Bawa, L.</string-name>
            </person-group>
            <year>2015</year>
            <article-title>Physicochemical and Bacteriological Quality of the Water Used in the Schools of the Zio Prefecture (Togo)</article-title>
            <source>International Journal of Biological and Chemical Sciences</source>
            <volume>9</volume>
            <elocation-id>504</elocation-id>
            <pub-id pub-id-type="doi">10.4314/ijbcs.v9i1.43</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B25">
        <label>25.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Talhaoui, A., El Hmaidi, A., Jaddi, H., Ousmana, H. and Manssouri, I. (2020) Calculation of the Water Quality Index (WQI) for the Assessment of the Physico-Chemical Quality of the Surface Waters of the Moulouya River (NE, Morocco). <italic>European Sci</italic><italic>entific Journal</italic>, 16, 64. (In French) https://doi.org/10.19044/esj.2020.v16n2p64 <pub-id pub-id-type="doi">10.19044/esj.2020.v16n2p64</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.19044/esj.2020.v16n2p64">https://doi.org/10.19044/esj.2020.v16n2p64</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Talhaoui, A.</string-name>
              <string-name>Hmaidi, A.</string-name>
              <string-name>Jaddi, H.</string-name>
              <string-name>Ousmana, H.</string-name>
              <string-name>Manssouri, I.</string-name>
              <string-name>NE, M</string-name>
            </person-group>
            <year>2020</year>
            <article-title>Calculation of the Water Quality Index (WQI) for the Assessment of the Physico-Chemical Quality of the Surface Waters of the Moulouya River (NE, Morocco)</article-title>
            <source>European Scientific Journal</source>
            <volume>16</volume>
            <pub-id pub-id-type="doi">10.19044/esj.2020.v16n2p64</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B26">
        <label>26.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Thomas, O. and Mazas, N. (1986) The Measurement of Chemical Oxygen Demand in Weakly Polluted Media. <italic>Analusis</italic>, 14, 300‑302. (In French)</mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Thomas, O.</string-name>
              <string-name>Mazas, N.</string-name>
            </person-group>
            <year>1986</year>
            <article-title>The Measurement of Chemical Oxygen Demand in Weakly Polluted Media</article-title>
            <source>Analusis</source>
            <volume>14</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B27">
        <label>27.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Sema, A.I.M., Kwamivi, S. and Baba, G. (2019) Impact of the Discharge of Industrial Wastewater on the Physicochemical Quality of Urban Waters: The Case of the Kpiyimboua Stream of the City of Kara. <italic>Afrique Science Revue Internationale des Sciences et Technologie</italic>, 15, 116‑129. (In French)</mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Sema, A.I.M.</string-name>
              <string-name>Kwamivi, S.</string-name>
              <string-name>Baba, G.</string-name>
            </person-group>
            <year>2019</year>
            <article-title>Impact of the Discharge of Industrial Wastewater on the Physicochemical Quality of Urban Waters: The Case of the Kpiyimboua Stream of the City of Kara</article-title>
            <source>Afrique Science Revue Internationale des Sciences et Technologie</source>
            <volume>15</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B28">
        <label>28.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Kpoviessy, G.H.F., Doto, V.C., Abahi, K.S., Agadjihouede, H. and Godonou, G. (2025) Wastewater Management Practices in Porto-Novo in Benin. <italic>Revue Marocaine des Sciences Agronomiques et Vétérinaires</italic>, 13, 256‑265. (In French)</mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Kpoviessy, G.H.F.</string-name>
              <string-name>Doto, V.C.</string-name>
              <string-name>Abahi, K.S.</string-name>
              <string-name>Agadjihouede, H.</string-name>
              <string-name>Godonou, G.</string-name>
            </person-group>
            <year>2025</year>
            <article-title>Wastewater Management Practices in Porto-Novo in Benin</article-title>
            <source>Revue Marocaine des Sciences Agronomiques et Vétérinaires</source>
            <volume>13</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B29">
        <label>29.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Idrissi, Y.A., Alemad, A., Aboubaker, S., Daifi, H., <italic>et al</italic>. (2015) Physico-Chemical Characterization of Wastewater from Azilal City—Morocco. <italic>International Journal of Innovation and Applied Studie</italic><italic>s</italic>, 11, 556-566. (In French)</mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Idrissi, Y.A.</string-name>
              <string-name>Alemad, A.</string-name>
              <string-name>Aboubaker, S.</string-name>
              <string-name>Daifi, H.</string-name>
            </person-group>
            <year>2015</year>
            <article-title>Physico-Chemical Characterization of Wastewater from Azilal City—Morocco</article-title>
            <source>International Journal of Innovation and Applied Studies</source>
            <volume>11</volume>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B30">
        <label>30.</label>
        <citation-alternatives>
          <mixed-citation publication-type="journal">Kpiagou, P., Tchegueni, S., Boguido, G., Sama, D., Gnandi, K., Tchacondo, T., <italic>et al</italic>. (2022) Assessment of the Pollution of the Water Resources of the Didagou Catchment (Dapaong, Northern Togo). <italic>International</italic><italic>Journal</italic><italic>of</italic><italic>Biological</italic><italic>and</italic><italic>Chemical</italic><italic>Sciences</italic>, 16, 481-497. (In French) https://doi.org/10.4314/ijbcs.v16i1.39 <pub-id pub-id-type="doi">10.4314/ijbcs.v16i1.39</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.4314/ijbcs.v16i1.39">https://doi.org/10.4314/ijbcs.v16i1.39</ext-link></mixed-citation>
          <element-citation publication-type="journal">
            <person-group person-group-type="author">
              <string-name>Kpiagou, P.</string-name>
              <string-name>Tchegueni, S.</string-name>
              <string-name>Boguido, G.</string-name>
              <string-name>Sama, D.</string-name>
              <string-name>Gnandi, K.</string-name>
              <string-name>Tchacondo, T.</string-name>
              <string-name>Dapaong, N</string-name>
            </person-group>
            <year>2022</year>
            <article-title>Assessment of the Pollution of the Water Resources of the Didagou Catchment (Dapaong, Northern Togo)</article-title>
            <source>International Journal of Biological and Chemical Sciences</source>
            <volume>16</volume>
            <pub-id pub-id-type="doi">10.4314/ijbcs.v16i1.39</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B31">
        <label>31.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Choumane, R. and Peulon, S. (2019) Development of an Innovative Electrochemical Process for the Depollution of Waters Loaded with Heavy Metals. <italic>Colloids</italic><italic>and</italic><italic>Surfaces</italic><italic>A</italic>: <italic>Physicochemical</italic><italic>and</italic><italic>Engineering</italic><italic>Aspects</italic>, 577, 594-603. (In French) https://doi.org/10.1016/j.colsurfa.2019.06.013 <pub-id pub-id-type="doi">10.1016/j.colsurfa.2019.06.013</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1016/j.colsurfa.2019.06.013">https://doi.org/10.1016/j.colsurfa.2019.06.013</ext-link></mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Choumane, R.</string-name>
              <string-name>Peulon, S.</string-name>
            </person-group>
            <year>2019</year>
            <article-title>Development of an Innovative Electrochemical Process for the Depollution of Waters Loaded with Heavy Metals</article-title>
            <source>Colloids and Surfaces A: Physicochemical and Engineering Aspects</source>
            <volume>577</volume>
            <pub-id pub-id-type="doi">10.1016/j.colsurfa.2019.06.013</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
      <ref id="B32">
        <label>32.</label>
        <citation-alternatives>
          <mixed-citation publication-type="other">Guillaume-Ruty, S., Meunier, A., Azaïs, A. and Lombard-Latune, R. (2024) Reuse of Treated Wastewater: Risk Management and Removal Efficiency of Treatment Processes with Regard to the Forthcoming French Regulatory Requirements (in French). <italic>Techniques</italic><italic>Sciences</italic><italic>Méthodes</italic>, 119, 81-96. (In French) https://doi.org/10.36904/20241081 <pub-id pub-id-type="doi">10.36904/20241081</pub-id><ext-link ext-link-type="uri" xlink:href="https://doi.org/10.36904/20241081">https://doi.org/10.36904/20241081</ext-link></mixed-citation>
          <element-citation publication-type="other">
            <person-group person-group-type="author">
              <string-name>Guillaume-Ruty, S.</string-name>
              <string-name>Meunier, A.</string-name>
              <string-name>Lombard-Latune, R.</string-name>
            </person-group>
            <year>2024</year>
            <article-title>Reuse of Treated Wastewater: Risk Management and Removal Efficiency of Treatment Processes with Regard to the Forthcoming French Regulatory Requirements (in French)</article-title>
            <source>Techniques Sciences Méthodes</source>
            <volume>119</volume>
            <pub-id pub-id-type="doi">10.36904/20241081</pub-id>
          </element-citation>
        </citation-alternatives>
      </ref>
    </ref-list>
  </back>
</article>