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  <front>
    <journal-meta>
      <journal-id journal-id-type="publisher-id">ajcc</journal-id>
      <journal-title-group>
        <journal-title>American Journal of Climate Change</journal-title>
      </journal-title-group>
      <issn pub-type="epub">2167-9509</issn>
      <issn pub-type="ppub">2167-9495</issn>
      <publisher>
        <publisher-name>Scientific Research Publishing</publisher-name>
      </publisher>
    </journal-meta>
    <article-meta>
      <article-id pub-id-type="doi">10.4236/ajcc.2026.153004</article-id>
      <article-id pub-id-type="publisher-id">ajcc-153319</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>A Three-Parameter Aerosol Optical Discrimination Framework Integrating Fine-Mode Fraction, Single Scattering Albedo, and Differential Ångström Exponent over Selected AERONET Sites in Africa</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author" corresp="yes">
          <contrib-id contrib-id-type="orcid">0009-0007-6374-5690</contrib-id>
          <name name-style="western">
            <surname>Situma</surname>
            <given-names>Yonah</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <contrib-id contrib-id-type="orcid">0000-0003-3267-4512</contrib-id>
          <name name-style="western">
            <surname>Makokha</surname>
            <given-names>John W.</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <contrib-id contrib-id-type="orcid">0000-0002-0683-2540</contrib-id>
          <name name-style="western">
            <surname>Khakina</surname>
            <given-names>Peter</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <contrib-id contrib-id-type="orcid">0000-0003-2415-2212</contrib-id>
          <name name-style="western">
            <surname>Khamala</surname>
            <given-names>Geoffrey W.</given-names>
          </name>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
      </contrib-group>
      <aff id="aff1"><label>1</label> Department of Science, Technology and Engineering, Kibabii University, Bungoma, Kenya </aff>
      <aff id="aff2"><label>2</label> Department of Renewable Energy and Technology, Turkana University College, Lodwar, Kenya </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>21</day>
        <month>08</month>
        <year>2026</year>
      </pub-date>
      <pub-date pub-type="collection">
        <month>08</month>
        <year>2026</year>
      </pub-date>
      <volume>15</volume>
      <issue>03</issue>
      <fpage>73</fpage>
      <lpage>84</lpage>
      <history>
        <date date-type="received">
          <day>30</day>
          <month>06</month>
          <year>2026</year>
        </date>
        <date date-type="accepted">
          <day>18</day>
          <month>08</month>
          <year>2026</year>
        </date>
        <date date-type="published">
          <day>21</day>
          <month>08</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/ajcc.2026.153004">https://doi.org/10.4236/ajcc.2026.153004</self-uri>
      <abstract>
        <p>Accurate aerosol optical discrimination remains challenging due to overlap among aerosol types under mixed atmospheric conditions. This study proposed a novel dAE-enhanced aerosol discrimination model using Fine Mode Fraction (FMF), Single Scattering Albedo (SSA), and Ångström Exponent Difference (dAE) derived from AERONET observations across African sites. Daily Level 2.0 aerosol retrievals were analyzed using FMF-SSA, FMF-dAE, and SSA-dAE relationships to evaluate the contribution of dAE in improving aerosol separation. Results showed that incorporation of dAE significantly reduced overlap between aerosol clusters and enhanced discrimination between fine-mode absorbing aerosols, mixed aerosols, and coarse mineral dust particles. Positive dAE values were associated with biomass burning and polluted continental aerosols, while near-zero or negative dAE values indicated coarse dust dominance. The proposed framework improves aerosol characterization and provides valuable applications for climate modeling, satellite validation, and radiative forcing assessment across Africa.</p>
      </abstract>
      <kwd-group kwd-group-type="author-generated" xml:lang="en">
        <kwd>Aerosol Discrimination</kwd>
        <kwd>dAE</kwd>
        <kwd>FMF</kwd>
        <kwd>SSA</kwd>
        <kwd>Africa</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec1">
      <title>1. Introduction</title>
      <p>Atmospheric aerosols significantly influence the Earth’s climate system through their interactions with solar radiation, cloud microphysics, and atmospheric chemistry ([<xref ref-type="bibr" rid="B9">9</xref>]). Aerosol radiative effects remain one of the largest sources of uncertainty in climate forcing assessments because aerosol optical properties vary substantially across regions and source types ([<xref ref-type="bibr" rid="B16">16</xref>]). Aerosols also affect visibility, precipitation processes, ecosystem productivity, and human health, particularly in regions characterized by intense biomass burning, dust outbreaks, and urban pollution ([<xref ref-type="bibr" rid="B14">14</xref>]; [<xref ref-type="bibr" rid="B15">15</xref>]).</p>
      <p>Aerosol characterization commonly relies on optical parameters retrieved from ground-based remote sensing networks such as AERONET, which provides globally standardized observations of aerosol optical depth (AOD), Ångström Exponent (AE), Single Scattering Albedo (SSA), and Fine Mode Fraction (FMF) ([<xref ref-type="bibr" rid="B3">3</xref>]). These parameters are widely applied in aerosol discrimination studies because they provide indirect information on particle size distribution, scattering efficiency, and absorptive behavior ([<xref ref-type="bibr" rid="B13">13</xref>]). Among these parameters, FMF and SSA have become particularly useful in identifying dominant aerosol regimes including mineral dust, biomass burning aerosols, urban-industrial pollution, and marine aerosols ([<xref ref-type="bibr" rid="B2">2</xref>]).</p>
      <p>Despite the success of FMF-SSA classification approaches, substantial overlap often exists between aerosol populations under mixed atmospheric conditions ([<xref ref-type="bibr" rid="B11">11</xref>]). Similar FMF-SSA combinations may represent entirely different aerosol mixtures, thereby limiting the reliability of traditional two-parameter discrimination models ([<xref ref-type="bibr" rid="B6">6</xref>]). This limitation is especially evident in Africa, where multiple aerosol sources coexist and interact seasonally across large spatial scales ([<xref ref-type="bibr" rid="B14">14</xref>]).</p>
      <p>Northern Africa is strongly dominated by coarse mineral dust aerosols originating from the Sahara Desert, whereas Southern Africa experiences substantial contributions from biomass burning emissions and polluted continental aerosols ([<xref ref-type="bibr" rid="B5">5</xref>]). These aerosol systems frequently mix during long-range transport, creating transitional aerosol states that are difficult to distinguish using conventional optical discrimination methods ([<xref ref-type="bibr" rid="B14">14</xref>]; [<xref ref-type="bibr" rid="B2">2</xref>]). Consequently, there is increasing interest in developing enhanced aerosol discrimination frameworks capable of resolving aerosol mixtures with greater precision ([<xref ref-type="bibr" rid="B11">11</xref>]).</p>
      <p>Recent aerosol studies have emphasized the importance of incorporating spectral curvature information into aerosol classification models because conventional AE alone may not adequately capture aerosol size heterogeneity (; [<xref ref-type="bibr" rid="B16">16</xref>]). The Ångström Exponent Difference (dAE), defined as the difference between AE calculated over two wavelength intervals, provides additional sensitivity to spectral variations associated with mixed aerosol populations ([<xref ref-type="bibr" rid="B13">13</xref>]). Positive dAE values are generally linked to fine-mode aerosol dominance, whereas negative or near-zero values indicate coarse-mode particle influence ([<xref ref-type="bibr" rid="B5">5</xref>]).</p>
      <p>Over Africa, several studies have demonstrated the effectiveness of AERONET-derived optical properties for aerosol source identification and characterization. For instance, strong seasonal variations in aerosol optical properties over East Africa associated with biomass burning, urban emissions, and long-range transported dust have been observed ([<xref ref-type="bibr" rid="B10">10</xref>]). Similarly, the influence of regional transport processes and mixed aerosol conditions on aerosol optical characteristics across African environments has been highlighted, which has emphasized the importance of advanced aerosol discrimination approaches for improving aerosol source attribution and climate impact assessments over the continent ([<xref ref-type="bibr" rid="B10">10</xref>]; [<xref ref-type="bibr" rid="B15">15</xref>]).</p>
      <p>Although dAE has demonstrated potential for representing aerosol spectral behavior, its integration into aerosol optical discrimination models remains limited, particularly over Africa, where aerosol mixing processes are highly dynamic ([<xref ref-type="bibr" rid="B14">14</xref>]). Incorporating dAE into FMF-SSA space may therefore improve separation among aerosol clusters and reduce ambiguity associated with overlapping aerosol regimes ([<xref ref-type="bibr" rid="B2">2</xref>]).</p>
      <p>This study proposes a novel dAE-enhanced aerosol optical discrimination model based on FMF, SSA, and dAE derived from AERONET observations across African sites. The study investigates how dAE improves aerosol discrimination within FMF-SSA space and evaluates regional aerosol variability between North and South Africa. The proposed framework aims to enhance aerosol typing capability for climate studies, satellite validation, and radiative forcing assessments ([<xref ref-type="bibr" rid="B16">16</xref>]).</p>
    </sec>
    <sec id="sec2">
      <title>2. Study Area, Data, and Methods</title>
      <sec id="sec2dot1">
        <title>2.1. Study Area and Data Source</title>
        <p>This study utilized aerosol optical observations obtained from selected African Aerosol Robotic Network (AERONET) stations representing contrasting aerosol environments across North and South Africa (<xref ref-type="fig" rid="fig1">Figure 1</xref>). The selected twelve AERONET sites capture dominant regional aerosol regimes, including Saharan dust, biomass burning smoke, marine aerosols, and polluted continental particles. Grouping the stations into North and South African regions enabled assessment of regional aerosol variability associated with different emission sources and atmospheric transport processes.</p>
        <p>AERONET Version 3 Level 2.0 quality-assured daily averaged retrievals were used in this study because they provide cloud-screened and calibration-corrected aerosol optical parameters with improved uncertainty characterization ([<xref ref-type="bibr" rid="B1">1</xref>]; [<xref ref-type="bibr" rid="B7">7</xref>]). Daily averages were selected to minimize short-term fluctuations while preserving synoptic aerosol variability relevant for aerosol discrimination analysis ([<xref ref-type="bibr" rid="B13">13</xref>]).</p>
      </sec>
      <sec id="sec2dot2">
        <title>2.2. Aerosol Discrimination Framework</title>
        <p>The aerosol discrimination framework was developed using three complementary parameter relationships: FMF-SSA, FMF-dAE, and SSA-dAE ([<xref ref-type="bibr" rid="B11">11</xref>]). In the FMF-SSA analysis, dAE was incorporated as a color-coded parameter to visualize spectral variability within conventional aerosol discrimination space ([<xref ref-type="bibr" rid="B2">2</xref>]). This approach enabled the identification of hidden aerosol transitions and mixed aerosol regimes that may not be clearly resolved using FMF and SSA alone ([<xref ref-type="bibr" rid="B16">16</xref>]).</p>
        <fig id="fig1">
          <label>Figure 1</label>
          <graphic xlink:href="https://html.scirp.org/file/2361758-rId16.jpeg?20260821024550" />
        </fig>
        <p>Figure 1. Spatial distribution of selected AERONET version 3 sites across Africa and their dominant aerosol types, classified as dust-dominated, biomass burning-dominated, mixed aerosols, and mixed/regional influences, illustrating the regional variability of aerosol sources and atmospheric transport processes over the continent.</p>
        <p>Scatter distributions were analyzed to identify aerosol clustering behavior associated with dominant aerosol types across Africa. Fine-mode absorbing aerosols such as biomass burning smoke were expected to exhibit high FMF and lower SSA values, whereas coarse mineral dust aerosols were expected to occupy lower FMF regions with variable SSA characteristics ([<xref ref-type="bibr" rid="B5">5</xref>]).</p>
      </sec>
      <sec id="sec2dot3">
        <title>2.3. Statistical Analysis</title>
        <p>The conventional aerosol classification framework is based on the joint relationship between the Fine Mode Fraction (FMF) and Single Scattering Albedo (SSA), where FMF represents particle size dominance, and SSA characterizes aerosol absorptive properties (<bold>Table 1</bold>) ([<xref ref-type="bibr" rid="B7">7</xref>]; [<xref ref-type="bibr" rid="B10">10</xref>]).</p>
        <p>Table 1. Statistical and analytical framework applied in the study.</p>
        <table-wrap id="tbl1">
          <label>Table 1</label>
          <table>
            <tbody>
              <tr>
                <td>
                  <bold>Analysis</bold>
                  <bold>Component</bold>
                </td>
                <td>
                  <bold>Method Applied</bold>
                </td>
                <td>
                  <bold>Purpose</bold>
                </td>
              </tr>
              <tr>
                <td>Data Source</td>
                <td>AERONET Version 3 Level 2.0</td>
                <td>Obtain quality-assured aerosol optical properties</td>
              </tr>
              <tr>
                <td>Temporal Resolution</td>
                <td>Daily averages</td>
                <td>Reduce short-term variability</td>
              </tr>
              <tr>
                <td>Aerosol Parameters</td>
                <td>FMF, SSA, AE, dAE</td>
                <td>Characterize aerosol optical behavior</td>
              </tr>
              <tr>
                <td>dAE Computation</td>
                <td>AE440-675-AE675-870</td>
                <td>Quantify aerosol spectral curvature</td>
              </tr>
              <tr>
                <td>Scatter Analysis</td>
                <td>FMF-SSA, FMF-dAE, SSA-dAE</td>
                <td>Evaluate aerosol clustering behavior</td>
              </tr>
              <tr>
                <td>Regional Comparison</td>
                <td>North vs South Africa</td>
                <td>Assess regional aerosol variability</td>
              </tr>
              <tr>
                <td>Aerosol Interpretation</td>
                <td>Threshold-based optical classification</td>
                <td>Identify dominant aerosol regimes</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p>The primary framework was expressed as:</p>
        <disp-formula id="FD1">
          <label>(1)</label>
          <mml:math>
            <mml:mrow>
              <mml:msub>
                <mml:mi>F</mml:mi>
                <mml:mn>1</mml:mn>
              </mml:msub>
              <mml:mo>=</mml:mo>
              <mml:mi>f</mml:mi>
              <mml:mrow>
                <mml:mo>(</mml:mo>
                <mml:mrow>
                  <mml:mi>F</mml:mi>
                  <mml:mi>M</mml:mi>
                  <mml:mi>F</mml:mi>
                  <mml:mo>,</mml:mo>
                  <mml:mi>S</mml:mi>
                  <mml:mi>S</mml:mi>
                  <mml:mi>A</mml:mi>
                </mml:mrow>
                <mml:mo>)</mml:mo>
              </mml:mrow>
            </mml:mrow>
          </mml:math>
        </disp-formula>
        <p>where <italic>F</italic><sub>1</sub> denotes the conventional two-parameter aerosol discrimination space. </p>
        <p>The Fine Mode Fraction (FMF) is defined as the proportion of aerosol optical depth (AOD) contributed by fine particles:</p>
        <disp-formula id="FD2">
          <label>(2)</label>
          <mml:math>
            <mml:mrow>
              <mml:mi>F</mml:mi>
              <mml:mi>M</mml:mi>
              <mml:mi>F</mml:mi>
              <mml:mo>=</mml:mo>
              <mml:mfrac>
                <mml:mrow>
                  <mml:mi>A</mml:mi>
                  <mml:mi>O</mml:mi>
                  <mml:msub>
                    <mml:mi>D</mml:mi>
                    <mml:mrow>
                      <mml:mi>f</mml:mi>
                      <mml:mi>i</mml:mi>
                      <mml:mi>n</mml:mi>
                      <mml:mi>e</mml:mi>
                    </mml:mrow>
                  </mml:msub>
                </mml:mrow>
                <mml:mrow>
                  <mml:mi>A</mml:mi>
                  <mml:mi>O</mml:mi>
                  <mml:msub>
                    <mml:mi>D</mml:mi>
                    <mml:mrow>
                      <mml:mi>t</mml:mi>
                      <mml:mi>o</mml:mi>
                      <mml:mi>t</mml:mi>
                      <mml:mi>a</mml:mi>
                      <mml:mi>l</mml:mi>
                    </mml:mrow>
                  </mml:msub>
                </mml:mrow>
              </mml:mfrac>
            </mml:mrow>
          </mml:math>
        </disp-formula>
        <p>With values approaching unity indicating fine-particle dominance and lower values indicating coarse-mode aerosols ([<xref ref-type="bibr" rid="B10">10</xref>]).</p>
        <p>The Single Scattering Albedo (SSA) is defined as:</p>
        <disp-formula id="FD3">
          <label>(3)</label>
          <mml:math>
            <mml:mrow>
              <mml:mi>S</mml:mi>
              <mml:mi>S</mml:mi>
              <mml:mi>A</mml:mi>
              <mml:mo>=</mml:mo>
              <mml:mfrac>
                <mml:mrow>
                  <mml:msub>
                    <mml:mi>σ</mml:mi>
                    <mml:mrow>
                      <mml:mi>s</mml:mi>
                      <mml:mi>c</mml:mi>
                      <mml:mi>a</mml:mi>
                    </mml:mrow>
                  </mml:msub>
                </mml:mrow>
                <mml:mrow>
                  <mml:msub>
                    <mml:mi>σ</mml:mi>
                    <mml:mrow>
                      <mml:mi>s</mml:mi>
                      <mml:mi>c</mml:mi>
                      <mml:mi>a</mml:mi>
                    </mml:mrow>
                  </mml:msub>
                  <mml:mo>+</mml:mo>
                  <mml:msub>
                    <mml:mi>σ</mml:mi>
                    <mml:mrow>
                      <mml:mi>a</mml:mi>
                      <mml:mi>b</mml:mi>
                      <mml:mi>s</mml:mi>
                    </mml:mrow>
                  </mml:msub>
                </mml:mrow>
              </mml:mfrac>
            </mml:mrow>
          </mml:math>
        </disp-formula>
        <p>where <italic>σ</italic><italic><sub>sca</sub></italic> and <italic>σ</italic><italic><sub>abs</sub></italic> are the aerosol scattering and absorption coefficients, respectively, lower SSA values indicate stronger aerosol absorption, while higher values correspond to predominantly scattering particles ([<xref ref-type="bibr" rid="B1">1</xref>]).</p>
        <p>To improve discrimination between aerosol types exhibiting similar FMF-SSA characteristics but different spectral behaviors, this study introduced the differential Ångström Exponent (dAE) as an additional constraint. The dAE was computed as:</p>
        <disp-formula id="FD4">
          <label>(4)</label>
          <mml:math>
            <mml:mrow>
              <mml:mi>d</mml:mi>
              <mml:mi>A</mml:mi>
              <mml:mi>E</mml:mi>
              <mml:mo>=</mml:mo>
              <mml:mi>A</mml:mi>
              <mml:msub>
                <mml:mi>E</mml:mi>
                <mml:mrow>
                  <mml:mn>440</mml:mn>
                  <mml:mtext>-</mml:mtext>
                  <mml:mn>675</mml:mn>
                  <mml:mi>n</mml:mi>
                  <mml:mi>m</mml:mi>
                </mml:mrow>
              </mml:msub>
              <mml:mo>−</mml:mo>
              <mml:mi>A</mml:mi>
              <mml:msub>
                <mml:mi>E</mml:mi>
                <mml:mrow>
                  <mml:mn>675</mml:mn>
                  <mml:mtext>-</mml:mtext>
                  <mml:mn>870</mml:mn>
                  <mml:mi>n</mml:mi>
                  <mml:mi>m</mml:mi>
                </mml:mrow>
              </mml:msub>
            </mml:mrow>
          </mml:math>
        </disp-formula>
        <p>where <italic>AE</italic><sub>440</sub><sub>-</sub><sub>675nm</sub> and <italic>AE</italic><sub>675</sub><sub>-</sub><sub>870nm</sub> are Ångström exponents calculated over the respective wavelength intervals. The parameter quantified spectral curvature and provided information on particle-size distribution and aerosol modification processes that may not be evident from FMF or SSA alone ([<xref ref-type="bibr" rid="B8">8</xref>]). The proposed enhanced framework, therefore, extended the conventional two-dimensional classification to:</p>
        <disp-formula id="FD5">
          <label>(5)</label>
          <mml:math>
            <mml:mrow>
              <mml:msub>
                <mml:mi>F</mml:mi>
                <mml:mn>2</mml:mn>
              </mml:msub>
              <mml:mo>=</mml:mo>
              <mml:mi>f</mml:mi>
              <mml:mrow>
                <mml:mo>(</mml:mo>
                <mml:mrow>
                  <mml:mi>F</mml:mi>
                  <mml:mi>M</mml:mi>
                  <mml:mi>F</mml:mi>
                  <mml:mo>,</mml:mo>
                  <mml:mi>S</mml:mi>
                  <mml:mi>S</mml:mi>
                  <mml:mi>A</mml:mi>
                  <mml:mo>,</mml:mo>
                  <mml:mi>d</mml:mi>
                  <mml:mi>A</mml:mi>
                  <mml:mi>E</mml:mi>
                </mml:mrow>
                <mml:mo>)</mml:mo>
              </mml:mrow>
            </mml:mrow>
          </mml:math>
        </disp-formula>
        <p>where <italic>F</italic><sub>2</sub> represented the novel three-parameter aerosol discrimination space adopted in this study.</p>
        <p>For each collocated daily observation, the aerosol feature vector was expressed as:</p>
        <disp-formula id="FD6">
          <label>(6)</label>
          <mml:math>
            <mml:mrow>
              <mml:msub>
                <mml:mi>x</mml:mi>
                <mml:mi>i</mml:mi>
              </mml:msub>
              <mml:mo>=</mml:mo>
              <mml:mrow>
                <mml:mo>[</mml:mo>
                <mml:mrow>
                  <mml:mi>F</mml:mi>
                  <mml:mi>M</mml:mi>
                  <mml:msub>
                    <mml:mi>F</mml:mi>
                    <mml:mi>i</mml:mi>
                  </mml:msub>
                  <mml:mo>,</mml:mo>
                  <mml:mi>S</mml:mi>
                  <mml:mi>S</mml:mi>
                  <mml:msub>
                    <mml:mi>A</mml:mi>
                    <mml:mi>i</mml:mi>
                  </mml:msub>
                  <mml:mo>,</mml:mo>
                  <mml:mi>d</mml:mi>
                  <mml:mi>A</mml:mi>
                  <mml:msub>
                    <mml:mi>E</mml:mi>
                    <mml:mi>i</mml:mi>
                  </mml:msub>
                </mml:mrow>
                <mml:mo>]</mml:mo>
              </mml:mrow>
            </mml:mrow>
          </mml:math>
        </disp-formula>
        <p>allowing simultaneous assessment of particle-size dominance, radiative characteristics, and spectral variability.</p>
        <p>Scatter-distribution analysis was then performed in the FMF-SSA and FMF-SSA-dAE parameter spaces to identify aerosol clusters and evaluate the additional discriminatory capability provided by dAE. Correlation analyses were further used to assess relationships among the variables and infer aerosol mixing and aging processes. Regional comparisons between northern and southern African observation sites were conducted to evaluate differences in aerosol composition, transport, and spectral variability associated with contrasting atmospheric environments. The spatial patterns of the resulting clusters were interpreted in the context of dominant regional emission sources and long-range transport mechanisms ([<xref ref-type="bibr" rid="B14">14</xref>]; [<xref ref-type="bibr" rid="B11">11</xref>]; [<xref ref-type="bibr" rid="B16">16</xref>]).</p>
      </sec>
    </sec>
    <sec id="sec3">
      <title>3. Results and Discussion</title>
      <sec id="sec3dot1">
        <title>3.1. Trend in Aerosol Optical Depth (AOD)</title>
        <p><xref ref-type="fig" rid="fig2">Figure 2</xref> presents the relationship between FMF and SSA, with dAE represented as a color gradient. The distribution reveals considerable overlap among aerosol populations when only FMF and SSA are considered, confirming limitations previously reported in conventional aerosol discrimination frameworks ([<xref ref-type="bibr" rid="B11">11</xref>]). However, incorporation of dAE introduces additional spectral information that improves separation among aerosol clusters ([<xref ref-type="bibr" rid="B4">4</xref>]; [<xref ref-type="bibr" rid="B12">12</xref>]; [<xref ref-type="bibr" rid="B15">15</xref>]).</p>
        <p>Higher dAE values were predominantly associated with elevated FMF and moderate SSA conditions, indicating dominance of fine-mode aerosols characterized by strong spectral curvature ([<xref ref-type="bibr" rid="B13">13</xref>]) (<bold>Table 2</bold>). These aerosol characteristics are consistent with biomass burning and polluted continental aerosols commonly observed over Southern Africa during intense fire seasons ([<xref ref-type="bibr" rid="B14">14</xref>]; [<xref ref-type="bibr" rid="B15">15</xref>]). Conversely, lower or negative dAE values were concentrated under lower FMF conditions, reflecting dominance of coarse mineral dust aerosols typically transported from the Sahara Desert (<bold>Table 3</bold>) ([<xref ref-type="bibr" rid="B6">6</xref>]).</p>
        <p>The distribution pattern demonstrates that dAE effectively constrains aerosol size heterogeneity within FMF-SSA space and therefore reduces ambiguity associated with overlapping aerosol regimes ([<xref ref-type="bibr" rid="B16">16</xref>]). This enhanced discrimination capability is particularly important for African aerosol environments where aerosol mixing processes are highly dynamic and spatially heterogeneous ([<xref ref-type="bibr" rid="B5">5</xref>]; [<xref ref-type="bibr" rid="B15">15</xref>]).</p>
        <fig id="fig2">
          <label>Figure 2</label>
          <graphic xlink:href="https://html.scirp.org/file/2361758-rId29.jpeg?20260821024551" />
        </fig>
        <p>Figure 2. Relationships between FMF (500 nm), SSA (440 nm), and dAE (<italic>AE</italic><sub>440</sub><sub>-</sub><sub>675</sub>-<italic>AE</italic><sub>675</sub><sub>-</sub><sub>870nm</sub>) across African AERONET sites: (a) FMF-SSA (colored by dAE; dashed lines at FMF = 0.6 and SSA = 0.89), (b) FMF-dAE (dAE = 0 shown), and (c) SSA-dAE. Data are grouped into North and South Africa.</p>
        <p>Table 2. Interpretation of scatterplot relationships in the dAE-enhanced aerosol discrimination model.</p>
        <table-wrap id="tbl2">
          <label>Table 2</label>
          <table>
            <tbody>
              <tr>
                <td>
                  <bold>Scatter</bold>
                  <bold>Relationship</bold>
                </td>
                <td>
                  <bold>Major Observation</bold>
                </td>
                <td>
                  <bold>Aerosol</bold>
                  <bold>Implication</bold>
                </td>
                <td>
                  <bold>Interpretation</bold>
                </td>
              </tr>
              <tr>
                <td>FMF-SSA</td>
                <td>Significant overlap among aerosol clusters</td>
                <td>Conventional discrimination limitation</td>
                <td>Aerosol mixtures are difficult to separate using two parameters alone</td>
              </tr>
              <tr>
                <td>FMF-SSA-dAE</td>
                <td>Improved cluster separation after inclusion of dAE</td>
                <td>Enhanced aerosol discrimination</td>
                <td>dAE introduces sensitivity to spectral curvature</td>
              </tr>
              <tr>
                <td>FMF-dAE</td>
                <td>Positive relationship between FMF and dAE</td>
                <td>Fine-mode aerosol dominance</td>
                <td>Biomass burning and polluted aerosols exhibit stronger spectral curvature</td>
              </tr>
              <tr>
                <td>SSA-dAE</td>
                <td>Lower SSA associated with positive dAE</td>
                <td>Absorbing aerosol behavior</td>
                <td>Biomass burning aerosols dominate absorbing clusters</td>
              </tr>
              <tr>
                <td>Transitional Clusters</td>
                <td>Intermediate dAE and FMF values</td>
                <td>Mixed aerosol conditions</td>
                <td>Indicates aerosol mixing and long-range transport</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p>Table 3. Regional aerosol characteristics across Africa.</p>
        <table-wrap id="tbl3">
          <label>Table 3</label>
          <table>
            <tbody>
              <tr>
                <td>
                  <bold>Region</bold>
                </td>
                <td>
                  <bold>Dominant</bold>
                  <bold>Aerosol Type</bold>
                </td>
                <td>
                  <bold>FMF</bold>
                  <bold>Behavior</bold>
                </td>
                <td>
                  <bold>SSA</bold>
                  <bold>Behavior</bold>
                </td>
                <td>
                  <bold>dAE</bold>
                  <bold>Behavior</bold>
                </td>
                <td>
                  <bold>Dominant</bold>
                  <bold>Atmospheric Processes</bold>
                </td>
              </tr>
              <tr>
                <td>North Africa</td>
                <td>Mineral Dust</td>
                <td>Low FMF</td>
                <td>Moderate SSA</td>
                <td>Negative to near-zero dAE</td>
                <td>Saharan dust transport</td>
              </tr>
              <tr>
                <td>South Africa</td>
                <td>Biomass Burning /Polluted Continental</td>
                <td>High FMF</td>
                <td>Lower SSA</td>
                <td>Positive dAE</td>
                <td>Biomass burning emissions</td>
              </tr>
              <tr>
                <td>Transitional Regions</td>
                <td>Mixed Aerosols</td>
                <td>Moderate FMF</td>
                <td>Variable SSA</td>
                <td>Transitional dAE</td>
                <td>Dust-smoke interactions</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
      </sec>
      <sec id="sec3dot2">
        <title>3.2. FMF-dAE Relationship</title>
        <p>A clear positive relationship exists between the two parameters, indicating increasing spectral curvature with increasing fine-mode aerosol contribution (<xref ref-type="fig" rid="fig2">Figure 2</xref>). Fine-mode aerosols exhibited predominantly positive dAE values, reflecting stronger wavelength dependence associated with combustion-generated particles and secondary aerosols ([<xref ref-type="bibr" rid="B2">2</xref>]).</p>
        <p>Coarse-mode aerosols clustered near or below dAE = 0, consistent with weaker spectral variation typically associated with mineral dust particles (<xref ref-type="fig" rid="fig1">Figure 1</xref>) ([<xref ref-type="bibr" rid="B6">6</xref>]). The clearer separation observed in FMF-dAE space compared to FMF-SSA space demonstrated the sensitivity of dAE to aerosol size transitions and mixed aerosol conditions (<bold>Tables 2-4</bold>) ([<xref ref-type="bibr" rid="B16">16</xref>]; [<xref ref-type="bibr" rid="B15">15</xref>]).</p>
        <p>Table 4. Proposed aerosol classification characteristics in the dAE-enhanced framework.</p>
        <table-wrap id="tbl4">
          <label>Table 4</label>
          <table>
            <tbody>
              <tr>
                <td>
                  <bold>Aerosol Type</bold>
                </td>
                <td>
                  <bold>FMF</bold>
                  <bold>Characteristics</bold>
                </td>
                <td>
                  <bold>SSA</bold>
                  <bold>Characteristics</bold>
                </td>
                <td>
                  <bold>dAE</bold>
                  <bold>Characteristics</bold>
                </td>
                <td>
                  <bold>Dominant</bold>
                  <bold>Aerosol Sources</bold>
                </td>
              </tr>
              <tr>
                <td>Mineral Dust (DU)</td>
                <td>Low FMF</td>
                <td>Moderate to high SSA</td>
                <td>Negative or near-zero dAE</td>
                <td>Saharan desert dust</td>
              </tr>
              <tr>
                <td>Biomass Burning (BB)</td>
                <td>High FMF</td>
                <td>Low SSA</td>
                <td>Positive dAE</td>
                <td>Vegetation fires and smoke</td>
              </tr>
              <tr>
                <td>Polluted Continental (PC)</td>
                <td>High FMF</td>
                <td>Moderate SSA</td>
                <td>Positive dAE</td>
                <td>Urban-industrial emissions</td>
              </tr>
              <tr>
                <td>Mixed Aerosols (MXD)</td>
                <td>Moderate FMF</td>
                <td>Variable SSA</td>
                <td>Transitional dAE values</td>
                <td>Dust-smoke- pollution mixtures</td>
              </tr>
              <tr>
                <td>Marine Aerosols (MAR)</td>
                <td>Low to moderate FMF</td>
                <td>High SSA</td>
                <td>Near-zero dAE</td>
                <td>Sea salt and oceanic particles</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p>Several transitional data points were observed between the dominant clusters, indicating coexistence of fine and coarse aerosol populations under mixed atmospheric conditions ([<xref ref-type="bibr" rid="B11">11</xref>]). Such mixed aerosol states are common over Africa due to interactions between transported Saharan dust, biomass burning smoke, and urban-industrial emissions ([<xref ref-type="bibr" rid="B5">5</xref>]). The observed transitional structures further confirm the usefulness of dAE in identifying aerosol mixing processes that are not adequately resolved using conventional aerosol optical parameters alone ([<xref ref-type="bibr" rid="B14">14</xref>]).</p>
      </sec>
      <sec id="sec3dot3">
        <title>3.3. SSA-dAE Relationship</title>
        <p>Analysis of the relationship between SSA and dAE revealed lower SSA values, primarily associated with positive dAE values, indicating absorbing fine-mode aerosols dominated by biomass burning smoke and black carbon-rich particles (<xref ref-type="fig" rid="fig2">Figure 2</xref>) ([<xref ref-type="bibr" rid="B16">16</xref>]). These aerosols are known to exhibit enhanced absorption and strong spectral curvature due to their small particle sizes and combustion origin ([<xref ref-type="bibr" rid="B2">2</xref>]; [<xref ref-type="bibr" rid="B15">15</xref>]).</p>
        <p>Higher SSA values displayed broader dAE variability, reflecting mixtures of scattering and absorbing aerosol components under varying atmospheric conditions ([<xref ref-type="bibr" rid="B11">11</xref>]). The relatively compact clustering observed for absorbing aerosols suggested that dAE improves the identification of combustion-related aerosol populations that are often poorly separated using SSA alone (<bold>Table 5</bold>).</p>
        <p>Table 5. Advantages of the proposed dAE-enhanced aerosol discrimination model.</p>
        <table-wrap id="tbl5">
          <label>Table 5</label>
          <table>
            <tbody>
              <tr>
                <td>
                  <bold>Conventional FMF</bold>
                  <bold>-</bold>
                  <bold>SSA Model Limitation</bold>
                </td>
                <td>
                  <bold>Contribution of</bold>
                  <bold>dAE</bold>
                </td>
                <td>
                  <bold>Improvement Achieved</bold>
                </td>
              </tr>
              <tr>
                <td>Overlapping aerosol clusters</td>
                <td>Introduces spectral curvature sensitivity</td>
                <td>Improved aerosol separation</td>
              </tr>
              <tr>
                <td>Poor identification of mixed aerosols</td>
                <td>Captures aerosol size heterogeneity</td>
                <td>Better mixed aerosol detection</td>
              </tr>
              <tr>
                <td>Limited sensitivity to aerosol transitions</td>
                <td>Resolves fine-to-coarse particle variability</td>
                <td>Enhanced transitional aerosol characterization</td>
              </tr>
              <tr>
                <td>Ambiguity in absorbing aerosol classification</td>
                <td>Links absorption to spectral behavior</td>
                <td>Improved biomass burning aerosol identification</td>
              </tr>
              <tr>
                <td>Reduced regional discrimination capability</td>
                <td>Enhances spectral differentiation</td>
                <td>Better regional aerosol interpretation across Africa</td>
              </tr>
            </tbody>
          </table>
        </table-wrap>
        <p>Regional contrasts were also evident within the SSA-dAE relationship. Southern African sites exhibited stronger fine-mode absorbing signatures associated with seasonal biomass burning emissions, whereas North African stations displayed broader coarse-mode variability linked to Saharan dust transport (<bold>Table 4</bold>) ([<xref ref-type="bibr" rid="B5">5</xref>]). These findings demonstrated that dAE provides additional discriminatory power for interpreting aerosol absorptive behavior and aerosol source characteristics across Africa ([<xref ref-type="bibr" rid="B6">6</xref>]).</p>
      </sec>
      <sec id="sec3dot4">
        <title>3.4. Implications of the dAE-Enhanced Aerosol Discrimination Model</title>
        <p>The proposed dAE-enhanced aerosol discrimination model demonstrates improved capability in resolving aerosol mixtures compared to conventional two-parameter approaches (<bold>Table 5</bold>).</p>
        <p>Incorporation of dAE introduces sensitivity to spectral curvature and aerosol size transitions, thereby enhancing aerosol cluster separation and reducing classification ambiguity. The improved aerosol discrimination achieved in this study has important implications for satellite aerosol retrieval validation, climate modeling, radiative forcing estimation, and air quality assessment ([<xref ref-type="bibr" rid="B11">11</xref>]). Enhanced aerosol typing frameworks are particularly valuable over Africa, where aerosol complexity and limited observational coverage continue to challenge atmospheric modeling efforts ([<xref ref-type="bibr" rid="B14">14</xref>]).</p>
      </sec>
    </sec>
    <sec id="sec4">
      <title>4. Summary and Conclusion</title>
      <p>This study developed a novel dAE-enhanced aerosol optical discrimination model using FMF, SSA, and dAE derived from AERONET observations across African sites. The results demonstrate that incorporation of dAE significantly improves aerosol separation within conventional FMF-SSA space by introducing sensitivity to spectral curvature and aerosol size heterogeneity. The FMF-dAE relationship revealed clear separation between fine-mode and coarse-mode aerosol populations, while the SSA-dAE relationship improved identification of absorbing aerosol regimes associated with biomass burning emissions. Regional analysis further highlighted strong contrasts between North African dust-dominated environments and Southern African biomass burning aerosol regimes.</p>
      <p>Looking at it as a whole, the findings confirmed that dAE is a valuable supplementary parameter for aerosol optical discrimination and substantially enhances characterization of mixed aerosol environments over Africa. The proposed framework has provided a promising basis for future aerosol classification studies, satellite retrieval improvement, and aerosol radiative forcing assessments under complex atmospheric conditions.</p>
    </sec>
    <sec id="sec5">
      <title>Acknowledgements</title>
      <p>The authors acknowledge the NASA Aerosol Robotic Network (AERONET) and all principal investigators and site operators who contributed to the establishment, maintenance, quality assurance, and dissemination of the aerosol data used in this study. Their sustained efforts in providing long-term, standardized, and freely accessible aerosol observations have greatly supported this research. We are particularly grateful to the managers and technical teams of the selected African AERONET stations for ensuring continuous data availability and quality.</p>
    </sec>
    <sec id="sec6">
      <title>Author Contributions</title>
      <p><bold>Situma</bold><bold>Y</bold><bold>onah:</bold> conceptualization, data curation, formal analysis, methodology, visualization, and writing original draft. <bold>Makokha</bold><bold>J</bold><bold>ohn:</bold> supervision, methodology, validation, review, and editing. <bold>Khakina Peter:</bold> data curation, formal analysis, investigation, and validation. <bold>Khamala Geoffrey:</bold> data curation, formal analysis, investigation, review, and editing. </p>
    </sec>
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