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  <front>
    <journal-meta>
      <journal-id journal-id-type="publisher-id">msce</journal-id>
      <journal-title-group>
        <journal-title>Journal of Materials Science and Chemical Engineering</journal-title>
      </journal-title-group>
      <issn pub-type="epub">2327-6053</issn>
      <issn pub-type="ppub">2327-6045</issn>
      <publisher>
        <publisher-name>Scientific Research Publishing</publisher-name>
      </publisher>
    </journal-meta>
    <article-meta>
      <article-id pub-id-type="doi">10.4236/msce.2026.141002</article-id>
      <article-id pub-id-type="publisher-id">msce-148874</article-id>
      <article-categories>
        <subj-group>
          <subject>Article</subject>
        </subj-group>
        <subj-group>
          <subject>Chemistry</subject>
          <subject>Materials Science</subject>
        </subj-group>
      </article-categories>
      <title-group>
        <article-title>Preparation of Eu3+-Doped Ca0.8Yb0.2F2.2 as a Fluorescent Probe and Its Application in Detecting Cr O 4 2− and C r 2 O 7 2− Ions</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <name name-style="western">
            <surname>Zhou</surname>
            <given-names>Lexiang</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <name name-style="western">
            <surname>Lei</surname>
            <given-names>Lu</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <name name-style="western">
            <surname>Qu</surname>
            <given-names>Xiao</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author" corresp="yes">
          <name name-style="western">
            <surname>Hu</surname>
            <given-names>Shanshan</given-names>
          </name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
      </contrib-group>
      <aff id="aff1"><label>1</label> School of Chemistry and Chemical Engineering, Southwest University, Chongqing, China </aff>
      <author-notes>
        <fn fn-type="conflict" id="fn-conflict">
          <p>The authors assert that there are no conflicts of interest about the publishing of this work.</p>
        </fn>
      </author-notes>
      <pub-date pub-type="epub">
        <day>16</day>
        <month>01</month>
        <year>2026</year>
      </pub-date>
      <pub-date pub-type="collection">
        <month>01</month>
        <year>2026</year>
      </pub-date>
      <volume>14</volume>
      <issue>01</issue>
      <fpage>15</fpage>
      <lpage>26</lpage>
      <history>
        <date date-type="received">
          <day>15</day>
          <month>12</month>
          <year>2025</year>
        </date>
        <date date-type="accepted">
          <day>13</day>
          <month>01</month>
          <year>2026</year>
        </date>
        <date date-type="published">
          <day>16</day>
          <month>01</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/msce.2026.141002">https://doi.org/10.4236/msce.2026.141002</self-uri>
      <abstract>
        <p>The accurate detection of hexavalent chromium (Cr(VI)) is crucial for environmental protection and public health. Rare earth fluorides have attracted considerable attention as fluorescent sensing materials due to their distinctive properties, including low lattice phonon energy, exceptional chemical stability and long fluorescence lifetime. This study reports the successful one-step hydrothermal synthesis of a Eu<sup>3+</sup>-doped Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub> fluorescent probe with excellent aqueous dispersibility. The obtained probe showed high sensitivity towards <inline-formula><mml:math display="inline"></mml:math></inline-formula></p>
        <p>CrO</p>
        <p>4</p>
        <p>2−</p>
        <p>and <inline-formula><mml:math display="inline"></mml:math></inline-formula></p>
        <p>Cr</p>
        <p>2</p>
        <p>O</p>
        <p>7</p>
        <p>2−</p>
        <p>ions, achieving detection limits of 1.45 µM and 1.50 µM. The obtained probe exhibited remarkable stability across a wide pH range (3 - 11) and strong anti-interference capability, confirming its suitability for analyzing real water samples. Owing to its robust performance and straightforward operation, this fluorescent probe presents a promising approach for efficient monitoring of trace Cr(VI) contaminants in aqueous environments.</p>
      </abstract>
      <kwd-group kwd-group-type="author-generated" xml:lang="en">
        <kwd>Fluorescent Probe</kwd>
        <kwd>Rare Earth Fluorides</kwd>
        <kwd>Cr(VI) Detection</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec1">
      <title>1. Introduction</title>
      <p>Chromium (Cr) is a pervasive heavy metal pollutant posing significant risks to ecosystems and human health. In environmental and industrial wastewater contexts, chromium primarily exists in two stable oxidation states: the less toxic trivalent form (Cr(III)) and the highly toxic hexavalent form (Cr(VI)) [<xref ref-type="bibr" rid="B1">1</xref>]-[<xref ref-type="bibr" rid="B3">3</xref>]. Cr(VI) species, predominantly occurring as oxyanions such as chromate (<inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ), hydrogen chromate (<inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> HCrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mo> − </mml:mo></mml:msubsup></mml:mrow></mml:math></inline-formula> ), and dichromate (<inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ) depending on pH, are notably soluble and mobile in water systems [<xref ref-type="bibr" rid="B4">4</xref>]-[<xref ref-type="bibr" rid="B8">8</xref>]. Recognized for its potent toxicity and carcinogenicity, Cr(VI) is classified as a Group 1 human carcinogen by the International Agency for Research on Cancer (IARC) [<xref ref-type="bibr" rid="B9">9</xref>][<xref ref-type="bibr" rid="B10">10</xref>]. Human exposure, often through industrial discharges, can lead to severe health issues including dermatological irritation, respiratory impairments, ocular damage, and gastrointestinal disorders. At the molecular level, Cr(VI) induces oxidative stress by interfering with cellular redox processes, promotes DNA adduct formation, and can cause chromosomal aberrations, ultimately increasing cancer risk [<xref ref-type="bibr" rid="B11">11</xref>][<xref ref-type="bibr" rid="B12">12</xref>].</p>
      <p>Consequently, the effective monitoring and removal of Cr(VI) from drinking water and groundwater sources is imperative, particularly its anionic forms (<inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ). Regulatory bodies worldwide have established stringent limits; for instance, the U.S. Environmental Protection Agency (EPA) sets a maximum contaminant level (MCL) of 0.1 mg/L for total chromium [<xref ref-type="bibr" rid="B13">13</xref>], while Chinese standards (GB 5749-2006) impose a stricter limit of 0.05 mg/L specifically for Cr(VI) [<xref ref-type="bibr" rid="B14">14</xref>]. This underscores the urgent need for developing reliable, sensitive, and selective methods for Cr(VI) detection in water. </p>
      <p>Conventional techniques for chromium analysis, such as Flame Atomic Absorption Spectrometry (FAAS), Graphite Furnace Atomic Absorption Spectrometry (GFAAS), Inductively Coupled Plasma-based methods (ICP-OES, ICP-MS), and X-ray Fluorescence (XRF), offer precision but often require sophisticated instrumentation, extensive sample preparation, and skilled operation, limiting their field applicability [<xref ref-type="bibr" rid="B15">15</xref>]-[<xref ref-type="bibr" rid="B17">17</xref>]. In contrast, fluorescence-based sensing has emerged as a powerful alternative due to its inherent advantages of high sensitivity, selectivity, rapid response, and operational simplicity. While numerous fluorescent probes for chromium detection have been explored, and most of them are based on organic fluorophores. Recent efforts have focused on designing novel probes for enhanced Cr(VI) selectivity and sensitivity. For example, Subash <italic>et al.</italic> developed a water-compatible N-aryl carbamate-substituted quinoxaline sensor for Cr(VI) with a quantum yield of 0.26, emitting blue-green fluorescence at 498 nm [<xref ref-type="bibr" rid="B18">18</xref>]. Wang <italic>et al.</italic> fabricated a composite film incorporating copper nanoclusters for visual and ratiometric fluorescence detection of Cr(VI) [<xref ref-type="bibr" rid="B19">19</xref>]. Narasimhappa <italic>et al.</italic> have reported aggregation-induced emission (AIE)-active probes acting as “turn-off” sensors for Cr(VI) and Fe(III), and naphthalene-functionalized metal-organic frameworks (MOFs) for sensing these ions [<xref ref-type="bibr" rid="B20">20</xref>].</p>
      <p>However, organic probes frequently suffer from limitations such as potential toxicity, poor photostability, or inadequate water solubility, hindering their practical deployment. Inorganic nanomaterials, particularly those doped with lanthanide ions, offer a compelling solution due to their superior photophysical properties—high quantum yield, long luminescence lifetime, excellent photostability and comparatively low toxicity [<xref ref-type="bibr" rid="B21">21</xref>]-[<xref ref-type="bibr" rid="B24">24</xref>]. Among these, rare earth fluorides stand out as promising host matrices for fluorescent sensors, benefiting from low phonon energies that minimize non-radiative decay, high chemical stability [<xref ref-type="bibr" rid="B25">25</xref>][<xref ref-type="bibr" rid="B26">26</xref>] and relatively straightforward synthesis routes like hydrothermal method that often yields products with good aqueous dispersibility [<xref ref-type="bibr" rid="B27">27</xref>][<xref ref-type="bibr" rid="B28">28</xref>].</p>
      <p>Herein, we present the hydrothermal synthesis of a Eu<sup>3+</sup>-doped Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub> fluorescent probe exhibiting excellent water dispersibility. The Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21% Eu<sup>3+</sup> material shown stable luminescence and phase integrity in aqueous solutions from pH = 3 to pH = 11. The probe serves as a highly selective and sensitive fluorescent sensor for <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ions via a quenching mechanism.</p>
    </sec>
    <sec id="sec2">
      <title>2. Experimental Section</title>
      <sec id="sec2dot1">
        <title>2.1. Materials and Synthesis</title>
        <p>Ytterbium oxide (Yb<sub>2</sub>O<sub>3</sub>, 99.99%), Europium oxide (Eu<sub>2</sub>O<sub>3</sub>, 99.99%), Calcium chloride (CaCl<sub>2</sub>, AR), Nitric acid (HNO<sub>3</sub>, AR), Hydrochloric acid (HCl, AR), Ammonium fluoride (NH<sub>4</sub>F, AR) and Ethanol absolute (C<sub>2</sub>H<sub>5</sub>OH, AR).</p>
        <p>The Ca<sub>0.8</sub>Yb<sub>(</sub><sub>0.2-</sub><sub>x)</sub>F<sub>2.2</sub>:x%Eu<sup>3+</sup> samples were synthesized hydrothermally. For the representative Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> sample, 2 mmol of CaCl<sub>2</sub> (dissolved in 1 M solution, 2000 µL) was added to 20 mL of deionized water in a 100 mL beaker. Under vigorous stirring, 0.79 mmol of Yb(NO<sub>3</sub>)<sub>3</sub> (1 M, 790 µL) and 0.21 mmol of Eu(NO<sub>3</sub>)<sub>3</sub> (1 M, 210 µL) were added sequentially. The mixture was stirred for 20 minutes to ensure homogeneity. Subsequently, 7 mmol of NH<sub>4</sub>F (4 M, 1750 µL) was added dropwise, and stirring continued for another 30 minutes, resulting in a milky white suspension. This suspension was transferred into a 50 mL Teflon-lined stainless-steel autoclave and heated at 180˚C for 12 hours. After natural cooling to room temperature, the resulting product was collected by centrifugation (5000 rpm), washed thoroughly with deionized water and ethanol, and finally dried at 60˚C in a vacuum oven for 6 hours.</p>
      </sec>
      <sec id="sec2dot2">
        <title>2.2. Characterization</title>
        <p>Powder X-ray diffraction (PXRD) patterns were acquired using a MSALNDS diffractometer (Beijing Purkinje General Instrument) with Cu K<italic>α</italic> radiation (<italic>λ</italic> = 0.154 nm, 36 kV, 20 mA), scanning from 10˚ to 90˚ (2<italic>θ</italic>). Morphological characterization and elemental analysis (EDS and mapping) were performed using a Sigma 500/10102 Field Emission Scanning Electron Microscope (Carl Zeiss, Germany). Photoluminescence spectra (excitation and emission) were recorded on an FLS fluorescence spectrometer (Edinburgh Instruments, UK).</p>
      </sec>
    </sec>
    <sec id="sec3">
      <title>3. Results and Discussion</title>
      <sec id="sec3dot1">
        <title>3.1. Morphology, Phase and Luminescence</title>
        <p>The phase purity and crystal structure of the synthesized Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:x%Eu<sup>3+</sup> powder were confirmed by X-ray diffraction (XRD). As shown in <xref ref-type="fig" rid="fig1">Figure 1</xref>, all diffraction peaks align perfectly with the reference pattern for Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub> (JCPDS 87-0978), indicating the successful formation of the desired crystalline phase without detectable impurities. Elemental composition and distribution were analyzed using Energy Dispersive X-ray Spectroscopy (EDS). The EDS spectrum (<xref ref-type="fig" rid="fig2">Figure 2(a)</xref>) confirms the presence of Ca, Yb, F, and Eu elements. Furthermore, elemental mapping (<xref ref-type="fig" rid="fig2">Figures 2(b)-(f)</xref>) reveals a homogeneous distribution of all these elements throughout the nanoparticles, providing strong evidence for the successful incorporation of Eu<sup>3+</sup> ions into the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub> host lattice.</p>
        <p>To optimize the luminescence output, samples with varying Eu<sup>3+</sup> doping concentrations were synthesized. Under 392 nm excitation, the emission spectra (<xref ref-type="fig" rid="fig3">Figure 3(a)</xref>) are dominated by the characteristic intra-4f transitions of Eu<sup>3+</sup> (<sup>5</sup>D₀ → <sup>7</sup>FJ, J = 1 - 4). The dependence of the integrated emission intensity on Eu<sup>3+</sup> concentration is plotted in <xref ref-type="fig" rid="fig3">Figure 3(b)</xref>. The intensity initially increases with doping concentration, reaching a maximum at 21%Eu<sup>3+</sup>, beyond which the quenching occurs. This phenomenon is attributed to enhanced non-radiative energy transfer between neighboring Eu<sup>3+</sup> ions at shorter inter-ionic distances, prevalent at higher doping levels. Therefore, the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> sample, exhibiting the strongest luminescence, was selected for all subsequent sensing experiments.</p>
        <fig id="fig1">
          <label>Figure 1</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId45.jpeg?20260116105451" />
        </fig>
        <p><bold>Figure 1</bold><bold>.</bold>XRD patterns of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:x%Eu (x = 15, 18, 21, 24, and 28) phosphors.</p>
        <fig id="fig2">
          <label>Figure 2</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId46.jpeg?20260116105451" />
        </fig>
        <p><bold>Figure 2</bold><bold>.</bold>(a) EDS spectrum and (b-f) elemental mapping of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> phosphor.</p>
        <fig id="fig3">
          <label>Figure 3</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId47.jpeg?20260116105451" />
        </fig>
        <p><bold>Figure 3</bold><bold>.</bold>(a) Excitation and emission spectra of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> and (b) Effect of Eu<sup>3+</sup> concentration on the emission intensity.</p>
      </sec>
      <sec id="sec3dot2">
        <title>3.2. Aqueous Stability and Dispersion</title>
        <p>The hydrothermal synthesis method yielded Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub> material with good aqueous dispersibility, which typically improves with lower crystallinity. Furthermore, as a rare-earth fluoride, Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub> maintains excellent chemical stability even at relatively low crystallinity levels. Consequently, the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> powder demonstrates both favorable dispersibility and remarkable pH stability in aqueous environments.</p>
        <p>To evaluate the luminescence stability of the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> aqueous suspension, emission spectra were systematically recorded at 20-second intervals. The pH-dependent luminescence behavior was investigated by measuring emission spectra from uniformly mixed suspensions adjusted to different pH values. As shown in <xref ref-type="fig" rid="fig4">Figure 4(a)</xref>, the luminescence intensity of the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> suspension remained essentially unchanged over a 100-second monitoring period. <xref ref-type="fig" rid="fig4">Figure 4(b)</xref> demonstrates that the luminescence intensity maintained remarkable consistency across a broad pH range from 3 to 11.</p>
        <p>Notably, the crystalline phase of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> powder remained intact after immersion in aqueous solution. The long-term stability assessment (<xref ref-type="fig" rid="fig5">Figure 5</xref>) revealed excellent retention of luminescence properties, with minimal degradation observed even after 50 days of suspension storage. This combination of phase stability and aqueous dispersibility establishes the fundamental basis for employing Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> powder as a reliable sensing platform for analyte detection in aqueous environments [<xref ref-type="bibr" rid="B29">29</xref>][<xref ref-type="bibr" rid="B30">30</xref>].</p>
      </sec>
      <sec id="sec3dot3">
        <title>3.3. Selectivity and Sensitivity</title>
        <p>The selectivity of the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> probe towards Cr(VI) anions was investigated by monitoring the fluorescence response upon addition of various potential interfering ions, including <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CO </mml:mtext></mml:mrow><mml:mn> 3 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , <inline-formula><mml:math display="inline"><mml:mrow><mml:msup><mml:mtext> F </mml:mtext><mml:mo> − </mml:mo></mml:msup></mml:mrow></mml:math></inline-formula> , <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> PO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 3 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> NO </mml:mtext></mml:mrow><mml:mn> 3 </mml:mn><mml:mo> − </mml:mo></mml:msubsup></mml:mrow></mml:math></inline-formula> , <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> SO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , I<sup>−</sup>, Br<sup>−</sup>, and<inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> ClO </mml:mtext></mml:mrow><mml:mn> 3 </mml:mn><mml:mo> − </mml:mo></mml:msubsup></mml:mrow></mml:math></inline-formula> . As depicted in <xref ref-type="fig" rid="fig6">Figure 6(a)</xref>, the introduction of these ions induced negligible changes in the fluorescence intensity compared to the blank suspension. In stark contrast, the addition of either <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> or <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> resulted in significant fluorescence quenching. The histogram in <xref ref-type="fig" rid="fig6">Figure 6(b)</xref>, representing the emission intensity at 592 nm, clearly visualizes this high selectivity, affirming the probe’s specific recognition capability for <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> over other common anions.</p>
        <fig id="fig4">
          <label>Figure 4</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId68.jpeg?20260116105452" />
        </fig>
        <p><bold>Figure 4</bold><bold>.</bold>(a) Emission spectra of the aqueous suspension of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> powder recorded at different time intervals; (b) Emission spectra of the suspension at different pH values.</p>
        <fig id="fig5">
          <label>Figure 5</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId69.jpeg?20260116105452" />
        </fig>
        <p><bold>Figure 5</bold><bold>.</bold>Emission spectra recorded on the 1st day and the 50th day after suspension preparation.</p>
        <p>The sensitivity of the probe was quantitatively evaluated by titrating the suspension with increasing concentrations of <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ions. As shown in <xref ref-type="fig" rid="fig7">Figure 7(a)</xref> and <xref ref-type="fig" rid="fig7">Figure 7(b)</xref>, the fluorescence intensity progressively decreased with higher analyte concentrations. The quenching data were analyzed using the Stern-Volmer equation: I<sub>0</sub>/I = 1 + K<sub>SV</sub> [M], where I<sub>0</sub> and I are the fluorescence intensities in the absence and presence of the quencher, respectively, K<sub>SV</sub> is the Stern-Volmer quenching constant, and [M] is the molar concentration of the quencher. The plots of I<sub>0</sub>/I versus quencher concentration ([<inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ] or [<inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ]) exhibited good linearity (R<sup>2</sup> = 1 for <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , R<sup>2</sup> = 0.996 for <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ), as shown in <xref ref-type="fig" rid="fig7">Figure 7(c)</xref> and <xref ref-type="fig" rid="fig7">Figure 7(d)</xref>. The K<sub>SV</sub> values were determined to be 0.00867 µM<sup>−1</sup> for <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and 0.0084 µM<sup>−1</sup> for<inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> . The limits of detection (LOD), calculated based on LOD = 3<italic>σ</italic>/S (where <italic>σ</italic> is the standard deviation of the blank signal and S is the slope of the calibration curve), were found to be 1.45 µM for <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and 1.50 µM for<inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> . These LODs values demonstrate the high sensitivity of the probe.</p>
        <fig id="fig6">
          <label>Figure 6</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId90.jpeg?20260116105452" />
        </fig>
        <p><bold>Figure 6</bold><bold>.</bold>(a) Emission spectra of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> phosphor mixed with different anions (l<sub>ex</sub>= 392 nm); (b) Comparison of the emission intensity at 592 nm for solutions containing different ions.</p>
        <fig id="fig7">
          <label>Figure 7</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId91.jpeg?20260116105452" />
        </fig>
        <p><bold>Figure 7</bold><bold>.</bold>Stern-Volmer plots for the detection of <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ions using the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> suspension; (a) Emission spectra of the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> suspension at different concentrations of <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ; (b) Emission spectra of the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> suspension at different concentrations of <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ; (c) Stern-Volmer plot for<inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ; (d) Stern-Volmer plot for <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> .</p>
      </sec>
      <sec id="sec3dot4">
        <title>3.4. Quenching Mechanism</title>
        <p>To elucidate the quenching mechanism of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> luminescence by <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ions, systematic characterization was conducted (<xref ref-type="fig" rid="fig8">Figure 8</xref>). Phase stability was first investigated by immersing the phosphor in 0.01 mol/L <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> solutions for 24 hours. After centrifugation and drying at 60˚C, XRD patterns revealed that the diffraction peaks of the treated samples remained sharp and closely matched the reference pattern for Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>. This observation confirmed that the crystal structure of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> remained unaltered, thereby ruling out structural alteration of the phosphor as the cause of the luminescence quenching by <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ions.</p>
        <p>UV-Vis absorption spectroscopy revealed that both <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ions exhibit strong absorption bands in the 200 - 800 nm range (<xref ref-type="fig" rid="fig9">Figure 9</xref>). This absorption profile significantly overlaps with the excitation spectrum of the Ca<sub>0</sub><sub>.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> probe. This spectral overlap suggests that the primary quenching mechanism is the inner filter effect (IFE). The target oxyanions compete with the fluorophore for the excitation light, effectively reducing the number of photons absorbed by the Eu<sup>3+</sup> ions in the probe, thereby leading to the observed decrease in fluorescence intensity.</p>
        <fig id="fig8">
          <label>Figure 8</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId120.jpeg?20260116105452" />
        </fig>
        <p><bold>Figure 8</bold><bold>.</bold>XRD patterns of Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> phosphor after immersion in <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> aqueous solutions and subsequent washing/drying.</p>
      </sec>
      <sec id="sec3dot5">
        <title>3.5. Anti-Interference</title>
        <p>To assess anti-interference capability, solutions containing <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> or <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> were mixed with solutions of potential interfering ions (<inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CO </mml:mtext></mml:mrow><mml:mn> 3 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , <inline-formula><mml:math display="inline"><mml:mrow><mml:msup><mml:mtext> F </mml:mtext><mml:mo> − </mml:mo></mml:msup></mml:mrow></mml:math></inline-formula> , <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> PO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 3 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> NO </mml:mtext></mml:mrow><mml:mn> 3 </mml:mn><mml:mo> − </mml:mo></mml:msubsup></mml:mrow></mml:math></inline-formula> , <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> SO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , I<sup>−</sup>, Br<sup>−</sup>, <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> ClO </mml:mtext></mml:mrow><mml:mn> 3 </mml:mn><mml:mo> − </mml:mo></mml:msubsup></mml:mrow></mml:math></inline-formula> ) at a 1:1 concentration ratio. For the fluorescence measurement, 3 mL of the probe suspension (3 mg/mL) was mixed with 100 µL of the mixed ion solution (0.01 M for each ion). The fluorescence emission intensity was then measured and compared to that of the blank suspension and the suspension containing only the target Cr(VI) anion. As shown in <xref ref-type="fig" rid="fig10">Figure 10</xref>, the presence of interfering ions did not significantly alter the pronounced quenching effect caused by <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> or<inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , confirming the high selectivity of the probe for practical applications.</p>
        <fig id="fig9">
          <label>Figure 9</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId139.jpeg?20260116105453" />
        </fig>
        <p><bold>Figure 9</bold><bold>.</bold>UV-Vis Absorption Spectra of <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> Ions and the excitation spectrum of the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.</sub><sub>2</sub>:Eu<sup>3+</sup> phosphor</p>
        <fig id="fig10">
          <label>Figure 10</label>
          <graphic xlink:href="https://html.scirp.org/file/1741492-rId144.jpeg?20260116105453" />
        </fig>
        <p><bold>Figure 10</bold><bold>.</bold>Relative luminescence intensity of the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21%Eu<sup>3+</sup> suspension after addition of target and interfering ions.</p>
      </sec>
    </sec>
    <sec id="sec4">
      <title>4. Conclusion</title>
      <p>In summary, a highly water-dispersible Eu<sup>3+</sup>-doped Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub> fluorescent probe was successfully synthesized via a facile one-step hydrothermal method. The optimal luminescence intensity was achieved with a Eu<sup>3+</sup> doping concentration of 21%. The probe serves as a selective sensor for toxic Cr(VI) oxyanions (<inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ) in water, operating primarily through an inner filter effect mechanism where the analytes compete for excitation energy. It demonstrates high sensitivity, with detection limits of 1.45 µM and 1.50 µM for <inline-formula><mml:math display="inline"><mml:mrow><mml:msubsup><mml:mrow><mml:mtext> CrO </mml:mtext></mml:mrow><mml:mn> 4 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math display="inline"><mml:mrow><mml:msub><mml:mrow><mml:mtext> Cr </mml:mtext></mml:mrow><mml:mtext> 2 </mml:mtext></mml:msub><mml:msubsup><mml:mtext> O </mml:mtext><mml:mn> 7 </mml:mn><mml:mrow><mml:mn> 2 </mml:mn><mml:mo> − </mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> , respectively, values that are significantly lower than the regulatory limit for drinking water. The material exhibits exceptional long-term stability in water and maintains its performance over a wide pH range (3 - 11) with excellent selectivity against common interfering ions. Combined with its simple synthesis and straightforward operation, the Ca<sub>0.8</sub>Yb<sub>0.2</sub>F<sub>2.2</sub>:21% Eu<sup>3+</sup> fluorescent probe represents a reliable and effective tool for the on-site monitoring of trace-level Cr(VI) contamination in real water samples. Furthermore, the design strategy presented here offers valuable insights for developing advanced sensing materials targeting other hazardous heavy metal ions.</p>
    </sec>
    <sec id="sec5">
      <title>Fund</title>
      <p>This project was financially sponsored the Natural Science Foundation of Chongqing (cstc2020jcyj-msxmX0332).</p>
    </sec>
  </body>
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