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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Environ. Sci.</journal-id>
<journal-title>Frontiers in Environmental Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Environ. Sci.</abbrev-journal-title>
<issn pub-type="epub">2296-665X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">1112522</article-id>
<article-id pub-id-type="doi">10.3389/fenvs.2023.1112522</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Environmental Science</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Compositional variations in algal organic matter during distinct growth phases in karst water</article-title>
<alt-title alt-title-type="left-running-head">Tian et al.</alt-title>
<alt-title alt-title-type="right-running-head">
<ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3389/fenvs.2023.1112522">10.3389/fenvs.2023.1112522</ext-link>
</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Tian</surname>
<given-names>Liye</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="fn" rid="fn1">
<sup>&#x2020;</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/2152813/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Zhang</surname>
<given-names>Zhiwei</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="fn" rid="fn1">
<sup>&#x2020;</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/2119879/overview"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Wang</surname>
<given-names>Zhikang</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1980828/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Zhang</surname>
<given-names>Ping</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1439625/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Xiong</surname>
<given-names>Chao</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Kuang</surname>
<given-names>Ye</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Peng</surname>
<given-names>Xingyi</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Yu</surname>
<given-names>Mengxin</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Qian</surname>
<given-names>Yu</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>College of Eco-Environmental Engineering</institution>, <institution>Guizhou Minzu University</institution>, <addr-line>Guizhou</addr-line>, <country>China</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Guiyang Institute of Information Science and Technology</institution>, <addr-line>Guiyang</addr-line>, <country>China</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>Second Branch of Environmental Monitoring Station</institution>, <addr-line>Guiyang</addr-line>, <country>China</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>
<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1773158/overview">Rong Mao</ext-link>, Jiangxi Agricultural University, China</p>
</fn>
<fn fn-type="edited-by">
<p>
<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2049134/overview">Zhidan Wen</ext-link>, Northeast Institute of Geography and Agroecology (CAS), China</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2043667/overview">Muhua Feng</ext-link>, Nanjing Institute of Geography and Limnology (CAS), China</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Zhikang Wang, <email>wangzhikang@gzmu.edu.cn</email>
</corresp>
<fn fn-type="equal" id="fn1">
<label>
<sup>&#x2020;</sup>
</label>
<p>These authors have contributed equally to this work</p>
</fn>
<fn fn-type="other">
<p>This article was submitted to Freshwater Science, a section of the journal Frontiers in Environmental Science</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>10</day>
<month>02</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>11</volume>
<elocation-id>1112522</elocation-id>
<history>
<date date-type="received">
<day>30</day>
<month>11</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>06</day>
<month>01</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2023 Tian, Zhang, Wang, Zhang, Xiong, Kuang, Peng, Yu and Qian.</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Tian, Zhang, Wang, Zhang, Xiong, Kuang, Peng, Yu and Qian</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p>
</license>
</permissions>
<abstract>
<p>Inland surface water plays an important role in global carbon cycling, which responds to transformation between dissolved inorganic carbon (DIC) and dissolved organic carbon (DOC). Studies have shown that algae in karst lakes and reservoirs can convert DIC to organic matter (OM) and form stable carbon sinks <italic>via</italic> photosynthesis. However, the pathways of conversion of inorganic carbon to organic carbon during algal growth remain unclear and need further investigation. In this study, spectroscopic techniques were applied to investigate the variations in algal organic matter (AOM) composition in the growth metabolism of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> under simulated karst water condition. The results showed that algal extracellular organic matter (EOM) contained high DIC concentration during the adaptation phase, which formed the carbon source for algal photosynthesis. In addition, DOC in algae increased after entering the stationary phase, while more OM was released into water. As algal growth proceeded, the amino groups in EOM were consumed to produce more aromatic protein-like material, while more lipid material was produced in intracellular organic matter (IOM). The spectral characterization results could intuitively determine AOM dynamics in different growth stages of algae, which can be used for establishing effective approaches for detecting organic carbon variations and responding to regional carbon cycling in karst water.</p>
</abstract>
<kwd-group>
<kwd>algal organic matter</kwd>
<kwd>karst water</kwd>
<kwd>carbon cycle</kwd>
<kwd>growth phases of algae</kwd>
<kwd>dissolved inorganic carbon</kwd>
</kwd-group>
</article-meta>
</front>
<body>
<sec id="s1">
<title>1 Introduction</title>
<p>With industrial development, a significant amount of CO<sub>2</sub> is emitted into the atmosphere (<xref ref-type="bibr" rid="B19">Kumar et al., 2011</xref>), causing a series of environmental pollution problems, eventually leading to global climate change (<xref ref-type="bibr" rid="B38">Rogelj et al., 2016</xref>). Recently, China has been actively pursuing the goals of achieving &#x201c;peak carbon dioxide emissions&#x201d; and &#x201c;carbon neutrality,&#x201d; which will help improve the present situation of global climate change (<xref ref-type="bibr" rid="B20">Li et al., 2016</xref>). Global carbon cycle refers to the transformation and flow of carbon through the Earth system (atmosphere, oceans, and land) (<xref ref-type="bibr" rid="B50">Yang et al., 2020</xref>). As a vital part of the global carbon cycle, the biological pump mechanism was first proposed for oceans (<xref ref-type="bibr" rid="B39">Shackleton, 1985</xref>). Over time, studies have shown that inland water bodies (rivers, lakes, <italic>etc.</italic>) also manifest a critical role as a carbon source and sink in the global carbon cycle, and hard-water lakes are more advantageous in carbon sequestration (<xref ref-type="bibr" rid="B24">Liang and Balser, 2011</xref>). The intense biological pump effect of aquatic photosynthetic organisms in karst lakes can fix part of the carbonate weathering carbon sink flux and form a stable carbon sink (<xref ref-type="bibr" rid="B28">Liu and Dreybrodt, 2015</xref>).</p>
<p>Karst lakes and reservoirs are major surface water bodies in karst landscapes and contain high concentrations of dissolved inorganic carbon (DIC), which can provide abundant carbon for photosynthesis in aquatic organisms (<xref ref-type="bibr" rid="B27">Liu et al., 2010</xref>). Water systems in karst regions possess divalent ions and have a high potential for CO<sub>2</sub> fixation and formation of new carbonates (<xref ref-type="bibr" rid="B23">Lian et al., 2011</xref>). Algae are the main component of aquatic organisms in karst areas and the main carrier in carbon uptake and deposition. Nitrogen and phosphorus are essential elements required for plant growth and can influence the growth of algae (<xref ref-type="bibr" rid="B42">Sun H. et al., 2022</xref>). In a study of the physicochemical properties of karst lakes, it was found that the growth of karst lake algae is controlled by N and P, instead of C and P, leading to co-precipitation with calcium carbonate generated by carbon sinks (<xref ref-type="bibr" rid="B17">Karlsson et al., 2009</xref>). Algae involved in biological pump processes reduce the nutrient content in water, improving the environmental quality of water (<xref ref-type="bibr" rid="B30">Liu et al., 2008</xref>). Outbreaks of algal bloom and the release of algal organic matter (AOM) are partially mitigated by the biological pump effect (<xref ref-type="bibr" rid="B49">Yang et al., 2016</xref>). In addition, studies proved that karst water has a fertilizing effect and can significantly promote the growth of algae (<xref ref-type="bibr" rid="B44">Wang et al., 2014</xref>). Ca<sup>2&#x2b;</sup> and Mg<sup>2&#x2b;</sup> released from dolomite and limestone in karst water through carbonate dissolution can also provide additional substrates for algal growth (<xref ref-type="bibr" rid="B57">Zhou et al., 2022</xref>), which can utilize DIC and promote Ca<sup>2&#x2b;</sup> deposition, compared to algal growth in a non-karst water environment (<xref ref-type="bibr" rid="B27">Liu et al., 2010</xref>). Although studies on the importance of algal growth in karst lakes for the increase of carbon sinks have been widely reported (<xref ref-type="bibr" rid="B44">Wang et al., 2014</xref>; <xref ref-type="bibr" rid="B29">Liu Z. H. et al., 2018</xref>), the metabolic conversion of DIC after absorption into algae at different growth periods still remains elusive.</p>
<p>Spectroscopic analysis techniques, developed based on spectroscopy theory, are essential analytical tools that can be used for both qualitative and quantitative analysis (<xref ref-type="bibr" rid="B15">Hua et al., 2019</xref>) and are widely used in chemical, biochemical, and environmental protection applications (<xref ref-type="bibr" rid="B25">Liu et al., 2011</xref>). Spectroscopic characterization techniques can be used to rapidly and sensitively characterize the physicochemical characteristics of AOM and effectively reveal the composition of AOM (<xref ref-type="bibr" rid="B16">Hua et al., 2017</xref>). Dissolved organic carbon (DOC) serves as a key indicator for characterizing AOM because algae are critical contributors to endogenous DOC in aquatic environments (<xref ref-type="bibr" rid="B54">Zhang et al., 2011</xref>). The amount of aromatic compounds, proteins, <italic>etc.</italic>, in AOM can be effectively evaluated by using ultraviolet&#x2013;visible (UV&#x2013;Vis) absorption technology (<xref ref-type="bibr" rid="B32">Matilainen et al., 2011</xref>). Characterization of organic functional groups using Fourier transform infrared (FT-IR) spectroscopy provides a thorough understanding of the specific composition and traceability of AOM (<xref ref-type="bibr" rid="B3">Chu et al., 2015</xref>), and evidences of contribution from biomolecules such as proteins, lipids, and polysaccharides in algae cells are obvious (<xref ref-type="bibr" rid="B47">Wang Z. et al., 2012</xref>; <xref ref-type="bibr" rid="B48">Wang Z. K. et al., 2012</xref>). Three-dimensional fluorescence spectroscopy combined with parallel factor analysis can decipher the fluorescence information of AOM and better probe the composition and differences of AOM (<xref ref-type="bibr" rid="B22">Li et al., 2020</xref>). Phytoplankton discovered downstream of karst rivers produce a large amount of organic matter with the increase in the fluorescence index (<xref ref-type="bibr" rid="B34">Ni et al., 2020</xref>).</p>
<p>In this study, the metabolic conversion of DIC at different algal growth periods was investigated. Two representative algal species, <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic>, were selected to explore changes in organic matter at different growth periods under simulated karst water environmental conditions. EOM and intracellular organic matter (IOM) were extracted for characterization through UV&#x2013;Vis absorption, FT-IR, and three-dimensional excitation and emission (3D-EEM) spectroscopy. This study aimed to reveal the <italic>in vivo</italic> metabolic conversion of DIC in karst lake reservoirs during the growth of algae and provide scientific support for the management of water eutrophication and the relationship between algae and carbon cycle in karst water.</p>
</sec>
<sec sec-type="materials|methods" id="s2">
<title>2 Material and methods</title>
<sec id="s2-1">
<title>2.1 Algal culture preparation</title>
<p>
<italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> were purchased from the Freshwater Algae Bank of the Chinese Academy of Sciences. Two dominant algal species were selected based on our previous study of the distribution of dominant algal species in Aha Reservoir, a typical karst lake in Guizhou Province, southwest of China (<xref ref-type="bibr" rid="B9">Ge et al., 2021</xref>). Based on our previous sampling results (<xref ref-type="bibr" rid="B57">Zhou et al., 2022</xref>), modified BG11 medium (<xref ref-type="sec" rid="s10">Supplementary Table S1</xref>, Supplementary Information) was configured to simulate the karst conditions for algae cultivation. Both algae were cultured in a light incubator (BS-2E; Wampuda, China) at 22&#x2da;C &#xb1; 1&#xb0;C with a light intensity of 2000 lux and a light&#x2013;dark ratio of 12&#xa0;h: 12&#xa0;h. After algae were cultured to the logarithmic phase, the algal solution was concentrated using a centrifuge (GT10-1; Beili, China) at 4,500&#xa0;r&#xb7;min <sup>&#x2212;1</sup> for spreading cultivation. Initial inoculum concentrations of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> were 2 &#xd7; 10<sup>6</sup>&#xa0;cells&#xb7;mL<sup>&#x2212;1</sup> and 1.65 &#xd7; 10<sup>6</sup>&#xa0;cells&#xb7;mL<sup>&#x2212;1</sup>, respectively, and the incubation time was 10&#xa0;days. The growth cycle of the algal cells was recorded by direct counting under a microscope (UB203i; Aopu, China) using a hemocytometer plate.</p>
</sec>
<sec id="s2-2">
<title>2.2 Extraction of algal organic matter</title>
<p>EOM was extracted by the following protocol: algal supernatant was obtained by centrifugation at 8,000&#xa0;r&#xb7;min<sup>&#x2212;1</sup> for 5&#xa0;min, then filtered through deionized water (18.2&#xa0;M&#x3a9;&#xa0;cm), and pre-cleaned by filtering through 0.70 &#x3bc;m glass fiber paper (GF/F 47&#xa0;mm; Whatman, USA) to obtain EOM (<xref ref-type="bibr" rid="B45">Wang et al., 2021</xref>). After EOM extraction, remaining algal cells were washed with deionized water and then centrifuged for 1&#xa0;min (repeated twice), repeatedly grounded and freeze&#x2013;thawed three times, and filtered <italic>via</italic> 0.45-&#xb5;m CA membranes to obtain IOM (<xref ref-type="bibr" rid="B35">Pivokonsky et al., 2014</xref>). The organic carbon levels of EOM and IOM were determined using a total organic carbon analyzer (Vario TOC; Elementar, Germany).</p>
</sec>
<sec id="s2-3">
<title>2.3 Spectral experimental characterization</title>
<sec id="s2-3-1">
<title>2.3.1 UV&#x2013;Vis</title>
<p>The strength of aromaticity of AOM and the content of aromatic substances can be interpreted by SUVA<sub>254</sub> (<xref ref-type="bibr" rid="B18">Kida et al., 2018</xref>), SUVA<sub>280</sub> can be used to characterize proteins (<xref ref-type="bibr" rid="B8">Fichot and Benner, 2012</xref>), and the ratio of UVA<sub>210</sub>/UVA<sub>254</sub> (<xref ref-type="bibr" rid="B43">Sururi et al., 2020</xref>) can be used to explore the relative content of the amino structure of aromatic substances (<xref ref-type="bibr" rid="B12">Her et al., 2004</xref>). UV&#x2013;Vis was performed after scanning the blank sample with deionized water, EOM and IOM solutions isolated from four growth periods of the two algae were subjected to a UV&#x2013;Vis analyzer (UV 1800; Meixi, China) at 200&#x2013;700&#xa0;nm, and analysis for each sample was repeated twice.</p>
</sec>
<sec id="s2-3-2">
<title>2.3.2 FT-IR characterization</title>
<p>EOM and IOM solutions isolated from four growth periods of the two algae were characterized using infrared spectroscopy, and the samples were mixed with a low amount of KBr (spectrum pure; Aladdin Co., Shanghai) after being made into a dry powder using a vacuum freeze&#x2013;drying machine (LGJ-12T; Songyuanhuaxin, China). All samples were compressed using a tablet press, which was further characterized by scanning using an infrared spectrometer (Nicolet 6,700, Thermo, USA), setting the scanning range to 500&#x2013;3,800&#xa0;cm<sup>&#x2212;1</sup>.</p>
</sec>
<sec id="s2-3-3">
<title>2.3.3 3D-EEM characterization</title>
<p>EOM and IOM solutions isolated from four growth periods of the two algae were scanned in three dimensions using a fluorescence spectrophotometer (F-380; Gangdong, China), the excitation (Ex) wavelength was set from 200 to 450&#xa0;nm (interval 5.0&#xa0;nm), and the emission (Em) wavelength was set from 250 to 600&#xa0;nm (interval 1.0&#xa0;nm), and the scanning speed, slit width, and voltage were set to 2,400&#xa0;nm&#xa0;min<sup>&#x2212;1</sup>, 5.0&#xa0;nm, and 700&#xa0;V, respectively. Three-dimensional fluorescence parallel factor analysis (EEM-PARAFAC) was performed using MATLAB R2019b to deduct blanks and omit the interference peaks to remove the effects of Rayleigh scattering and Raman scattering (<xref ref-type="bibr" rid="B36">Qian et al., 2017</xref>), and the AOM model was validated by split-half analysis and residual analysis.</p>
</sec>
</sec>
<sec id="s2-4">
<title>2.4 Data processing and statistical methods</title>
<p>Spectral data processing was performed using Origin 8.5 (USA). Analysis of variance at the 0.05 level and Pearson correlation analysis (at the 0.01 and 0.05 levels) were performed using SPSS 20.</p>
</sec>
</sec>
<sec sec-type="results|discussion" id="s3">
<title>3 Results and discussion</title>
<sec id="s3-1">
<title>3.1 Algal culturing and DOC variation</title>
<p>The growth of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> in simulated karst water is shown in <xref ref-type="fig" rid="F1">Figure 1</xref>. The growth cycle of algae can be divided into four stages: adaptation stage, logarithmic stage, plateau stage, and decline stage. Both <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> entered the logarithmic stage of rapid growth and reproduction on the third&#xa0;day, but the logarithmic stage lasted for a short time. In addition, the growth of the two algae entered a stable period on days 4&#x2013;7. In the stable stage, algal cells maintained a relatively stable level, the maximum algal cell concentration reached 5.7&#xd7;10<sup>6</sup> cells&#xb7;mL<sup>&#x2212;1</sup> and 5.9&#xd7;10<sup>6</sup> cells&#xb7;mL<sup>&#x2212;1</sup>, and the algae entered a period of decline on the eighth day. Results showed that the maintenance time of the stable period in the karst area was shortened, which led to the overall growth cycle being obviously shortened.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Growth curves of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> (colored points represent the characteristic days of each growth period). <bold>(A)</bold> <italic>Chlorella vulgaris</italic>; <bold>(B)</bold> <italic>Scenedesmus obliquus</italic>. AP, adaptation phase; LP, logarithmic phase; SP, stationary phase; DP, decline phase.</p>
</caption>
<graphic xlink:href="fenvs-11-1112522-g001.tif"/>
</fig>
<p>The variations in DOC values of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> are shown in <xref ref-type="table" rid="T1">Table 1</xref>. With the change in the growth cycle of the two algal species of, DOC increased significantly from the adaptation stage to the logarithmic stage. In the stable period, more cell metabolites were released in AOM, and the concentration of DOC increased. The amount of DOC in EOM was higher than that in IOM at each growth stage of <italic>Chlorella vulgaris</italic>, indicating that EOM would produce more DOC under the simulated condition in the karst lake reservoir. The higher DOC content in stable EOM represents more DOC accumulation with the growth of algae (<xref ref-type="bibr" rid="B56">Zhao et al., 2020</xref>; <xref ref-type="bibr" rid="B33">Ni et al., 2021</xref>). During the adaptation period, the amount of DIC was abundant and reached the maximum in EOM (20.32 &#xb1; 0.12a&#xa0;mg/L and 22.60 &#xb1; 0.08a&#xa0;mg/L). Although DIC provided the carbon source for the photosynthesis of algae, it can also be extrapolated that the biological pump effect may provide a promoting effect on the growth of algae (<xref ref-type="sec" rid="s10">Supplementary Table SI2</xref>).</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Values of dissolved organic carbon (DOC/mg &#x2022; L<sup>&#x2212;1</sup>) in common <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> at different growth stages.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Growing period</th>
<th align="center">
<italic>Chlorella vulgaris</italic> EOM (mg&#x2022;L<sup>&#x2212;1</sup>)</th>
<th align="center">
<italic>Chlorella vulgaris</italic> IOM (mg&#x2022;L<sup>&#x2212;1</sup>)</th>
<th align="center">
<italic>Scenedesmus obliquus</italic> EOM (mg&#x2022;L<sup>&#x2212;1</sup>)</th>
<th align="center">
<italic>Scenedesmus obliquus</italic> IOM (mg&#x2022;L<sup>&#x2212;1</sup>)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Adaptation phase</td>
<td align="center">5.65 &#xb1; 0.29<xref ref-type="table-fn" rid="Tfn1">
<sup>c</sup>
</xref>
</td>
<td align="center">2.45 &#xb1; 0.03<xref ref-type="table-fn" rid="Tfn1">
<sup>b</sup>
</xref>
</td>
<td align="center">6.93 &#xb1; 0.33<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">4.65 &#xb1; 0.03<xref ref-type="table-fn" rid="Tfn1">
<sup>d</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">Logarithmic phase</td>
<td align="center">6.38 &#xb1; 0.04<xref ref-type="table-fn" rid="Tfn1">
<sup>b</sup>
</xref>
</td>
<td align="center">2.25 &#xb1; 0.02<xref ref-type="table-fn" rid="Tfn1">
<sup>b</sup>
</xref>
</td>
<td align="center">6.08 &#xb1; 0.04<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">1.98 &#xb1; 0.04<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">Stationary phase</td>
<td align="center">8.90 &#xb1; 0.09<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">3.99 &#xb1; 0.00<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">6.61 &#xb1; 0.04<xref ref-type="table-fn" rid="Tfn1">
<sup>ab</sup>
</xref>
</td>
<td align="center">6.85 &#xb1; 0.03<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
</tr>
<tr>
<td align="left">Decline phase</td>
<td align="center">8.79 &#xb1; 0.07<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">3.74 &#xb1; 0.19<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref>
</td>
<td align="center">6.52 &#xb1; 0.01<xref ref-type="table-fn" rid="Tfn1">
<sup>ab</sup>
</xref>
</td>
<td align="center">5.06 &#xb1; 0.01<xref ref-type="table-fn" rid="Tfn1">
<sup>b</sup>
</xref>
</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="Tfn1">
<label>
<sup>a&#x2013;d</sup>
</label>
<p>: Significance analysis letter marking method, significance level: 0.01.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s3-2">
<title>3.2 UV&#x2013;Vis determination and chemical composition analysis</title>
<p>The changes in SUVA<sub>254</sub>, SUVA<sub>280</sub>, and URI values in different growth stages of the two algae are shown in <xref ref-type="fig" rid="F2">Figure 2</xref>. The SUVA<sub>254</sub> of logarithmic IOM for <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> was 1.898 &#xb1; 0.043&#xa0;L&#xa0;mg<sup>&#x2212;1</sup>&#xb7;m<sup>&#x2212;1</sup> and 2.619 &#xb1; 0.007&#xa0;L&#xa0;mg<sup>&#x2212;1</sup>&#xb7;m<sup>&#x2212;1</sup> (<xref ref-type="fig" rid="F2">Figure 2A</xref>), respectively, suggesting more aromatic substances were produced in IOM during this period (<xref ref-type="bibr" rid="B5">Dong et al., 2019</xref>; <xref ref-type="bibr" rid="B41">Sun F. et al., 2022</xref>). SUVA<sub>254</sub> in AOM was generally less than 1.5&#xa0;L&#xa0;mg<sup>&#x2212;1</sup>&#xb7;m<sup>&#x2212;1</sup> (<xref ref-type="bibr" rid="B58">Zhou et al., 2014</xref>), showing that the aromaticity of AOM was low&#x2014;AOM seemed to contain less protein-like substances and organic nitrogen (<xref ref-type="bibr" rid="B14">Hua et al., 2018</xref>). The DOC content in EOM of both algae during all periods was higher than that in IOM, except for the stationary phase of <italic>Scenedesmus obliquus</italic>, but SUVA<sub>254</sub> in EOM was lower than that in IOM in all growth periods, showing a stronger aromatic expression in IOM under the influence of complex karst water condition (<xref ref-type="bibr" rid="B21">Li et al., 2012</xref>). SUVA<sub>280</sub> and SUVA<sub>254</sub> share the same trend, suggesting a potent correlation between aromaticity and protein levels (<xref ref-type="bibr" rid="B46">Wang et al., 2013</xref>; <xref ref-type="bibr" rid="B26">Liu W. et al., 2018</xref>). The SUVA<sub>254</sub> and SUVA<sub>280</sub> values in <xref ref-type="fig" rid="F2">Figures 2A, B</xref> were the highest in the logarithmic phase of IOM, indicating high accumulation of aromatic compounds and proteins in the algal cells during rapid growth. However, the decrease in SUVA<sub>280</sub> in IOM during the decline phase may be due to the release of more organic matter outside the cell during decay of the algae (<xref ref-type="bibr" rid="B16">Hua et al., 2017</xref>) and higher accumulation of polysaccharides than proteins (<xref ref-type="bibr" rid="B11">Henderson et al., 2008</xref>). In addition, the trends of SUVA<sub>254</sub> and SUVA<sub>280</sub> in the two algae at different growth periods were completely opposite in EOM and IOM, with a gradual decrease in IOM after the logarithmic phase, indicating higher release of aromatic protein substances from cells. This was different from the results of many studies in non-karst areas (<xref ref-type="bibr" rid="B10">Gough et al., 2015</xref>; <xref ref-type="bibr" rid="B2">Chen et al., 2017</xref>). After the logarithmic phase, higher accumulation of aromatic substances in EOM than consumption was observed as SUVA<sub>254</sub> in EOM gradually increased.</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>UV absorbance of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> at different growth stages. <bold>(A)</bold> SUVA<sub>254</sub>; <bold>(B)</bold> SUVA<sub>280</sub>; <bold>(C)</bold> URI.</p>
</caption>
<graphic xlink:href="fenvs-11-1112522-g002.tif"/>
</fig>
<p>URI values in EOM reached their highest during the adaptation period (43.877 &#xb1; 0.442a and 35.235 &#xb1; 1.059a) and gradually decreased with algal growth (<xref ref-type="fig" rid="F2">Figure 2C</xref>). IOM was found to have higher URI values in the study of AOM in karst areas (<xref ref-type="bibr" rid="B31">Ma et al., 2022</xref>), which showed that the concentration of amino groups was higher than that of aromatic groups in EOM, and there were more proteins in EOM at the early growth stage of algae in karst lakes. The concentration of amino groups in IOM in the decline stage increased compared with that in the stable stage, which may result in the formation of unsaturated aromatic substances during the decline stage (<xref ref-type="bibr" rid="B12">Her et al., 2004</xref>).</p>
</sec>
<sec id="s3-3">
<title>3.3 Analysis of chemical components determined by FT-IR</title>
<p>The FT-IR spectra of EOM and IOM of the two algae at different growth periods are shown in <xref ref-type="fig" rid="F3">Figure 3</xref>. The spectral peaks of EOM at 3,500&#x2013;3,300&#xa0;cm<sup>&#x2212;1</sup> indicated O-H and N-H stretching vibrations (<xref ref-type="bibr" rid="B55">Zhang et al., 2014</xref>), and both algae exhibited N-H stretching at 3,200&#x2013;3,100&#xa0;cm<sup>&#x2212;1</sup> during the decline phase (<xref ref-type="bibr" rid="B31">Ma et al., 2022</xref>). The peaks at 1700&#x2013;1,600&#xa0;cm<sup>&#x2212;1</sup> can be explained by C&#x3d;O vibrations of amide I (<xref ref-type="bibr" rid="B7">Fawzy, 2016</xref>; <xref ref-type="bibr" rid="B52">Zambrano et al., 2021</xref>), while those at 1,500&#x2013;1,400&#xa0;cm<sup>&#x2212;1</sup> correspond to CH<sub>2</sub>/CH<sub>3</sub> vibrations (<xref ref-type="bibr" rid="B51">Yang et al., 2018</xref>). Wavelength ranges of 1,200&#x2013;1,100&#xa0;cm<sup>&#x2212;1</sup> and 875&#xa0;cm<sup>&#x2212;1</sup> show C-O-C stretching vibrations. The peak of <italic>Chlorella vulgaris</italic> IOM at 3,200&#x2013;3,100&#xa0;cm<sup>&#x2212;1</sup> was not observed (<xref ref-type="fig" rid="F3">Figure 3A</xref>), whereas a significant N-H stretching during the adaptation and decline phases of <italic>Scenedesmus obliquus</italic> was noted. In addition, C-H stretching at 3,000&#x2013;2,800&#xa0;cm<sup>&#x2212;1</sup> was observed in IOM in each growth period (<xref ref-type="bibr" rid="B4">Dias et al., 2021</xref>; <xref ref-type="bibr" rid="B6">Fawzy and Alharthi, 2021</xref>). Vibrations of amide II were also observed at 1,580&#x2013;1,500&#xa0;cm<sup>&#x2212;1</sup> in the latter two periods of <italic>Scenedesmus obliquus</italic> (<xref ref-type="fig" rid="F3">Figure 3B</xref>; <xref ref-type="bibr" rid="B40">Singh et al., 2018</xref>); these peaks caused by amide groups proved the presence of proteins (<xref ref-type="bibr" rid="B58">Zhou et al., 2014</xref>).</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>FT-IR spectra of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> at different growth stages. <bold>(A)</bold> <italic>Chlorella vulgaris</italic> EOM; <bold>(B)</bold> <italic>Chlorella vulgaris</italic> IOM; <bold>(C)</bold> <italic>Scenedesmus obliquus</italic> EOM; <bold>(D)</bold> <italic>Scenedesmus obliquus</italic> IOM.</p>
</caption>
<graphic xlink:href="fenvs-11-1112522-g003.tif"/>
</fig>
<p>The main components of both algae showed different patterns: both <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> had more than 50% protein content, with lipids and polysaccharides forming 7%&#x2013;24% of the main compounds (<xref ref-type="bibr" rid="B1">Becker, 2007</xref>; <xref ref-type="bibr" rid="B46">Wang et al., 2013</xref>). The obvious functional groups of proteins and polysaccharides were found at 3,500&#x2013;3,300&#xa0;cm<sup>&#x2212;1</sup> during the adaptation phase of both algal species, and the concentration of these biochemical constituents gradually decreased during the growth period. Protein peaks corresponding to 1,700&#x2013;1,400&#xa0;cm<sup>&#x2212;1</sup> similarly weakened in peak intensity after the adaptation phase, and polysaccharide peaks corresponding to 1,200&#x2013;1,000/875&#xa0;cm<sup>&#x2212;1</sup> showed a similar trend. However, the functional groups in the 3,200&#x2013;3,100&#xa0;cm<sup>&#x2212;1</sup> band were observed much frequently during the decline phase, suggesting that algal growth requires consumption of organic substances such as proteins and polysaccharides by the algal cells after the stationary phase. The peak at 3,000&#x2013;2,800&#xa0;cm<sup>&#x2212;1</sup> was more strongly expressed in IOM and can be used to explain the presence of lipids (<xref ref-type="fig" rid="F3">Figure 3B</xref>). The FT-IR results revealed that both algae contain proteins and polysaccharides in EOM and IOM and that DIC promotes the production of more protein and polysaccharide material during the adaptation phase to provide energy for algal growth. The functional groups of proteins were more abundant, and as the growth of algae increased, more lipids were retained in the IOM.</p>
</sec>
<sec id="s3-4">
<title>3.4 3D-EEM determination of chemical composition</title>
<p>The 3D-EEM-PARAFAC results of EOM and IOM in <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> are shown in <xref ref-type="fig" rid="F4">Figure 4</xref>. All analyses yielded two fluorescence fractions: the C1 fraction had two excitation peaks and one emission peak, representing aromatic protein-like organic matter (AP) and soluble metabolites (SMP), respectively, and the C2 fraction for humic acid-like organic matter (HA). It was similarly found that AP and SMP were the dominant fluorescent components in AOM (<xref ref-type="bibr" rid="B45">Wang et al., 2021</xref>).</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>Fluorescence spectral characteristics of EOM and IOM of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> at different growth stages. <bold>(A)</bold> <italic>Chlorella vulgaris</italic>; <bold>(B)</bold> <italic>Scenedesmus obliquus</italic>.</p>
</caption>
<graphic xlink:href="fenvs-11-1112522-g004.tif"/>
</fig>
<p>Although both algae showed the same fluorescence components, the fluorescence intensity differed in different periods, and the fluorescence intensity of two fluorescence components of <italic>Chlorella vulgaris</italic> (113.02 and 13.54) and EOM (102.89 and 17.61) increased significantly after entering the stationary phase (<xref ref-type="fig" rid="F4">Figure 4A</xref>). Tryptophan-like aromatic substances, biochemical organic substances with abundant activity in algal cells, were found at 230/350&#xa0;nm. This means that <italic>Chlorella vulgaris</italic> accumulates more protein-like substances with aromatic compounds in the AOM after entering the stationary phase (<xref ref-type="bibr" rid="B21">Li et al., 2012</xref>). SMP is mainly composed of tryptophan, tyrosine, and protein-like substances, and production of these substances shows that AOM is enriched in organic nitrogen and promotes the production of compounds rich in organic nitrogen (<xref ref-type="bibr" rid="B21">Li et al., 2012</xref>; <xref ref-type="bibr" rid="B56">Zhao et al., 2020</xref>). Humic acid-like substances were mainly derived from dead algal cells, and damage of algal cells was caused during grinding or freeze&#x2013;thaw extraction of IOM (<xref ref-type="bibr" rid="B56">Zhao et al., 2020</xref>). C2 in EOM had stronger fluorescence intensity during the decline phase, and post-death, algal cells exhibited obvious humic signals. The low intensity of C2 fluorescence might be caused by powerful cell activity in the algal solution (<xref ref-type="bibr" rid="B37">Rochelle-Newall and Fisher, 2002</xref>).</p>
<p>Unlike <italic>Chlorella vulgaris</italic>, the C1 fraction of <italic>Scenedesmus obliquus</italic> had the greatest fluorescence intensity during the IOM stationary phase (112.73) (<xref ref-type="fig" rid="F4">Figure 4B</xref>) and higher protein enrichment during the stationary phase, which might be driven by intracellular AOM release (<xref ref-type="bibr" rid="B2">Chen et al., 2017</xref>). During the decline phase, due to the death of a large quantity of algae, protein materials also decreased. Although IOM has been proven to be mainly organic nitrogen compounds with more protein aromatic substances, the soluble protein generated would be gradually broken down by the activities of algal cells (<xref ref-type="bibr" rid="B16">Hua et al., 2017</xref>). The highest fluorescence intensity of humic substances in the C2 fraction of <italic>Scenedesmus obliquus</italic> EOM was found during the decline phase (10.94), associated with the death of algae.</p>
</sec>
<sec id="s3-5">
<title>3.5 Correlation analysis</title>
<p>The spectral parameters of both algae were correlated to the chemical characteristics of AOM. In <italic>Chlorella vulgaris</italic> (<xref ref-type="fig" rid="F5">Figures 5A, B</xref>), the correlation between DIC and TN was high (0.87 and 0.99), indicating that there was a good correlation between the accumulation of N production in algae and the change in DIC during the growth period. The correlation between DOC, DIC, and TN of <italic>Chlorella vulgaris</italic> and SUVA<sub>254</sub> and SUVA<sub>280</sub> showed the opposite trend in EOM and IOM, proving differences in the chemical properties of AOM, and the growth change in AOM could be better judged based on the changes in DOC, DIC, and TN. There was a high correlation between TN and URI in IOM (0.97) (<xref ref-type="fig" rid="F5">Figure 5B</xref>), showing that changes in the amino-structured organic matter in IOM of <italic>Chlorella vulgaris</italic> can be analyzed in conjunction with the changes in TN. The correlation between DOC and C1 and C2 indicated a positive effect of organic carbon on the production of aromatic, soluble biometabolites and humic substances in EOM.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>Pearson correlation analysis of spectral parameters of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus.</italic> <bold>(A)</bold> <italic>Chlorella vulgaris</italic> EOM; <bold>(B)</bold> <italic>Chlorella vulgaris</italic> IOM; <bold>(C)</bold> <italic>Scenedesmus obliquus</italic> EOM; <bold>(D)</bold> <italic>Scenedesmus obliquus</italic> IOM (n &#x3d; 16).</p>
</caption>
<graphic xlink:href="fenvs-11-1112522-g005.tif"/>
</fig>
<p>The correlations of the indices of <italic>Scenedesmus obliquus</italic> were slightly different from those of <italic>Chlorella vulgaris</italic> (<xref ref-type="fig" rid="F5">Figures 5C, D</xref>). As shown in <xref ref-type="fig" rid="F5">Figure 5C</xref>, DIC showed negative correlations with SUVA<sub>254</sub> and SUVA<sub>280</sub> in EOM; the differences arising between the two algae may be related to the transformation of DIC and organic matter production. The negative correlation between DIC and TN further reflected that the chemical composition and changes in EOM in <italic>Scenedesmus obliquus</italic> were more complex. The relationship between DOC and C1 and C2 was significantly different from that in <italic>Chlorella vulgaris</italic>. It is recommended to avoid using a single DOC trend for interpretation of the derivation of compositional changes in AOM (<xref ref-type="bibr" rid="B13">Hestir et al., 2015</xref>; <xref ref-type="bibr" rid="B53">Zeng et al., 2019</xref>). SUVA<sub>254</sub> and SUVA<sub>280</sub> showed an intense correlation in AOM of both algae, confirming that it is possible to discuss the analysis of aromaticity and protein content in organic matter by combining two UV coefficients (<xref ref-type="fig" rid="F5">Figure 5</xref>). In addition, URI and C1 fractions were negatively correlated in both algae, and the negative correlation was more significant in EOM (<xref ref-type="fig" rid="F5">Figures 5A, C</xref>), indicating that the content of amino-structured substances in EOM gradually decreased with the growth of algae. High levels of aromatic proteins (tryptophan-like substances) were produced in the algal cells, suggesting lower aromaticity in EOM. FT-IR of the adaptation phase also reflected weakening of the peak intensity of the functional groups containing amino groups, and more aromatic structure-related functional groups were generated during subsequent growth periods (<xref ref-type="fig" rid="F3">Figure 3</xref>).</p>
</sec>
</sec>
<sec id="s4">
<title>4 Conclusion and perspectives</title>
<p>In this study, we documented changes in the organic matter of <italic>Chlorella vulgaris</italic> and <italic>Scenedesmus obliquus</italic> during different growth periods under karst water conditions using various spectral characterization techniques. The conclusions of this study are as follows.<list list-type="simple">
<list-item>
<p>1) Both algae contained high concentrations of DIC in the EOM during the adaptation phase, and DIC provided a stable carbon source for the algae to carry out photosynthesis; the increase in DIC during the decline phase might have had a facilitating effect on the conversion of the carbon cycle.</p>
</list-item>
<list-item>
<p>2) More DOC would be accumulated in EOM during the stabilization and decay periods, and more organic matter was released into the water column during this period. While more aromatic compounds were generated, the aromaticity gradually decreased after the logarithmic phase of IOM.</p>
</list-item>
<list-item>
<p>3) IOM was found to contain more pronounced lipid functional groups. A negative correlation between URI and C1 further indicated that the amino structural material in EOM gradually decreases with the growth of algae, and more aromatic protein-like material was produced after entering the stationary phase.</p>
</list-item>
</list>
</p>
<p>In summary, the changes in DOC and DIC during the different growth periods of AOM contributed critically to the biological pump effect and accumulation of carbon sinks. By monitoring the characteristics of organic matter in AOM during different growth periods, the changes in chemical characteristics of algae involved in carbon cycle in the aquatic environment of karst areas can be determined, and the biological pump effect of aquatic ecosystems could be explored in future studies.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s5">
<title>Data availability statement</title>
<p>The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.</p>
</sec>
<sec id="s6">
<title>Author contributions</title>
<p>LT and ZW contributed to the conception and design of the study and wrote the first draft of the manuscript. PZ organized the database. CX performed the statistical analysis. YK, XP, MY, and YQ wrote sections of the manuscript. ZW contributed to conception, funding acquisition, resources, supervision, and writing&#x2014;review and editing. All authors contributed to manuscript revision and read and approved the submitted version.</p>
</sec>
<sec id="s7">
<title>Funding</title>
<p>This study was financially supported by the National Natural Science Foundation of China (NSFC grant Nos. 41867048, 42167050, and 42207086), the Innovation Team Project of Guizhou Higher Education ((2022)013), and the construction project of Key Laboratory of State Ethnic Affairs Commission ((2020) No. 91 of DDA office, i.e., The Karst Environmental Geological Hazard Prevention Laboratory of Guizhou Minzu University).</p>
</sec>
<sec sec-type="COI-statement" id="s8">
<title>Conflict of interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="disclaimer" id="s9">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors, and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec id="s10">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fenvs.2023.1112522/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fenvs.2023.1112522/full&#x23;supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet1.DOCX" id="SM1" mimetype="application/DOCX" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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