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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Ecol. Evol.</journal-id>
<journal-title>Frontiers in Ecology and Evolution</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Ecol. Evol.</abbrev-journal-title>
<issn pub-type="epub">2296-701X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fevo.2023.1121632</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Ecology and Evolution</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Intensified sensitivity and adaptability of zooplankton Bosminidae in subtropical shallow freshwater lakes with increasing trophic level</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author"><name>
<surname>Cheng</surname>
<given-names>Longjuan</given-names>
</name><xref rid="aff1" ref-type="aff"><sup>1</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/2015678/overview"/>
</contrib>
<contrib contrib-type="author"><name>
<surname>Gao</surname>
<given-names>Xinyuan</given-names>
</name><xref rid="aff1" ref-type="aff"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author"><name>
<surname>Wang</surname>
<given-names>Guangwei</given-names>
</name><xref rid="aff1" ref-type="aff"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author"><name>
<surname>Ding</surname>
<given-names>Zhou</given-names>
</name><xref rid="aff1" ref-type="aff"><sup>1</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/2201620/overview"/>
</contrib>
<contrib contrib-type="author" corresp="yes"><name>
<surname>Xue</surname>
<given-names>Bin</given-names>
</name><xref rid="aff2" ref-type="aff"><sup>2</sup></xref>
<xref rid="c001" ref-type="corresp"><sup>&#x002A;</sup></xref>
</contrib>
<contrib contrib-type="author" corresp="yes"><name>
<surname>Zhang</surname>
<given-names>Can</given-names>
</name><xref rid="aff2" ref-type="aff"><sup>2</sup></xref>
<xref rid="c001" ref-type="corresp"><sup>&#x002A;</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/2022670/overview"/>
</contrib>
<contrib contrib-type="author"><name>
<surname>Liu</surname>
<given-names>Jinliang</given-names>
</name><xref rid="aff3" ref-type="aff"><sup>3</sup></xref>
</contrib>
<contrib contrib-type="author"><name>
<surname>Jiang</surname>
<given-names>Qingfeng</given-names>
</name><xref rid="aff1" ref-type="aff"><sup>1</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/840431/overview"/>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>School of Geographical Science, Nantong University</institution>, <addr-line>Nantong, Jiangsu</addr-line>, <country>China</country></aff>
<aff id="aff2"><sup>2</sup><institution>State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences</institution>, <addr-line>Nanjing, Jiangsu</addr-line>, <country>China</country></aff>
<aff id="aff3"><sup>3</sup><institution>School of Environmental Science, Nanjing Xiaozhuang University</institution>, <addr-line>Nanjing, Jiangsu</addr-line>, <country>China</country></aff>
<author-notes>
<fn id="fn0001" fn-type="edited-by">
<p>Edited by: Kunshan Bao, South China Normal University, China</p>
</fn>
<fn id="fn0002" fn-type="edited-by">
<p>Reviewed by: Yuan Li, Chinese Academy of Sciences, China; Xu Chen, China University of Geosciences Wuhan, China</p>
</fn>
<corresp id="c001">&#x002A;Correspondence: Bin Xue, <email>bxue@niglas.ac.cn</email>; Can Zhang, <email>czhang@niglas.ac.cn</email></corresp>
<fn id="fn0003" fn-type="other">
<p>This article was submitted to Paleoecology, a section of the journal Frontiers in Ecology and Evolution</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>02</day>
<month>03</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>11</volume>
<elocation-id>1121632</elocation-id>
<history>
<date date-type="received">
<day>12</day>
<month>12</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>08</day>
<month>02</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2023 Cheng, Gao, Wang, Ding, Xue, Zhang, Liu and Jiang.</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Cheng, Gao, Wang, Ding, Xue, Zhang, Liu and Jiang</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>The deterioration in lake water environments, especially increasing lake eutrophication, is prevalent all over the world, which has seriously affected the balance and stability of the internal ecosystem of lakes. In this study, modern water and sediment samples were collected from three subtropical freshwater lakes with significant differences in nutrient levels to analyze the concentration of the zooplankton Cladocera Bosminidae and its relationship with lakes&#x2019; ecological changes. The results show that the deterioration in lake water environments caused by increasing eutrophication limits the survival of most zooplankton. However, the Bosminidae shows a positive adaptability to eutrophication and high sensitivity to the changes in the lake environment. In addition, the lake eutrophication process caused by the intensification of human activities enhances the survival advantage of Bosminidae with more food sources, which is more conducive to its rapid reproduction.</p>
</abstract>
<kwd-group>
<kwd>subtropical shallow freshwater lake</kwd>
<kwd>zooplankton</kwd>
<kwd>Bosminidae</kwd>
<kwd>eutrophication</kwd>
<kwd>ecological changes</kwd>
</kwd-group>
<counts>
<fig-count count="6"/>
<table-count count="2"/>
<equation-count count="0"/>
<ref-count count="55"/>
<page-count count="11"/>
<word-count count="7214"/>
</counts>
</article-meta>
</front>
<body>
<sec id="sec1" sec-type="intro">
<title>1. Introduction</title>
<p>Crustacean zooplankton Cladocera are highly abundant in freshwater bodies worldwide. These Cladocera communities are sensitive to changes in the environment and climate (<xref ref-type="bibr" rid="ref24">Korhola and Rautio, 2001</xref>; <xref ref-type="bibr" rid="ref41">Szeroczy&#x0144;ska and Sarmaja-Korjonen, 2007</xref>; <xref ref-type="bibr" rid="ref35">Paw&#x0142;owski et al., 2015</xref>; <xref ref-type="bibr" rid="ref9">Cheng et al., 2020a</xref>). The Bosminidae family belongs to Cladocera communities and is characterized by small body sizes (0.2&#x2013;1.0&#x2009;mm). They are ubiquitous on lake surfaces where the concentration of nutrients is relatively high (<xref ref-type="bibr" rid="ref51">Zaret and Kerfoot, 1975</xref>; <xref ref-type="bibr" rid="ref21">Jiang and Du, 1979</xref>; Zaret and Kerfoot, 1980; <xref ref-type="bibr" rid="ref42">Threlkeld, 1981</xref>; <xref ref-type="bibr" rid="ref14">De Melo and Hebert, 1994</xref>). The different species of the Bosminidae family exhibit unique adaptability to different nutritional environments (<xref ref-type="bibr" rid="ref21">Jiang and Du, 1979</xref>; <xref ref-type="bibr" rid="ref41">Szeroczy&#x0144;ska and Sarmaja-Korjonen, 2007</xref>). For example, <italic>Bosmina longirostris</italic> is commonly reported in eutrophic lakes, warming waters, and metal-contaminated lakes (<xref ref-type="bibr" rid="ref4">Boucherle and Z&#x00FC;llig, 1983</xref>; <xref ref-type="bibr" rid="ref3">Balcer et al., 1984</xref>; <xref ref-type="bibr" rid="ref25">Labaj et al., 2015</xref>; <xref ref-type="bibr" rid="ref1">Adamczuk, 2016</xref>). <italic>Bosmina</italic> (E.) <italic>longispina</italic> can be used to indicate oligotrophic and mesotrophic environment changes (<xref ref-type="bibr" rid="ref15">Deevey, 1942</xref>; <xref ref-type="bibr" rid="ref4">Boucherle and Z&#x00FC;llig, 1983</xref>; <xref ref-type="bibr" rid="ref34">Miroslaw-Grabowska et al., 2015</xref>). However, due to the destruction of Bosminidae chitin fossils in the process of deposition, it is difficult to distinguish all the specific species of Bosminidae. Recent studies showed that the total number of Bosminidae, including both the eutrophic species <italic>Bosmina longirostris</italic> and oligotrophic and mesotrophic species <italic>Bosmina</italic> (E.) <italic>longispina</italic>, shows clear survival advantages in lakes with high trophic levels (<xref ref-type="bibr" rid="ref11">Cheng et al., 2019</xref>, <xref ref-type="bibr" rid="ref6">2020b</xref>). For example, a large number of Bosminidae (a relative abundance greater than 80% in the total concentration of Cladocera) have been found in shallow eutrophic lakes in the subtropical zone (<xref ref-type="bibr" rid="ref31">Liu et al., 2008</xref>; <xref ref-type="bibr" rid="ref45">Wang et al., 2019</xref>; <xref ref-type="bibr" rid="ref6">Cheng et al., 2020b</xref>). Furthermore, the abundance of <italic>Bosmina longirostris</italic> is usually greater than that of the species <italic>Bosmina</italic> (E.) <italic>longispina</italic> (<xref ref-type="bibr" rid="ref11">Cheng et al., 2019</xref>, <xref ref-type="bibr" rid="ref10">2021</xref>) in eutrophic lakes. Therefore, we studied whether the Bosminidae can be used as a new indicator of the evolution of eutrophication in freshwater lakes in a subtropical region.</p>
<p>Since entering the Anthropocene, the impact of human activities on freshwater environments such as lakes has been increasing (<xref ref-type="bibr" rid="ref30">Lin et al., 2020</xref>). Under the combined effects of anthropogenic activities (such as rapid industrialization and urbanization) and climate change, lakes in the middle and lower reaches of the Yangtze River in eastern China, which is located in a subtropical region with a relatively dense population and developed economy, have undergone drastic deterioration over a few decades (<xref ref-type="bibr" rid="ref37">Qin et al., 2013</xref>; <xref ref-type="bibr" rid="ref55">Zhu et al., 2019</xref>). Currently, these freshwater shallow lakes in the middle and lower reaches of the Yangtze River are a prominent area of environmental deterioration in China (<xref ref-type="bibr" rid="ref37">Qin et al., 2013</xref>; <xref ref-type="bibr" rid="ref55">Zhu et al., 2019</xref>). Furthermore, most lakes in this area have entered either a mesotrophic stage or a eutrophic stage, or in between, and are suffering serious cyanobacteria outbreaks that the stability and balance in the lake ecosystem are seriously disturbed (<xref ref-type="bibr" rid="ref55">Zhu et al., 2019</xref>). For example, the biological composition of lakes has changed significantly, including the miniaturization of fishery structure, the reduction of aquatic plant area, cyanobacteria outbreaks, and a significant decline in biodiversity (<xref ref-type="bibr" rid="ref33">Mao et al., 2012</xref>; <xref ref-type="bibr" rid="ref53">Zhang K. et al., 2018</xref>; <xref ref-type="bibr" rid="ref19">Jenny et al., 2020</xref>).</p>
<p>Taihu Lake (severe eutrophication), Nanyi Lake (transition from mesotrophication to eutrophication), and Shengjin Lake (mesotrophication) are located in the middle and lower reaches of the Yangtze River. They show significant differences in trophic level, area, and local economic development level and are representative of the research on the relationship between the evolution of zooplankton community and eutrophication. Therefore, in this study, we chose the three shallow freshwater lakes as our research object. Based on the research methods of paleolimnology and limnology, we focused on the indicative significance of Bosminidae in lake eutrophication in the three lakes since the 1950s. We analyzed the temporal and spatial changes in Bosminidae density and focused on revealing the adaptability and sensitivity of Bosminidae to lake eutrophication.</p>
</sec>
<sec id="sec2" sec-type="materials|methods">
<title>2. Materials and methods</title>
<sec id="sec3">
<title>2.1. Study area and field sampling</title>
<p>Taihu Lake, Nanyi Lake, and Shengjin Lake are located in the middle and lower reaches of the Yangtze River (<xref rid="fig1" ref-type="fig">Figure 1</xref>). The annual temperature and precipitation in the lower reaches of the Yangtze River Basin are 15&#x2013;16&#x00B0;C and 1,010&#x2013;1,600&#x2009;mm, respectively (<xref ref-type="bibr" rid="ref38">Qin et al., 2007</xref>; <xref ref-type="bibr" rid="ref43">Wang et al., 2015</xref>; <xref ref-type="bibr" rid="ref50">Yao and Xue, 2016</xref>; <xref ref-type="bibr" rid="ref52">Zhang M. et al., 2018</xref>). Taihu Lake (mean depth&#x2009;=&#x2009;1.89&#x2009;m, area&#x2009;=&#x2009;2,338&#x2009;km<sup>2</sup>) is socioeconomically important and is the third largest freshwater lake in the Yangtze Delta. It supplies drinking water to some of the large cities in the delta, including Shanghai, Suzhou, and Wuxi (<xref ref-type="bibr" rid="ref38">Qin et al., 2007</xref>). Taihu Lake is divided into different ecological types (<xref ref-type="bibr" rid="ref38">Qin et al., 2007</xref>). The eastern area of Taihu Lake (called the East Taihu Lake) has an average water depth of &#x003C; l m. As opposed to the western and central lake areas, it is a grass lake dominated by large areas of aquatic plants (<xref ref-type="bibr" rid="ref9">Cheng et al., 2020a</xref>). More than 200 rivers flow into Taihu Lake with a combined total length of ~120,000&#x2009;km (<xref ref-type="bibr" rid="ref54">Zhong et al., 2014</xref>). The lake has been experiencing prolonged eutrophication over the past 40&#x2009;years, with increased cyanobacterial (Microcystis) blooms mostly during summer, reducing both water quality and biodiversity (<xref ref-type="bibr" rid="ref38">Qin et al., 2007</xref>; <xref ref-type="bibr" rid="ref48">Yang et al., 2008</xref>; <xref ref-type="bibr" rid="ref27">Li and Chen, 2010</xref>; <xref ref-type="bibr" rid="ref12">Dai et al., 2016</xref>).</p>
<fig position="float" id="fig1">
<label>Figure 1</label>
<caption>
<p>The location of the study area and the sample site. <bold>(A)</bold> Taihu Lake; <bold>(B)</bold> Nanyi Lake; and <bold>(C)</bold> Shengjin Lake.</p>
</caption>
<graphic xlink:href="fevo-11-1121632-g001.tif"/>
</fig>
<p>Nanyi Lake (31&#x00B0;03&#x2032;-31&#x00B0;10&#x2032;N, 118&#x00B0;50&#x2032;-119&#x00B0;02&#x2032; E) is located in the Shuiyangjiang River Basin, which belongs to the lower reaches of the Yangtze River. The lake&#x2019;s surface area is 203&#x2009;km<sup>2</sup> with a mean depth of approximately 2&#x2009;m (<xref ref-type="bibr" rid="ref44">Wang et al., 2013</xref>). The Langchuan River and the New Langchuan River flow into the northeastern part of Nanyi Lake (<xref ref-type="bibr" rid="ref50">Yao and Xue, 2016</xref>). Since the 1970s, significant increases in the trophic level and water level of Nanyi Lake have been observed, and currently, it is in a critical period of ecosystem transformation from mesotrophic to eutrophic status (<xref ref-type="bibr" rid="ref10">Cheng et al., 2021</xref>).</p>
<p>Shengjin Lake (116&#x00B0; 55&#x2032;&#x2013;117&#x00B0; 15&#x2032; E and 30&#x00B0; 15&#x2032;&#x2013;30&#x00B0; 30&#x2032; N), which is an important national nature reserve, has a surface area of 133&#x2009;km<sup>2</sup> and consists of three parts: upper, middle, and lower (<xref ref-type="bibr" rid="ref43">Wang et al., 2015</xref>). Shengjin Lake serves as a habitat for more than 70,000 wintering water birds each year (<xref ref-type="bibr" rid="ref46">Yang, 2011</xref>). It also joined the East Asian&#x2013;Australasian Waterfowl Reserve Network in 2005 and was added to the list of Wetlands of International Importance in 2015 (<xref ref-type="bibr" rid="ref5">Cao et al., 2018</xref>; <xref ref-type="bibr" rid="ref36">Peng et al., 2019</xref>; <xref ref-type="bibr" rid="ref47">Yang et al., 2019</xref>). With the increase in human activities, the trophic state of Shengjin Lake has also been increasing since the 1980s (<xref ref-type="bibr" rid="ref8">Cheng et al., 2020c</xref>).</p>
</sec>
<sec id="sec4">
<title>2.2. Materials and methods</title>
<p>Modern zooplankton samples were collected in October 2017 and in April and July 2018. Sedimentary cores were collected in October 2016 and 2017 (<xref rid="tab1" ref-type="table">Table 1</xref>). The number of zooplankton in a unit volume of water was counted and the individuals were counted under the microscope at 100&#x2013;200x magnification. The pretreatment process for subfossil Cladocera and geochemical indices (TN, TP, and &#x03B4;<sup>13</sup>C in the Bosminidae (&#x03B4;<sup>13</sup>C<sub>bos</sub>)) have been described in detail in previous studies (<xref ref-type="bibr" rid="ref6">Cheng et al., 2020b</xref>,<xref ref-type="bibr" rid="ref8">c</xref>, <xref ref-type="bibr" rid="ref10">2021</xref>). The subsamples for subfossil Cladocera were treated with 100&#x2009;ml of 10% potassium hydroxide (KOH) solution, heated at 60&#x00B0;C for 45&#x2009;min, sieved through a 38-&#x03BC;m mesh under running deionized water, and transferred into 15-ml centrifuge tubes (<xref ref-type="bibr" rid="ref17">Frey, 1986</xref>; <xref ref-type="bibr" rid="ref24">Korhola and Rautio, 2001</xref>). Most Cladocera remains were identified by their shell, headshield, postabdomen, and claw, and at least 100 individuals from each Cladocera (species) were counted in each sample (<xref ref-type="bibr" rid="ref21">Jiang and Du, 1979</xref>; <xref ref-type="bibr" rid="ref41">Szeroczy&#x0144;ska and Sarmaja-Korjonen, 2007</xref>). For the data on dating results and subfossil Bosminidae in the sedimentary cores, we refer to published literature and Supporting Information (<xref ref-type="bibr" rid="ref11">Cheng et al., 2019</xref>, <xref ref-type="bibr" rid="ref8">2020c</xref>, <xref ref-type="bibr" rid="ref10">2021</xref>). Bosminidae (<italic>Bosmina</italic> spp.) includes unidentified <italic>Bosmina</italic> spp., <italic>Bosmina longirostris</italic>, <italic>Bosmina</italic> (E.) <italic>longispina</italic>, and <italic>Bosmina</italic> (E.) <italic>coregoni</italic>.</p>
<table-wrap position="float" id="tab1">
<label>Table 1</label>
<caption>
<p>The physical and chemical water parameters noted in the sample sites.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Lake</th>
<th align="left" valign="top">Site</th>
<th align="left" valign="top">Season</th>
<th align="center" valign="top">Water depth (m)</th>
<th align="center" valign="top">Water temperature (&#x00B0;C)</th>
<th align="center" valign="top">pH</th>
<th align="center" valign="top">Transparency (cm)</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top" rowspan="9">Taihu lake</td>
<td align="left" valign="top" rowspan="3">TH-2 (31.40890&#x00B0;N, 120.04118&#x00B0;E)</td>
<td align="left" valign="top">Spring</td>
<td align="char" valign="top" char=".">2.2</td>
<td align="char" valign="top" char=".">19.3</td>
<td align="char" valign="top" char=".">8.49</td>
<td align="center" valign="top">73</td>
</tr>
<tr>
<td align="left" valign="top">Summer</td>
<td align="char" valign="top" char=".">2.8</td>
<td align="char" valign="top" char=".">28.9</td>
<td align="char" valign="top" char=".">8.9</td>
<td align="center" valign="top">25</td>
</tr>
<tr>
<td align="left" valign="top">Autumn</td>
<td align="char" valign="top" char=".">2.8</td>
<td align="char" valign="top" char=".">15</td>
<td align="char" valign="top" char=".">7.24</td>
<td align="center" valign="top">60</td>
</tr>
<tr>
<td align="left" valign="top" rowspan="3">TH-7 (31.15603&#x00B0;N, 120.05130&#x00B0;E)</td>
<td align="left" valign="top">Spring</td>
<td align="char" valign="top" char=".">2.8</td>
<td align="char" valign="top" char=".">17</td>
<td align="char" valign="top" char=".">8.5</td>
<td align="center" valign="top">25</td>
</tr>
<tr>
<td align="left" valign="top">Summer</td>
<td align="char" valign="top" char=".">3.5</td>
<td align="char" valign="top" char=".">31.9</td>
<td align="char" valign="top" char=".">9.09</td>
<td align="center" valign="top">23</td>
</tr>
<tr>
<td align="left" valign="top">Autumn</td>
<td align="char" valign="top" char=".">4</td>
<td align="char" valign="top" char=".">15</td>
<td align="char" valign="top" char=".">7.68</td>
<td align="center" valign="top">15</td>
</tr>
<tr>
<td align="left" valign="top" rowspan="3">TH-5 (31.08744&#x00B0;N, 120.51746&#x00B0;E)</td>
<td align="left" valign="top">Spring</td>
<td align="char" valign="top" char=".">1.5</td>
<td align="char" valign="top" char=".">18.9</td>
<td align="char" valign="top" char=".">8.77</td>
<td align="center" valign="top">41</td>
</tr>
<tr>
<td align="left" valign="top">Summer</td>
<td align="char" valign="top" char=".">1.7</td>
<td align="char" valign="top" char=".">30.5</td>
<td align="char" valign="top" char=".">8.66</td>
<td align="center" valign="top">28</td>
</tr>
<tr>
<td align="left" valign="top">Autumn</td>
<td align="char" valign="top" char=".">1.8</td>
<td align="char" valign="top" char=".">15</td>
<td align="char" valign="top" char=".">7.58</td>
<td align="center" valign="top">60</td>
</tr>
<tr>
<td align="left" valign="top" rowspan="5">Nanyi lake</td>
<td align="left" valign="top" rowspan="3">NYH (31.11354&#x00B0;N, 118.97826&#x00B0;E)</td>
<td align="left" valign="top">Spring</td>
<td align="char" valign="top" char=".">1.8</td>
<td align="char" valign="top" char=".">19.4</td>
<td align="char" valign="top" char=".">8.21</td>
<td align="center" valign="top">18</td>
</tr>
<tr>
<td align="left" valign="top">Summer</td>
<td align="char" valign="top" char=".">2.8</td>
<td align="char" valign="top" char=".">37.4</td>
<td align="char" valign="top" char=".">8.54</td>
<td align="center" valign="top">20</td>
</tr>
<tr>
<td align="left" valign="top">Autumn</td>
<td align="char" valign="top" char=".">2.6</td>
<td align="char" valign="top" char=".">27</td>
<td align="char" valign="top" char=".">8.79</td>
<td align="center" valign="top">40</td>
</tr>
<tr>
<td align="left" valign="top">NY-2 (31.06560&#x00B0;N, 118.95933&#x00B0;E)</td>
<td align="left" valign="top">Autumn</td>
<td align="char" valign="top" char=".">2.7</td>
<td align="char" valign="top" char=".">26</td>
<td align="char" valign="top" char=".">8.22</td>
<td align="center" valign="top">66</td>
</tr>
<tr>
<td align="left" valign="top">NY-3 (31.10030&#x00B0;N, 118.90244&#x00B0;E)</td>
<td align="left" valign="top">Autumn</td>
<td align="char" valign="top" char=".">2.4</td>
<td align="char" valign="top" char=".">26</td>
<td align="char" valign="top" char=".">8.07</td>
<td align="center" valign="top">67</td>
</tr>
<tr>
<td align="left" valign="top" rowspan="3">Shengjin lake</td>
<td align="left" valign="top" rowspan="3">SJH (30.38942&#x00B0; N, 117.04160&#x00B0; E)</td>
<td align="left" valign="top">Spring</td>
<td align="char" valign="top" char=".">0.6</td>
<td align="char" valign="top" char=".">20.5</td>
<td align="char" valign="top" char=".">7.38</td>
<td align="center" valign="top">17</td>
</tr>
<tr>
<td align="left" valign="top">Summer</td>
<td align="char" valign="top" char=".">2.1</td>
<td align="char" valign="top" char=".">33</td>
<td align="char" valign="top" char=".">7.5</td>
<td align="center" valign="top">38</td>
</tr>
<tr>
<td align="left" valign="top">Autumn</td>
<td align="char" valign="top" char=".">1.3</td>
<td align="char" valign="top" char=".">19</td>
<td align="char" valign="top" char=".">7.44</td>
<td align="center" valign="top">40</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="sec5">
<title>2.3. Statistical analysis</title>
<p>Graphical representations of modern zooplankton, Bosminidae, and &#x03B4;<sup>13</sup>C<sub>bos</sub> records were generated using Origin 8.0 and CorelDRAW 2018. Pearson&#x2019;s correlation analysis was conducted by IBM SPSS 19.0 (Statistical Graphics Corp, Princeton, United States) and Origin 8.0 using TN, TP, and Bosminidae to investigate the relationships between the biological indicator (Cladocera) and trophic indicators (TN and TP).</p>
</sec>
</sec>
<sec id="sec6" sec-type="results">
<title>3. Results</title>
<sec id="sec7">
<title>3.1. Variability in modern Bosminidae abundance</title>
<p>We identified the modern zooplankton in Taihu Lake, Nanyi Lake, and Shengjin Lake. The results showed that Cladocera were the dominant zooplankton species in the three lakes, with the exception of the total number of Copepoda in Shengjin Lake in summer (52 ind./L) exceeding that of Cladocera (44 ind./L) and Rotifera (5 ind./L) (<xref rid="fig2" ref-type="fig">Figure 2</xref>). There were higher proportions of Cladocera in zooplankton in the Nanyi Lake (NYH: mean 320 ind./L). Values in the western area of the Taihu Lake (TH-2: mean 127 ind./L) and central area (TH-7: mean 198 ind./L) were much higher than in the Shengjin Lake (SJH: mean 24 ind./L). In spring, the total number of Cladocera identified in TH-7 and NYH reached the maximum values of 478 ind./L and 805 ind./L, respectively (<xref rid="fig2" ref-type="fig">Figure 2</xref>). The abundance of zooplankton in the eastern area (TH-5) of the Taihu Lake was far lower than those in the western and central areas (<xref rid="fig2" ref-type="fig">Figure 2</xref>). Only the abundance of Cladocera in summer was greater than 50 ind./L in TH-5, while the abundances of Cladocera, Copepoda, and Rotifera in spring and autumn were relatively low and balanced. The total number of zooplankton in SJH was similar to that in TH-5 with a low abundance in each season (<xref rid="fig2" ref-type="fig">Figure 2</xref>).</p>
<fig position="float" id="fig2">
<label>Figure 2</label>
<caption>
<p>Modern zooplankton and Bosminidae from the Taihu Lake (TH-2, TH-7, and TH-5), Nanyi Lake (NYH), and Shengjin Lake (SJH) in the main living seasons.</p>
</caption>
<graphic xlink:href="fevo-11-1121632-g002.tif"/>
</fig>
<p>The dominant species of the zooplankton composition in different seasons in the three lakes was Cladocera, which mainly consisted of Bosminidae (<xref rid="fig2" ref-type="fig">Figure 2</xref>). The composition characteristics of Bosminidae concentrations in each lake and season were consistent with the distribution of the total number of Cladocera. The total abundance of Bosminidae in TH-2 and TH-7 with severe eutrophication and in NYH in the transitional stage from the mesotrophic to the eutrophic status exceeded 400 ind./L, with a relative proportion of more than 95% in spring. The peak values for Bosminidae in other lake areas mostly reached in summer and autumn.</p>
</sec>
<sec id="sec8">
<title>3.2. Changes in trophic levels (TN and TP) and subfossil Bosminidae abundances since the 1950s</title>
<p>Information about species and abundances of subfossil Cladocera and trophic indices (TN and TP) has been described in detail elsewhere (<xref ref-type="bibr" rid="ref9">Cheng et al., 2020a</xref>,<xref ref-type="bibr" rid="ref6">b</xref>,<xref ref-type="bibr" rid="ref8">c</xref>, <xref ref-type="bibr" rid="ref10">2021</xref>). For data on Bosminidae, total Cladocera, and chronology, we refer to the &#x201C;Supporting Information.&#x201D; The trophic levels (TN-% and TP-mg/g) remained at a high level since the 1950s, with average values of 0.11% and 0.68&#x2009;mg/g in the TH-2 core, 0.97% and 0.42&#x2009;mg/g in the TH-5 core, 0.07% and 0.43&#x2009;mg/g in the TH-7 core, 0.13% and 0.50&#x2009;mg/g in the NY-2 core, 0.16% and 0.53&#x2009;mg/g in the NY-3 core, and 0.28% and 0.59&#x2009;mg/g in the SJH core (<xref rid="fig3" ref-type="fig">Figures 3</xref>, <xref rid="fig4" ref-type="fig">4</xref>). The values of TN and TP in the west (TH-2 core) and central (TH-7 core) areas of the Taihu Lake significantly increased, while the values of TN in the east (TH-5 core) tended to decline but were kept at a higher level (0.92%&#x2009;~&#x2009;1.0%) than in the TH-2 core (0.08%&#x2009;~&#x2009;0.18%) and TH-7 core (0.06%&#x2009;~&#x2009;0.10%). The values of TP in the cores of TH-2, TH-7, and TH-5 ranged from 0.12 to 0.48&#x2009;mg/g, 0.35 to 0.51&#x2009;mg/g, and 0.40 to 0.45&#x2009;mg/g, respectively. The abundance of Bosminidae in the Taihu Lake changed consistently with TN and TP in the western and central areas, but there was a significant decreasing trend in the eastern Taihu Lake (<xref rid="fig3" ref-type="fig">Figures 3</xref>, <xref rid="fig4" ref-type="fig">4</xref>). The values of TN and TP in the Nanyi Lake and Shengjin Lake clearly increased. The values of TN in the cores of NY-2, NY-3, and SJH ranged from 0.08 to 0.20%, 0.10 to 0.21%, and 0.23 to 0.31%, respectively. The values of TP in the cores of NY-2, NY-3, and SJH changed from 0.31 to 0.69&#x2009;mg/g, 0.37 to 0.68&#x2009;mg/g, and 0.45 to 0.64&#x2009;mg/g, respectively. The abundance of Bosminidae also increased corresponding to the increase in nitrogen and phosphorus concentrations in the Nanyi Lake and Shengjin Lake.</p>
<fig position="float" id="fig3">
<label>Figure 3</label>
<caption>
<p>Changes in TN and Bosminidae (<italic>Bosmina</italic> spp.) in the Taihu Lake <bold>(A&#x2013;C)</bold>, Nanyi Lake <bold>(D,E)</bold>, and Shengjin Lake <bold>(F)</bold> since the 1950s.</p>
</caption>
<graphic xlink:href="fevo-11-1121632-g003.tif"/>
</fig>
<fig position="float" id="fig4">
<label>Figure 4</label>
<caption>
<p>Changes in TP and Bosminidae (<italic>Bosmina</italic> spp.) in the Taihu Lake <bold>(A&#x2013;C)</bold>, Nanyi Lake <bold>(D,E)</bold>, and Shengjin Lake <bold>(F)</bold> since the 1950s.</p>
</caption>
<graphic xlink:href="fevo-11-1121632-g004.tif"/>
</fig>
<p>The abundances of Cladocera sum and Bosminidae in the cores of TH-2 and TH-7 remained at a high level. Among them, the abundances of total Cladocera and Bosminidae in the TH-2 core ranged from 1,080&#x2009;~&#x2009;5,295 ind./g with a mean value of 3,048 ind./g, i.e., 94%&#x2009;~&#x2009;98% with a mean value of 96%, respectively, while those in the TH-7 core ranged from approximately 2,507&#x2009;~&#x2009;9,373 ind./g with a mean value of 5,140 ind./g, i.e., 90%&#x2009;~&#x2009;96% with a mean value of 94%, respectively (<xref rid="fig5" ref-type="fig">Figure 5</xref>). After the 1950s, the Cladocera sum decreased in the TH-2 core, but the abundance of Bosminidae increased significantly. The change in Cladocera sum and Bosminidae abundances in the TH-7 core was similar to that in the TH-2 core; that is, the fluctuation in Bosminidae increased after the 1950s (<xref rid="fig5" ref-type="fig">Figure 5</xref>). The change in Cladocera sum in the TH-5 core corresponding to that of Bosminidae decreased after the 1950s and their changed ranges were 463&#x2009;~&#x2009;1,127 ind./g with a mean value of 758 ind./g, i.e., 12%&#x2009;~&#x2009;86% with a mean value of 44%, respectively. The change in the abundance of Bosminidae was consistent with that of the Cladocera sum that increased gradually with time in Nanyi Lake and Shengjin Lake (<xref rid="fig5" ref-type="fig">Figure 5</xref>). The ranges for Cladocera sum and Bosminidae in the NY-2 core were 111&#x2009;~&#x2009;901 ind./g with a mean value of 444 ind./g, i.e., 71%&#x2009;~&#x2009;95% with a mean value of 86%, respectively. Values in the NY-3 core were 101&#x2009;~&#x2009;639 ind./g with a mean value of 400 ind./g, i.e., 53%&#x2009;~&#x2009;89% with a mean value of 77%, respectively. The abundances of Cladocera sum and Bosminidae in Shengjin Lake (SJH core) were relatively lower than those of in the other two lakes, which changed from 241&#x2009;~&#x2009;487 ind./g with a mean value of 366 ind./g, i.e., 13%&#x2009;~&#x2009;69% with a mean value of 48%, respectively (<xref rid="fig5" ref-type="fig">Figure 5</xref>).</p>
<fig position="float" id="fig5">
<label>Figure 5</label>
<caption>
<p>Changes in Cladocera sum and Bosminidae (<italic>Bosmina</italic> spp.) in the Taihu Lake <bold>(A&#x2013;C)</bold>, Nanyi Lake <bold>(D,E)</bold>, and Shengjin Lake <bold>(F)</bold> since the 1950s.</p>
</caption>
<graphic xlink:href="fevo-11-1121632-g005.tif"/>
</fig>
</sec>
<sec id="sec9">
<title>3.3. Changes in the &#x03B4;<sup>13</sup>C values of subfossil Bosminidae in Taihu Lake since the 1950s</title>
<p>To accurately track the flow characteristics of carbon sources in primary consumers, the results of the stable carbon isotope analysis of subfossil Bosminidae (&#x03B4;<sup>13</sup>C<sub>bos</sub>) in the cores of TH-2 and TH-7 from the heavily eutrophic area in Taihu Lake after the 1950s are shown in <xref rid="fig6" ref-type="fig">Figure 6</xref>. The mean values of &#x03B4;<sup>13</sup>C<sub>bos</sub> in the cores of TH-2 and TH-7 showed relatively consistent mean values of &#x2212;22.45&#x2030; and&#x2009;&#x2212;&#x2009;22.51&#x2030;, respectively. However, the variation range in the &#x03B4;<sup>13</sup>C<sub>bos</sub> value of the TH-2 core was higher than that of the TH-7 core (<xref rid="fig6" ref-type="fig">Figure 6A</xref>). The &#x03B4;<sup>13</sup>C<sub>bos</sub> values in the TH-2 core varied in the range of &#x2212;25.77&#x2030;&#x2009;~&#x2009;&#x2212;19.54&#x2030;, while the &#x03B4;<sup>13</sup>C<sub>bos</sub> values in the TH-7 core changed from &#x2212;23.40&#x2030; to &#x2212;20.80&#x2030;. After the 1980s, with intensified eutrophication of Taihu Lake, the &#x03B4;<sup>13</sup>C<sub>bos</sub> values of the two cores shared a common downward trend that was lower than the mean values (<xref rid="fig6" ref-type="fig">Figure 6B</xref>).</p>
<fig position="float" id="fig6">
<label>Figure 6</label>
<caption>
<p>Changes in the &#x03B4;<sup>13</sup>C values of subfossil Bosminidae in the Taihu Lake after the 1950s. <bold>(A)</bold> Statistical distribution of &#x03B4;<sup>13</sup>C<sub>bos</sub> in the cores of TH-2 and TH-7 and <bold>(B)</bold> temporal distribution of &#x03B4;<sup>13</sup>C<sub>bos</sub> in the cores of TH-2 and TH-7.</p>
</caption>
<graphic xlink:href="fevo-11-1121632-g006.tif"/>
</fig>
</sec>
<sec id="sec10">
<title>3.4. Pearson&#x2019;s correlation analysis between Bosminidae abundance change and trophic level</title>
<p>The Pearson correlation analysis between Bosminidae and trophic indices showed that the abundance of Bosminidae, including <italic>B. longirostris</italic> and <italic>B</italic> (E.) <italic>longispina</italic>, were significantly correlated with TN and TP (<xref rid="tab2" ref-type="table">Table 2</xref>; <xref ref-type="bibr" rid="ref9">Cheng et al., 2020a</xref>,<xref ref-type="bibr" rid="ref6">b</xref>,<xref ref-type="bibr" rid="ref8">c</xref>, <xref ref-type="bibr" rid="ref10">2021</xref>). There were significant positive correlations between Bosminidae and TN in the cores of TH-2, NY-2, and NY-3. The Bosminidae were positively correlated with TP in all cores except TH-5, which had a significant negative correlation. In addition, there were significant positive correlations between Bosminidae and TP in the cores of Nanyi Lake and Shengjin Lake. The eutrophic species <italic>B</italic>. <italic>longirostris</italic> in the three lakes was significantly positively correlated with TN, except in the TH-5 core. There were significant positive correlations between <italic>B</italic>. <italic>longirostris</italic> and TP in the cores of TH-2, NY-2, NY-3, and SJH. The oligotrophic species <italic>B</italic> (E.) <italic>longispina</italic> had a significant negative correlation with TN in the cores of TH-2 and TH-7 but a significant positive correlation in the two cores of Nanyi Lake. <italic>B</italic> (E.) <italic>longispina</italic> was negatively correlated with TP in the cores of TH-2 and TH-5 and was positively correlated with TP in the cores of NY-2 and NY-3.</p>
<table-wrap position="float" id="tab2">
<label>Table 2</label>
<caption>
<p>Pearson&#x2019;s correlation analysis between the trophic indices TN and TP with the species of Bosminidae. Data sources of TH-2, TH-7, TH-5, NY-2, NY-3, and SJH cores were taken from <xref ref-type="bibr" rid="ref9">Cheng et al. (2020a</xref>,<xref ref-type="bibr" rid="ref6">b</xref>,<xref ref-type="bibr" rid="ref8">c</xref>, <xref ref-type="bibr" rid="ref10">2021)</xref>.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th/>
<th align="center" valign="top">TN/Bosminidae</th>
<th align="center" valign="top">TN/<italic>B. longirostris</italic></th>
<th align="center" valign="top">TN/<italic>B</italic> (E.) <italic>longispina</italic></th>
<th align="center" valign="top">TP/Bosminidae</th>
<th align="center" valign="top">TP/<italic>B</italic>. <italic>longirostris</italic></th>
<th align="center" valign="top">TP/<italic>B</italic> (E.) <italic>longispina</italic></th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">TH-2 (<italic>n</italic>&#x2009;=&#x2009;13)</td>
<td align="char" valign="top" char=".">0.673&#x002A;</td>
<td align="char" valign="top" char=".">0.819&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">&#x2212;0.794&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.493</td>
<td align="char" valign="top" char=".">0.630&#x002A;</td>
<td align="char" valign="top" char=".">&#x2212;0.718&#x002A;&#x002A;</td>
</tr>
<tr>
<td align="left" valign="top">TH-7 (<italic>n</italic>&#x2009;=&#x2009;13)</td>
<td align="char" valign="top" char=".">0.279</td>
<td align="char" valign="top" char=".">0.651&#x002A;</td>
<td align="char" valign="top" char=".">&#x2212;0.764&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.195</td>
<td align="char" valign="top" char=".">0.345</td>
<td align="char" valign="top" char=".">&#x2212;0.291</td>
</tr>
<tr>
<td align="left" valign="top">TH-5 (<italic>n</italic>&#x2009;=&#x2009;12)</td>
<td align="char" valign="top" char=".">0.376</td>
<td align="char" valign="top" char=".">0.154</td>
<td align="char" valign="top" char=".">0.33</td>
<td align="char" valign="top" char=".">&#x2212;0.720&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">&#x2212;0.176</td>
<td align="char" valign="top" char=".">&#x2212;0.646&#x002A;</td>
</tr>
<tr>
<td align="left" valign="top">NY-2 (<italic>n</italic>&#x2009;=&#x2009;15)</td>
<td align="char" valign="top" char=".">0.853&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.747&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.799&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.851&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.726&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.851&#x002A;&#x002A;</td>
</tr>
<tr>
<td align="left" valign="top">NY-3 (<italic>n</italic>&#x2009;=&#x2009;14)</td>
<td align="char" valign="top" char=".">0.897&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.842&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.855&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.926&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.867&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.875&#x002A;&#x002A;</td>
</tr>
<tr>
<td align="left" valign="top">SJH (<italic>n</italic>&#x2009;=&#x2009;15)</td>
<td align="char" valign="top" char=".">0.294</td>
<td align="char" valign="top" char=".">0.665&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">&#x2212;0.484</td>
<td align="char" valign="top" char=".">0.715&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">0.907&#x002A;&#x002A;</td>
<td align="char" valign="top" char=".">&#x2212;0.064</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p>&#x002A;Correlation is significant at the <italic>p</italic>&#x2009;&#x003C;&#x2009;0.05 level. &#x002A;&#x002A;Correlation is significant at the <italic>p</italic>&#x2009;&#x003C;&#x2009;0.01 level.</p>
</table-wrap-foot>
</table-wrap>
</sec>
</sec>
<sec id="sec11" sec-type="discussions">
<title>4. Discussion</title>
<p>The lake trophic status in the lower reaches of the Yangtze River from a recent study showed that most of the lakes have been categorized into the mesotrophic or the eutrophic status (<xref ref-type="bibr" rid="ref7">Cheng and Li, 2006</xref>; <xref ref-type="bibr" rid="ref37">Qin et al., 2013</xref>). The trophic levels of the three lakes, located in the middle and lower reaches of the Yangtze River, have also reached the mid-eutrophic level and above and are increasing from Shengjin Lake to Nanyi Lake and then to Taihu Lake, which is closely related to the distribution of economic development, population, and urbanization in each region (<xref ref-type="bibr" rid="ref37">Qin et al., 2013</xref>; <xref ref-type="bibr" rid="ref52">Zhang M. et al., 2018</xref>; <xref ref-type="bibr" rid="ref39">Shi et al., 2019</xref>; <xref ref-type="bibr" rid="ref8">Cheng et al., 2020c</xref>, <xref ref-type="bibr" rid="ref10">2021</xref>). An analysis of modern zooplankton compositions showed that Cladocera was dominant in the three lakes and that the abundance was gradually increasing from Shengjin Lake through Nanyi Lake to Taihu Lake (<xref rid="fig2" ref-type="fig">Figure 2</xref>). Furthermore, the abundances of Bosminidae in the Nanyi Lake and in the western and central areas of the Taihu Lake were greater than 90% (<xref rid="fig2" ref-type="fig">Figure 2</xref>). This showed that Bosminidae abundance increased corresponding to the increasing trophic level (<xref ref-type="bibr" rid="ref29">Li et al., 2016</xref>; <xref ref-type="bibr" rid="ref6">Cheng et al., 2020b</xref>; <xref ref-type="bibr" rid="ref28">Li et al., 2021</xref>). However, a higher Copepod density was recorded in summer than that of Cladocera and there was a low abundance of Bosminidae in the composition of modern zooplankton in the Shengjin Lake, which might indirectly suggest that the Bosminidae did not have a reproductive advantage under low trophic levels. The subfossil Cladocera in the sedimental cores of the three lakes also showed that the Bosminidae was a broadly dominant species (<xref rid="fig5" ref-type="fig">Figure 5</xref>). Especially in Taihu Lake, the density of Bosminidae subfossils was close to 10,000 ind./cm<sup>3</sup> (<xref ref-type="bibr" rid="ref11">Cheng et al., 2019</xref>). In Nanyi Lake and Shengjin Lake, where trophic levels had increased significantly since the 1950s, the abundance of subfossil Bosminidae also increased (<xref rid="fig5" ref-type="fig">Figure 5</xref>). In addition, among the modern Cladocera in the three lakes, Bosminidae was the dominant species, which was consistent with the Cladocera subfossil results at the same location and also indirectly proved that Bosminidae subfossils were well preserved in lakes of the middle and lower reaches of the Yangtze River.</p>
<p>In terms of space, there were huge differences in the economic development level, the urbanization level, and population along the Yangtze River from west to east. Taihu Lake is located in the eastern delta of the Yangtze River, which has an extremely developed economy and a very large population (<xref ref-type="bibr" rid="ref38">Qin et al., 2007</xref>). Because Taihu Lake is located near many developed cities such as Shanghai, Suzhou, and Wuxi, a large quantity of nutrients such as nitrogen and phosphorus flow into Taihu Lake on account of human activities, which are far greater in Taihu Lake than in Nanyi Lake and Shengjin Lake in the Anhui Province (<xref ref-type="bibr" rid="ref12">Dai et al., 2016</xref>). Agricultural and fisheries development in Nanyi Lake is more adequate than in Shengjin Lake (<xref ref-type="bibr" rid="ref44">Wang et al., 2013</xref>). As a national nature reserve, Shengjin Lake has a relatively good environment and low nutrient level compared with the other two lakes (<xref ref-type="bibr" rid="ref43">Wang et al., 2015</xref>). The spatial gradient distributions of Bosminidae abundance in the three lakes were in line with the different economic development levels (<xref rid="fig5" ref-type="fig">Figure 5</xref>). Thus, it could be inferred that there were different types of interference of human activities around the three lakes.</p>
<p>The significant positive relationship between Bosminidae and eutrophic species <italic>B. longirostris</italic> with TN and TP further proved that Bosminidae had an advantage in the eutrophic process (<xref rid="tab2" ref-type="table">Table 2</xref>). In particular, <italic>B. longirostris</italic> demonstrated strong adaptability and sensitivity in a wide range of water environments, such as the eutrophic status, warming waters, and metal-contaminated lakes in previous studies (<xref ref-type="bibr" rid="ref4">Boucherle and Z&#x00FC;llig, 1983</xref>; <xref ref-type="bibr" rid="ref13">De Kluijver et al., 2012</xref>; <xref ref-type="bibr" rid="ref25">Labaj et al., 2015</xref>; <xref ref-type="bibr" rid="ref23">Kong et al., 2017</xref>; <xref ref-type="bibr" rid="ref6">Cheng et al., 2020b</xref>). Our study showed that Bosminidae abundance increased with the increase in the outbreak intensity of cyanobacteria in eutrophic lake areas (<xref rid="fig3" ref-type="fig">Figures 3</xref>, <xref rid="fig4" ref-type="fig">4</xref>). Especially in the west and central lake areas of Taihu Lake with serious eutrophication, the concentration of Bosminidae has increased to a relatively stable state. While Nanyi Lake and Shengjin Lake are in the stage of rising trophic levels, and the abundance of Bosminidae is also showing a synchronous rising trend (<xref rid="fig3" ref-type="fig">Figure 3</xref>). Although previous studies suggested that Bosminidae were too small to feed on Microcystis directly with a large size (<xref ref-type="bibr" rid="ref21">Jiang and Du, 1979</xref>; <xref ref-type="bibr" rid="ref27">Li and Chen, 2010</xref>), more studies showed that Microcystis tended to form large suspended aggregates with materials after cell death including dissolved organic carbon, dissolved inorganic carbon, and dissolved inorganic nitrogen and phosphorus in the water column and then were likely the main diet of Bosminidae (<xref ref-type="bibr" rid="ref13">De Kluijver et al., 2012</xref>; <xref ref-type="bibr" rid="ref2">Agasild et al., 2019</xref>; <xref ref-type="bibr" rid="ref6">Cheng et al., 2020b</xref>). It could be speculated that cyanobacteria blooms might change the food preference of the zooplankton Bosminidae. At the same time, the water environment also changed greatly due to excessive reproduction of cyanobacteria; thus, Bosminidae made timely adaptive adjustments to the original living environment and food source changes (<xref ref-type="bibr" rid="ref2">Agasild et al., 2019</xref>). For example, Cladocera&#x2019;s size gradually became smaller to better escape the predation of zooplankton-feeding fish (<xref ref-type="bibr" rid="ref40">Shurin, 2001</xref>; <xref ref-type="bibr" rid="ref20">Jeppesen et al., 2003</xref>; <xref ref-type="bibr" rid="ref32">Liu et al., 2009</xref>). Accordingly, in lake areas where cyanobacteria blooms were stronger, the density of small-size species of Bosminidae was greater and other species of zooplankton may have decreased or even gone extinct (<xref ref-type="bibr" rid="ref22">Jiang et al., 2013</xref>; <xref ref-type="bibr" rid="ref29">Li et al., 2016</xref>).</p>
<p>The present study revealed that Bosminidae could accelerate reproduction under rich food sources, resulting in excessive abundance (accounting for more than 90% of the total number of Cladocera) (<xref rid="fig2" ref-type="fig">Figure 2</xref>). However, water temperature also impacts the body size and community trophic structure of zooplankton (<xref ref-type="bibr" rid="ref18">Gao et al., 2021</xref>). The three shallow freshwater lakes located in the middle and lower reaches of the Yangtze River in a subtropical zone had suitable temperature conditions that produced a favorable habitat for most lake creatures, including the zooplankton. However, a strong disturbance can easily occur in these shallow freshwater lakes, which can result in the release of sediment nitrogen and phosphorus and a large amount of exogenous nitrogen and phosphorus inputs from catchment by increasing human activities (<xref ref-type="bibr" rid="ref55">Zhu et al., 2019</xref>). Excessive nitrogen and phosphorus inputs caused cyanobacteria blooms that seriously threatened the survival of most aquatic organisms such as fish. Large aquatic plants and other biodiversity significantly decreased, and this finally led to the imbalance of lake ecosystems (<xref ref-type="bibr" rid="ref37">Qin et al., 2013</xref>). Surprisingly, the cyanobacteria outbreak provided favorable conditions for the expansion of the Bosminidae (<xref ref-type="bibr" rid="ref13">De Kluijver et al., 2012</xref>; <xref ref-type="bibr" rid="ref6">Cheng et al., 2020b</xref>). The changes in &#x03B4;<sup>13</sup>C<sub>bos</sub> values after 1950s also revealed the flow characteristics of carbon sources in the Bosminidae (<xref rid="fig6" ref-type="fig">Figure 6</xref>). In particular, after the 1980s (after China&#x2019;s Reform and Open Policy), with increasing lake eutrophication, the &#x03B4;<sup>13</sup>C<sub>bos</sub> values exhibited a significant negative trend (<xref rid="fig6" ref-type="fig">Figure 6</xref>), which was consistent with the change in organic carbon isotopes in sediments (&#x03B4;<sup>13</sup>C<sub>org</sub>; <xref ref-type="bibr" rid="ref6">Cheng et al., 2020b</xref>). The &#x03B4;<sup>13</sup>C value of algae in Taihu Lake was similar to the value of &#x03B4;<sup>13</sup>C in modern Bosminidae during the cyanobacteria bloom (<xref ref-type="bibr" rid="ref6">Cheng et al., 2020b</xref>). This further indicated that the cyanobacteria outbreak provided a rich food source for Bosminidae. Bosminidae propagation in large numbers due to the outbreak of cyanobacteria also showed that Bosminidae had its own unique adaptability to the eutrophic environment and strong competitiveness compared with other zooplankton. The high adaptive ability of Bosminidae to eutrophication could indicate that it is more competitive than other larger Cladocera species.</p>
<p>Our data on subfossil Cladocera in the TH-5 core of East Taihu Lake showed that the total Cladocera and Bosminidae abundances were lower than those found in the core of other lake areas and tended to decrease after the 1950s (<xref rid="fig2" ref-type="fig">Figure 2</xref>). This was due to intensification of the swamping trend in East Taihu Lake, the water level reduction, aquatic macrophyte development, and water stagnation for prolonged periods of time caused by enclosed fish cultures and crab farming practices. These are extremely detrimental to the survival of the planktonic species Bosminidae but provide a more suitable habitat for the littoral Cladocera species (<xref ref-type="bibr" rid="ref49">Yang et al., 2003</xref>; <xref ref-type="bibr" rid="ref26">Li, 2004</xref>; <xref ref-type="bibr" rid="ref9">Cheng et al., 2020a</xref>). The significant negative correlation between Bosminidae and TP also indirectly proved that the environment of the East Taihu Lake was not conducive to the survival of Bosminidae (<xref rid="tab2" ref-type="table">Table. 2</xref>). It could be seen that the trophic level was not the only factor limiting the growth of Bosminidae, but it was the key factor behind the rapid expansion of Bosminidae, once certain restrictive conditions were exceeded. As shown in the western and central areas of Taihu Lake, Bosminidae reproduction expanded and abundance increased once the trophic level was enriched and the water level depth met the living conditions of the planktonic species Bosminidae (<xref rid="fig2" ref-type="fig">Figures 2</xref>, <xref rid="fig5" ref-type="fig">5</xref>). Additionally, the significant positive correlations between oligotrophic species Bosminidae with TN and TP in Nanyi Lake were opposite of those in Taihu Lake, which was closely related to the fact that Nanyi Lake was in a critical period of transition from the mesotrophic to the eutrophic status (<xref ref-type="bibr" rid="ref10">Cheng et al., 2021</xref>). Research by <xref ref-type="bibr" rid="ref16">Dodson (1992)</xref> showed that the abundance of zooplankton usually increased with increasing nutritional levels within a certain range. The current trophic level of the Nanyi Lake is still increasing, but it has not reached the eutrophic level as in the central and western areas of Taihu Lake. Therefore, the abundance of oligotrophic species increased significantly with the increase in trophic level.</p>
</sec>
<sec id="sec12" sec-type="conclusions">
<title>5. Conclusion</title>
<p>The spatial distribution of the three subtropical shallow freshwater lakes in the middle and lower reaches of the Yangtze River was characterized by gradually increasing nutrient levels from west to east. An analysis of the composition of zooplankton in the modern lake water of the three lakes and Cladocera subfossils from the sedimental cores revealed that the Cladocera planktonic species Bosminidae changed relatively consistently with the temporal and spatial distributions of the nutrient levels in the three lakes, indicating that the small planktonic Bosminidae species had unique sensitivity and adaptability during lake eutrophication. In addition, the significant correlation between Bosminidae and nutrient indicators such as TN and TP, as well as the gradually negative &#x03B4;<sup>13</sup>C<sub>bos</sub> values under increasing eutrophication, further proved that the abundance of Bosminidae changed with the change in eutrophication level. This reflected the change in food source preference of the Bosminidae and its strong adaptability to harsh environments during lake eutrophication. Bosminidae was more adaptive to the change in this environment, which showed that the genus was highly sensitive to changes in the lake environment and can indicate the evolution of the lake. This study offered a new alternative index for paleoecology research and also provided a new idea for mechanism research on modern lake eutrophication environments.</p>
</sec>
<sec id="sec13" sec-type="data-availability">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="supplementary-material" rid="SM1">Supplementary material</xref>, further inquiries can be directed to the corresponding authors.</p>
</sec>
<sec id="sec14">
<title>Author contributions</title>
<p>LC: writing&#x2013;original draft, validation, resources, and formal analysis. XG, GW, and JL: visualization and investigation. ZD: investigation and field work. BX: supervision, project administration, and funding acquisition. CZ: supervision, visualization, investigation, and writing&#x2013;editing. QJ: software and resources. All authors contributed to the article and approved the submitted version.</p>
</sec>
<sec id="sec15" sec-type="funding-information">
<title>Funding</title>
<p>This research was supported by grants from the Natural Science Foundation of China project (42002204 and 42177426), the National Key Research and Development Program of China (2019YFA0607100), and the Jiangsu Special Fund on Technology Innovation of Carbon Dioxide Peaking and Carbon Neutrality (BK20220016).</p>
</sec>
<sec id="conf1" sec-type="COI-statement">
<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 id="sec100" sec-type="disclaimer">
<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>
</body>
<back>
<sec id="sec17" sec-type="supplementary-material">
<title>Supplementary material</title>
<p>The Supplementary material for this article can be found online at: <ext-link xlink:href="https://www.frontiersin.org/articles/10.3389/fevo.2023.1121632/full#supplementary-material" ext-link-type="uri">https://www.frontiersin.org/articles/10.3389/fevo.2023.1121632/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Table_1.XLSX" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet" xmlns:xlink="http://www.w3.org/1999/xlink"/>
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