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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Ecol. Evol.</journal-id>
<journal-title-group>
<journal-title>Frontiers in Ecology and Evolution</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Ecol. Evol.</abbrev-journal-title>
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<issn pub-type="epub">2296-701X</issn>
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<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-meta>
<article-id pub-id-type="doi">10.3389/fevo.2025.1744072</article-id>
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<article-categories>
<subj-group subj-group-type="heading">
<subject>Original Research</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>A comparative study of predation rhythms on cladocerans by juvenile invasive crayfish and native shrimp</article-title>
</title-group>
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<name><surname>Zhang</surname><given-names>Hui</given-names></name>
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<name><surname>Jiao</surname><given-names>Yiying</given-names></name>
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<name><surname>Wan</surname><given-names>Liang</given-names></name>
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<name><surname>Zhao</surname><given-names>Xiaoyao</given-names></name>
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<name><surname>Jeppesen</surname><given-names>Erik</given-names></name>
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<name><surname>Chen</surname><given-names>Feizhou</given-names></name>
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<aff id="aff1"><label>1</label><institution>Key Laboratory of Intelligent Health Perception and Ecological Restoration of Rivers and Lakes, Ministry of Education, Hubei University of Technology</institution>, <city>Wuhan</city>,&#xa0;<country country="cn">China</country></aff>
<aff id="aff2"><label>2</label><institution>Hubei Key Laboratory of Environmental Geotechnology and Ecological Remediation for Lake and River, Hubei University of Technology</institution>, <city>Wuhan</city>,&#xa0;<country country="cn">China</country></aff>
<aff id="aff3"><label>3</label><institution>Hubei Fisheries Science Research Institute</institution>, <city>Wuhan</city>,&#xa0;<country country="cn">China</country></aff>
<aff id="aff4"><label>4</label><institution>Department of Ecoscience, Aarhus University</institution>, <city>Aarhus</city>,&#xa0;<country country="dk">Denmark</country></aff>
<aff id="aff5"><label>5</label><institution>Institute for Ecological Research and Pollution Control of Plateau Lakes, School of Ecology and Environmental Science, Yunnan University</institution>, <city>Kunming</city>,&#xa0;<country country="cn">China</country></aff>
<aff id="aff6"><label>6</label><institution>Sino-Danish Centre for Education and Research, University of Chinese Academy of Sciences</institution>, <city>Beijing</city>,&#xa0;<country country="cn">China</country></aff>
<aff id="aff7"><label>7</label><institution>Key Laboratory of Lake and Watershed Science for Water Security, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences</institution>, <city>Nanjing</city>,&#xa0;<country country="cn">China</country></aff>
<author-notes>
<corresp id="c001"><label>*</label>Correspondence: Hui Zhang, <email xlink:href="mailto:huizhangeco@163.com">huizhangeco@163.com</email>; Jian Gao, <email xlink:href="mailto:jgao13@hotmail.com">jgao13@hotmail.com</email></corresp>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-01-12">
<day>12</day>
<month>01</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2025</year>
</pub-date>
<volume>13</volume>
<elocation-id>1744072</elocation-id>
<history>
<date date-type="received">
<day>11</day>
<month>11</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>22</day>
<month>12</month>
<year>2025</year>
</date>
<date date-type="rev-recd">
<day>14</day>
<month>12</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2026 Zhang, Liu, Gao, Liao, Wang, Ji, Jiao, Wan, Zhao, Jeppesen and Chen.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Zhang, Liu, Gao, Liao, Wang, Ji, Jiao, Wan, Zhao, Jeppesen and Chen</copyright-holder>
<license>
<ali:license_ref start_date="2026-01-12">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. 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.</license-p>
</license>
</permissions>
<abstract>
<p>The red swamp crayfish <italic>Procambarus clarkii</italic> is one of the most widely distributed invasive species in the world. Effects of juvenile crayfish (&lt; 5&#xa0;cm in body length) in lake ecosystems remain largely unknown, despite that they have a great potential of preying upon zooplankton. The shrimp <italic>Exopalaemon modestus</italic> is one of the most abundant native shrimps in China and also predate on zooplankton. The predation rhythm of juvenile crayfish on zooplankton and how it differs from native shrimps remain to be studied. We elucidated the predation rhythms of juvenile and sub-adult crayfish and shrimps on <italic>Simocephalus mixtus</italic>, a common Cladocera in the littoral region of freshwater lakes. Predation rates during the day or at night were measured for juvenile crayfish (~3.75 cm in body length), sub-adult crayfish (~6.68 cm) and juvenile shrimp (~3.88 cm) at different zooplankton densities (18, 54, 108 ind./L representing low, medium and high natural densities, respectively). The results showed that (1) juvenile crayfish predated slightly more at night than during the day, and with significantly higher predation rates than sub-adult crayfish; (2) Juvenile shrimp predated significantly more at night than during the day, as predation was almost absent during the day; (3) Juvenile shrimp had slightly higher night-time predation rates than juvenile crayfish, however, their daytime predation rates were significantly lower at medium and high zooplankton densities. Juvenile crayfish fed for a longer period than shrimp of similar length, exhibiting higher feeding capacity on zooplankton which supports the inherent superiority hypothesis that invasive species possess advantages over native species in feeding capacity. Our study provides information about the predation rhythms on Cladocera of early stages of crayfish and of shrimp, that may help in explaining, in part, the invasion success of red swamp crayfish.</p>
</abstract>
<kwd-group>
<kwd>feeding rhythms</kwd>
<kwd>native shrimp</kwd>
<kwd>predation rates</kwd>
<kwd>red swamp crayfish</kwd>
<kwd>zooplankton</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was received for this work and/or its publication. This study was supported by the open project funding of Key Laboratory of Intelligent Health Perception and Ecological Restoration of Rivers and Lakes, Ministry of Education (HGKFZ04, HGKFZ08), the open project funding of Hubei Key Laboratory of Environmental Geotechnology and Ecological Remediation for Lake &amp; River, Hubei University of Technology (HJKFYB202403), the National Natural Science Foundation of China (Grant No. 32471648), the Nature Science Foundation of Hubei Province (2025AFB524) and the Green Industrial Science and Technology Leading Project of Hubei University of Technology (XJ2024000401). Erik Jeppesen is thankful for the support from Yunnan Provincial Council of Academicians and Experts Workstations (202405AF140006).</funding-statement>
</funding-group>
<counts>
<fig-count count="4"/>
<table-count count="2"/>
<equation-count count="1"/>
<ref-count count="68"/>
<page-count count="9"/>
<word-count count="3438"/>
</counts>
<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Population, Community, and Ecosystem Dynamics</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>Red swamp crayfish <italic>Procambarus clarkii</italic> is one of the most important invasive species worldwide, the only alien freshwater crayfish introduced in China since 1930s (<xref ref-type="bibr" rid="B6">Chen et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B37">Oficialdegui et&#xa0;al., 2020</xref>). It is a popular aquatic product in China and is cultured in more than 20 provinces with an area larger than 1.46 million hectares (<xref ref-type="bibr" rid="B64">Yuan et&#xa0;al., 2022</xref>). Red swamp crayfish is also widely distributed in lakes, rivers, ditches, sloughs, and elsewhere (<xref ref-type="bibr" rid="B63">Yi et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B65">Yue et&#xa0;al., 2021</xref>). Crayfish have been found to disrupt the clear water state of lakes through physical disturbances and direct consumption of macrophytes (<xref ref-type="bibr" rid="B49">van der Wal et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B10">Dercksen et&#xa0;al., 2025</xref>). They also negatively impact native species such as amphibians, gastropods, and insect larvae through predation or competition for food (<xref ref-type="bibr" rid="B45">Souty-Grosset et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B24">Huang et&#xa0;al., 2025</xref>). However, most research on the impacts of crayfish has focused on macrophytes and benthic animals (<xref ref-type="bibr" rid="B41">Ruokonen et&#xa0;al., 2016</xref>), while little attention has been paid to other taxa within the freshwater food web.</p>
<p>Crayfish are generally omnivores and their diet varies according to life stage (<xref ref-type="bibr" rid="B8">Correia, 2003</xref>; <xref ref-type="bibr" rid="B16">Geiger et&#xa0;al., 2005</xref>). The diet of adult crayfish (&gt;8&#xa0;cm in total length) consists of macrophytes, insect larvae, gastropods, and detritus (<xref ref-type="bibr" rid="B49">van der Wal et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B60">Wu et&#xa0;al., 2022</xref>), while little is known about the diet of juveniles and sub-adults. Adult female crayfish lay eggs and incubate them on their pleopods until hatching. By the third instar stage, juveniles become free-living (<xref ref-type="bibr" rid="B19">Hamasaki et&#xa0;al., 2023</xref>). Juvenile crayfish (&lt;5&#xa0;cm) are primarily carnivorous, feeding on zooplankton or small benthic animals (<xref ref-type="bibr" rid="B8">Correia, 2003</xref>; <xref ref-type="bibr" rid="B57">Weber and Traunspurger, 2017</xref>). They are capable of capturing planktonic organisms, giving them great potential to influence the littoral food web (<xref ref-type="bibr" rid="B1">Alcorlo et&#xa0;al., 2004</xref>; <xref ref-type="bibr" rid="B16">Geiger et&#xa0;al., 2005</xref>). The total length of sub-adult crayfish is 5~8 cm and they share trophic niches with both juvenile and adult crayfish (<xref ref-type="bibr" rid="B9">Correia and Anast&#xe1;cio, 2008</xref>; <xref ref-type="bibr" rid="B51">Vesel&#xfd; et&#xa0;al., 2020</xref>). In the field, 30%~80% of individuals are juveniles or sub-adults (<xref ref-type="bibr" rid="B11">Dorn et&#xa0;al., 2005</xref>), highlighting the importance of investigating their impacts on the food web to understand their effect on the stability of freshwater ecosystems.</p>
<p>Zooplankton play an important role in freshwater ecosystems and are the main food source for many kinds of fish and macroinvertebrates (<xref ref-type="bibr" rid="B32">Li et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B36">Neale and Rudolf, 2025</xref>). High densities of white leg shrimps <italic>Litopenaeus vannamei</italic> significantly reduce zooplankton abundance and diversity (<xref ref-type="bibr" rid="B47">Tran et&#xa0;al., 2023</xref>). The presence of juvenile and sub-adult crayfish <italic>P. clarkii</italic> has been shown to greatly reduce the abundances of the crustaceans <italic>Daphnia</italic> and <italic>Cyclops</italic> (<xref ref-type="bibr" rid="B9">Correia and Anast&#xe1;cio, 2008</xref>), indicating that crayfish have strong potential to feed on and influence zooplankton community.</p>
<p>Aquatic animals including fish, macroinvertebrates, and zooplankton exhibit diurnal feeding rhythms that vary among species and habitats (<xref ref-type="bibr" rid="B59">Williamson et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B30">Krylov et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B52">Viccon-Pale, 2022</xref>). Light intensity influences the circadian rhythm of crustaceans which is regulated by putative pacemakers such as the brain (<xref ref-type="bibr" rid="B34">L&#xf3;pez-Becerril et&#xa0;al., 2025</xref>). The juvenile shrimp <italic>L. vannamei</italic> exhibit higher feeding rates in light than in darkness (<xref ref-type="bibr" rid="B43">Sanudin et&#xa0;al., 2014</xref>). Crayfish <italic>P. clarkii</italic> often hide in burrows to avoid predators such as fish or waterbirds, which mainly feed during the day (<xref ref-type="bibr" rid="B21">Haubrock et&#xa0;al., 2019</xref>). The feeding activity of crayfish follows rhythmic patterns (<xref ref-type="bibr" rid="B52">Viccon-Pale, 2022</xref>), some studies reported peak feeding time in the morning from 8:00 to 10:00 and at night from 19:00 to 22:00 (<xref ref-type="bibr" rid="B61">Xu et&#xa0;al., 2012</xref>), while others suggested continuous feeding during the day and at night (<xref ref-type="bibr" rid="B67">Zhou and Zhao, 2007</xref>). Most studies on feeding rhythms focus on adult crayfish, while little is known about the behavior of the juveniles.</p>
<p>Invasive crayfish have significant impacts on native crustaceans due to their advantages in growth, reproduction and locomotion (<xref ref-type="bibr" rid="B33">Lodge et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B18">Guareschi et&#xa0;al., 2024</xref>). Native freshwater shrimps in China are generally omnivorous, feeding on zooplankton, dipteran larvae, periphyton and detritus (<xref ref-type="bibr" rid="B46">Tiffan and Hurst, 2016</xref>; <xref ref-type="bibr" rid="B68">Zhu et&#xa0;al., 2022</xref>). Presence of shrimp may reduce periphyton biomass and increase macrophyte biomass in freshwater lakes (<xref ref-type="bibr" rid="B62">Ye et&#xa0;al., 2019</xref>). Shrimps prefer to feed on cladocerans, leading to changes in zooplankton community structure (<xref ref-type="bibr" rid="B35">Mamani et&#xa0;al., 2019</xref>). The shrimp <italic>Exopalaemon modestus</italic> is one of the most abundant and common native shrimp in lakes in the lower reaches of the Yangtze River (<xref ref-type="bibr" rid="B66">Zhao et&#xa0;al., 2023</xref>). <italic>E. modestus</italic> predate on various zooplankton species (<xref ref-type="bibr" rid="B22">He et&#xa0;al., 2021</xref>), with cladocerans and copepods constituting a high percentage in their diets (<xref ref-type="bibr" rid="B68">Zhu et&#xa0;al., 2022</xref>). This shrimp is generally active at night, with feeding activity peaked near 22:00 (<xref ref-type="bibr" rid="B58">Wen and Xie, 2013</xref>). Co-occurrences of <italic>P. clarkii</italic> and <italic>E. modestus</italic> have been reported in natural lakes in China (<xref ref-type="bibr" rid="B60">Wu et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B66">Zhao et&#xa0;al., 2023</xref>). Although field observations indicate a similar trophic niche between the invasive <italic>P. clarkii</italic> and the native <italic>E. modestus</italic> (<xref ref-type="bibr" rid="B60">Wu et&#xa0;al., 2022</xref>), their differential predation rhythms on zooplankton remain unclear.</p>
<p>In this study, we hypothesized that there is a circadian rhythm difference between invasive juvenile crayfish and native shrimp in their predation of zooplankton, which might lead to a higher zooplankton feeding intensity in juvenile crayfish than in shrimp. To test this hypothesis, we compared the predation intensity and efficiency of crayfish and shrimp on cladoceran <italic>Simocephalus mixtus</italic>, one of the most common cladocerans in the littoral regions of freshwater lakes (<xref ref-type="bibr" rid="B25">Huang, 2014</xref>), at different prey densities under both daytime and night-time conditions. Our results provide insights into the mechanisms through which invasive species adversely affect native ones and partly help explain the invasion success of crayfish.</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<label>2</label>
<title>Materials and methods</title>
<sec id="s2_1">
<label>2.1</label>
<title>Pre-culturing of the animals</title>
<p>Juvenile and sub-adult crayfish were obtained from a rice-crayfish field in Qianjiang, China (112&#xb0;59&#x201d;6&#x2019; E, 30&#xb0;11&#x201d;1&#x2019; N) in April 2024. <italic>Simocephalus mixtus</italic>, was collected from a natural pond in Wuhan, China (114&#xb0;18&#x201d;24&#x2019; E, 30&#xb0;29&#x201d;4&#x2019; N). Shrimps were collected from Lake Taihu, China (120&#xb0;13&#x201d;36&#x2019; E, 31&#xb0;24&#x201d;05&#x2019; N). All organisms were obtained in April 2024 and cultured in the lab for a month prior to the experiment. One day before the experiment, individuals were placed in BG11 medium to evacuate their guts.</p>
<p>The experiments were conducted in cylindrical glass beakers (diameter 15&#xa0;cm, height 8&#xa0;cm, volume 1.4 L) with black tape applied under the bottom to mimic natural conditions (<xref ref-type="fig" rid="f1"><bold>Figure&#xa0;1</bold></xref>). Culture medium (500 mL BG11) was added to each beaker as well as shelters (tiles) to mimic crayfish burrows (<xref ref-type="bibr" rid="B21">Haubrock et&#xa0;al., 2019</xref>). The beakers were placed in an incubator (PGx-60013) at 25&#xb0;C, with a light intensity of 1000lx and a light:dark cycle of 12:12 h.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>Schematic overview of the experimental beakers. (1) Juvenile crayfish <italic>procambarus clarkii</italic> (J) + low density of zooplankton (L); (2) J + medium density of zooplankton (M); (3) J + high density of zooplankton (H); (4) J + L + light during the day (D); (5) J + M + D; (6) J + H + D; (7) Sub-adult crayfish (S) + L; (8) S + M; (9) S + H; (10) shrimp <italic>Exopalaemon modestus</italic> (E) + L; (11) E + M; (12) E + H; (13) E + L + D; (14) E + M + D; (15) E + H + D.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-13-1744072-g001.tif">
<alt-text content-type="machine-generated">Fifteen labeled diagrams depict crayfish and shrimps in beakers. Tanks in rows one and three have no sunlight; rows two and four display sunlight. Each row has three densities of prey and different types of predators: low (L), medium (M), and high (H), with predators J, S and E. The setups illustrate different environmental conditions represented by combinations of labels JL, JM, JH, JLD, JMD, JHD, SL, SM, SH, EL, EM, EH, ELD, EMD, and EHD.</alt-text>
</graphic></fig>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Predation experiment</title>
<p>The densities of zooplankton were set at 18 ind./L in the low-density treatment, 54 ind./L in the medium-density treatment, and 108 ind./L in the high-density treatment. The density gradients were set based on field observations of cladocerans (<xref ref-type="bibr" rid="B7">Choi and Kim, 2020</xref>; <xref ref-type="bibr" rid="B5">Chen et&#xa0;al., 2021</xref>). The predation experiments included all three zooplankton densities, with three replicates per treatment. The average body length of <italic>S. mixtus</italic> used in the experiments was 1.57&#xa0;&#xb1;&#xa0;0.29 mm in body length and 0.24&#xa0;&#xb1;&#xa0;0.15 mg in wet weight. The number of living zooplankton in each beaker was counted at the end of the experiment, and potential leftovers under the bottom of beakers were checked. A control experiment containing only zooplankton was included to determine the natural mortality rate of zooplankton.</p>
<p>The experiment was conducted with the five treatments at the three zooplankton densities mentioned above, with one predator per beaker. Each treatment has three replicates, and the set-ups are listed in the table (<xref ref-type="table" rid="T1"><bold>Table&#xa0;1</bold></xref>). The first and second treatments tested the predation of juvenile crayfish on zooplankton during the day and at night, respectively. The third treatment tested the predation of sub-adult crayfish on zooplankton at night. The fourth and fifth treatments tested the predation of juvenile shrimp on zooplankton during the day and at night, respectively.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Experimental set-up for predation experiment.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center">Number</th>
<th valign="middle" align="center">Predator</th>
<th valign="middle" align="center">Length (cm, mean&#xb1;SE)</th>
<th valign="middle" align="center">Wet weight (g, mean&#xb1;SE)</th>
<th valign="middle" align="center">Period</th>
<th valign="middle" align="center">Duration</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="center">1</td>
<td valign="middle" align="center">Juvenile crayfish</td>
<td valign="middle" align="center">3.75&#xb1;0.037</td>
<td valign="middle" align="center">1.10&#xb1;0.041</td>
<td valign="middle" align="center">Daytime</td>
<td valign="middle" align="center">10:00~18:00</td>
</tr>
<tr>
<td valign="middle" align="center">2</td>
<td valign="middle" align="center">Juvenile crayfish</td>
<td valign="middle" align="center">3.74&#xb1;0.033</td>
<td valign="middle" align="center">1.07&#xb1;0.028</td>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">0:00~8:00</td>
</tr>
<tr>
<td valign="middle" align="center">3</td>
<td valign="middle" align="center">Sub-adult crayfish</td>
<td valign="middle" align="center">6.68&#xb1;0.026</td>
<td valign="middle" align="center">8.35&#xb1;0.034</td>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">0:00~8:00</td>
</tr>
<tr>
<td valign="middle" align="center">4</td>
<td valign="middle" align="center">Juvenile shrimp</td>
<td valign="middle" align="center">3.88&#xb1;0.073</td>
<td valign="middle" align="center">0.40&#xb1;0.026</td>
<td valign="middle" align="center">Daytime</td>
<td valign="middle" align="center">10:00~18:00</td>
</tr>
<tr>
<td valign="middle" align="center">5</td>
<td valign="middle" align="center">Juvenile shrimp</td>
<td valign="middle" align="center">3.87&#xb1;0.067</td>
<td valign="middle" align="center">0.40&#xb1;0.030</td>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">0:00~8:00</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Data analysis</title>
<p>Predation rates were estimated based on differences in the biomass of zooplankton between the start and end of the experiment, taking predator biomass into account (<xref ref-type="bibr" rid="B54">Vucic-Pestic et&#xa0;al., 2010</xref>):</p>
<disp-formula>
<mml:math display="block" id="M1"><mml:mrow><mml:mi>r</mml:mi><mml:mo>=</mml:mo><mml:mfrac bevelled="true"><mml:mrow><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:msub><mml:mi>m</mml:mi><mml:mi>t</mml:mi></mml:msub><mml:mo>&#x2212;</mml:mo><mml:msub><mml:mi>m</mml:mi><mml:mn>0</mml:mn></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:mrow><mml:mrow><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>M</mml:mi><mml:mo>&#xb7;</mml:mo><mml:mi>T</mml:mi></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:mrow></mml:mfrac></mml:mrow></mml:math>
</disp-formula>
<p>where <italic>r</italic> is the predation rates (mg/(g&#xb7;h)), <italic>m<sub>0</sub></italic> is the initial biomass of zooplankton (mg), <italic>m<sub>t</sub></italic> is the final biomass of zooplankton (mg); <italic>M</italic> is the biomass of predator (g) and <italic>T</italic> is the duration of experimental period (h). For each treatment, predation rates at different zooplankton densities were analyzed using one-way ANOVA, and the LSD test was used for pairwise comparisons. Differences in predation rates between juvenile crayfish and shrimp during the day or at night were assessed using Student&#x2019;s T-test. All analyses were performed using R (<xref ref-type="bibr" rid="B39">R core Team, 2023</xref>).</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<label>3</label>
<title>Results</title>
<sec id="s3_1">
<label>3.1</label>
<title>Predation rates of juvenile crayfish on zooplankton</title>
<p>Predation rates of juvenile crayfish on cladoceran <italic>S. mixtus</italic> increased with increasing prey density (<xref ref-type="fig" rid="f2"><bold>Figure&#xa0;2</bold></xref>). In the control treatments with only zooplankton, no dead individual was observed during the 8 hour-experimental period. At the initial high zooplankton density of 108 ind./L, the night-time predation rate (1.3 mg/(g&#xb7;h)) was significantly higher than at medium zooplankton density (<italic>p</italic>&#xa0;&lt;&#xa0;0.001).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Daytime <bold>(A)</bold> and night-time <bold>(B)</bold> predation rates of juvenile crayfish <italic>procambarus clarkii</italic> on different densities (18, 54 and 108 ind./L) of zooplankton. Different letters indicate significant differences in the LSD test by ranks.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-13-1744072-g002.tif">
<alt-text content-type="machine-generated">Bar charts compare predation rates at different densities in two panels, A and B. In both panels, predation rate increases with density. Panel A shows bars in shades of yellow and orange, while panel B uses shades of blue. Letters a, b, and c signify statistical significance, with a being the highest rate and c the lowest. Error bars indicate variability.</alt-text>
</graphic></fig>
<p>For juvenile crayfish, the daytime predation rate at the high zooplankton density was significantly higher than at medium zooplankton density (<italic>p</italic>&#xa0;&lt;&#xa0;0.05; <xref ref-type="fig" rid="f2"><bold>Figure&#xa0;2A</bold></xref>). Mean predation rates tended to be lower during the day than at night, though the differences were not significant at any zooplankton density (<xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Table S1</bold></xref>).</p>
<p>For sub-adult crayfish, predation rate was significantly higher at the high zooplankton density than at medium zooplankton density (<italic>p</italic>&#xa0;&lt;&#xa0;0.05; <xref ref-type="fig" rid="f3"><bold>Figure&#xa0;3</bold></xref>). Juvenile crayfish (length&lt; 5&#xa0;cm) showed higher predation rates than sub-adult crayfish (length 5~8 cm) at all densities (<italic>p</italic>&#xa0;&lt;&#xa0;0.05; <xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Table S2</bold></xref>).</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Night-time predation rates of sub-adult crayfish <italic>procambarus clarkii</italic> on different densities of zooplankton (18, 54 and 108 ind./L). Different letters indicate significant differences in the LSD test by ranks.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-13-1744072-g003.tif">
<alt-text content-type="machine-generated">Bar graph showing predation rate in milligrams per gram per hour against density in individuals per liter. Three bars represent densities 18, 45 and 108 ind./L, with predation rates increasing from left to right. Bars marked with letters c, b, and a, indicating statistical differences.</alt-text>
</graphic></fig>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Predation rates of juvenile shrimps on zooplankton</title>
<p>For juvenile shrimps, the predation rate was significantly higher at the high zooplankton density than at medium zooplankton density (<italic>p</italic>&#xa0;&lt;&#xa0;0.05; <xref ref-type="fig" rid="f4"><bold>Figure&#xa0;4</bold></xref>). Night-time predation rates of juvenile shrimps on zooplankton tended to be higher than those of juvenile crayfish at all zooplankton densities, though the differences were not significant (<xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>).</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Predation rates of shrimps <italic>exopalaemon modestus</italic> during the day <bold>(A)</bold> and at night <bold>(B)</bold> on different densities of zooplankton (18, 54 and 108 ind./L). Different letters indicate significant differences in the LSD test by ranks.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-13-1744072-g004.tif">
<alt-text content-type="machine-generated">Bar graphs showing predation rate (milligrams per gram per hour) against density (individuals per liter). Graph A has lower predation rates across densities, with significant differences marked by the same letter. Graph B shows higher rates, with different letters indicating distinct groups at different densities.</alt-text>
</graphic></fig>
<table-wrap id="T2" position="float">
<label>Table&#xa0;2</label>
<caption>
<p>Daytime and night-time predation rates of juvenile crayfish and shrimp.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center">Number</th>
<th valign="middle" align="center">Density (ind./L)</th>
<th valign="middle" align="center">Period</th>
<th valign="middle" align="center">Predator</th>
<th valign="middle" align="center">Mean predation rate (mg/(g&#xb7;h))</th>
<th valign="middle" align="center"><italic>p</italic> value</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" rowspan="4" align="center">1</td>
<td valign="middle" rowspan="4" align="center">18</td>
<td valign="middle" align="center">Daytime</td>
<td valign="middle" align="center">Crayfish</td>
<td valign="middle" align="center">0.135 &#xb1; 0.073</td>
<td valign="middle" rowspan="2" align="center">0.0922</td>
</tr>
<tr>
<td valign="middle" align="center">Daytime</td>
<td valign="middle" align="center">Shrimp</td>
<td valign="middle" align="center">0.017 &#xb1; 0.029</td>
</tr>
<tr>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">Crayfish</td>
<td valign="middle" align="center">0.209 &#xb1; 0.063</td>
<td valign="middle" rowspan="2" align="center">0.8612</td>
</tr>
<tr>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">Shrimp</td>
<td valign="middle" align="center">0.225 &#xb1; 0.130</td>
</tr>
<tr>
<td valign="middle" rowspan="4" align="center">2</td>
<td valign="middle" rowspan="4" align="center">54</td>
<td valign="middle" align="center">Daytime</td>
<td valign="middle" align="center">Crayfish</td>
<td valign="middle" align="center">0.622 &#xb1; 0.102</td>
<td valign="middle" rowspan="2" align="center">0.0034**</td>
</tr>
<tr>
<td valign="middle" align="center">Daytime</td>
<td valign="middle" align="center">Shrimp</td>
<td valign="middle" align="center">0.084 &#xb1; 0.058</td>
</tr>
<tr>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">Crayfish</td>
<td valign="middle" align="center">0.718 &#xb1; 0.016</td>
<td valign="middle" rowspan="2" align="center">0.0516</td>
</tr>
<tr>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">Shrimp</td>
<td valign="middle" align="center">1.175 &#xb1; 0.189</td>
</tr>
<tr>
<td valign="middle" rowspan="4" align="center">3</td>
<td valign="middle" rowspan="4" align="center">108</td>
<td valign="middle" align="center">Daytime</td>
<td valign="middle" align="center">Crayfish</td>
<td valign="middle" align="center">1.093 &#xb1; 0.215</td>
<td valign="middle" rowspan="2" align="center">0.0210*</td>
</tr>
<tr>
<td valign="middle" align="center">Daytime</td>
<td valign="middle" align="center">Shrimp</td>
<td valign="middle" align="center">0.354 &#xb1; 0.263</td>
</tr>
<tr>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">Crayfish</td>
<td valign="middle" align="center">1.264 &#xb1; 0.057</td>
<td valign="middle" rowspan="2" align="center">0.0987</td>
</tr>
<tr>
<td valign="middle" align="center">Night-time</td>
<td valign="middle" align="center">Shrimp</td>
<td valign="middle" align="center">2.000 &#xb1; 0.439</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Significant results of <italic>p</italic> values are indicated as follows: <italic>p</italic> &#x2264; 0.05 and <italic>p</italic> &#x2264; 0.01 are marked with * and **, respectively.</p></fn>
</table-wrap-foot>
</table-wrap>
<p>For juvenile shrimps, the daytime predation rates were similar at all three zooplankton densities, being close to 0 at low and medium densities (<xref ref-type="fig" rid="f4"><bold>Figure&#xa0;4</bold></xref>). Mean predation rates on zooplankton during the day were significantly lower than at night at medium and high zooplankton densities (<italic>p</italic>&#xa0;&lt;&#xa0;0.01; <xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Table S3</bold></xref>), with no significant difference at the low zooplankton density.</p>
<p>Predation rates of juvenile shrimp on zooplankton during the day were significantly lower than for juvenile crayfish at medium and high zooplankton densities (<italic>p</italic>&#xa0;&lt;&#xa0;0.05; <xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>), with no significant difference being found at the low zooplankton density.</p>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<label>4</label>
<title>Discussion</title>
<p>Invasive species generally have higher feeding efficiency, faster growth rate and/or higher fecundity than native species (<xref ref-type="bibr" rid="B53">Vila-gispert et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B50">Van Kleunen et&#xa0;al., 2010</xref>). In our study, juvenile crayfish exhibited higher zooplankton feeding intensity than shrimp. The results confirmed the hypothesis that the invasive crayfish and native shrimp differ in circadian rhythm of predation on cladocerans. Invasive juvenile crayfish fed continuously throughout the day and night, while native shrimp showed low feeding activity during the day.</p>
<p>Predation rates of crayfish increased with increasing zooplankton densities in all experiments. As prey abundance rises, encounter and predation rates normally increase (<xref ref-type="bibr" rid="B48">Turesson and Br&#xf6;nmark, 2007</xref>). Functional responses describe the relationship between predation rate and prey density (<xref ref-type="bibr" rid="B14">Faria et&#xa0;al., 2023</xref>). Juvenile crayfish shows a Type II functional responses when feeding on another cladoceran <italic>Daphnia magana</italic>, maintaining high feeding rates at low prey densities (<xref ref-type="bibr" rid="B44">South et&#xa0;al., 2019</xref>). Prey density also affects the defense of cladocerans against handling of predators, which tends to be stronger at higher prey densities (<xref ref-type="bibr" rid="B27">Jeschke and Tollrian, 2000</xref>). We found that feeding rates of juvenile crayfish on cladocerans increased as prey density increased, however, density gradient of zooplankton was not high enough to fit the Type I, Type II or Type III functional responses. Further studies are needed to explore the functional responses of juvenile crayfish and shrimp to variations in density of <italic>S. mixtus</italic> and other zooplankton species.</p>
<p>We found that the larger sub-adult crayfish predated less on zooplankton than juvenile crayfish at all zooplankton densities. Furthermore, one individual of sub-adult crayfish also predated less on zooplankton than one juvenile crayfish (1.71 versus 4.88 ind./h under high zooplankton density). This aligns with the fact that juvenile crayfish tend to be carnivores, while sub-adult and adult crayfish shift toward higher degree of herbivory (<xref ref-type="bibr" rid="B8">Correia, 2003</xref>). Moreover, juvenile crayfish are capable swimmers (<xref ref-type="bibr" rid="B16">Geiger et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B29">Kato et&#xa0;al., 2018</xref>), whereas the swimming ability of sub-adult crayfish is limited, resulting in low possibility of catching cladocerans (<xref ref-type="bibr" rid="B3">Barbaresi et&#xa0;al., 2004</xref>). Predation of juvenile and sub-adult crayfish on cladocerans will influence zooplankton community structure, with potential cascading effects on phytoplankton abundance and water clarity (<xref ref-type="bibr" rid="B26">Jeppesen et&#xa0;al., 2004</xref>). Crayfish influence the zooplankton community not only through predation but also by increasing water turbidity (<xref ref-type="bibr" rid="B9">Correia and Anast&#xe1;cio, 2008</xref>), and their influence on zooplankton is more complicated under natural conditions. Differences in eyesight between juvenile and sub-adult crayfish also contribute to variations in their catching ability (<xref ref-type="bibr" rid="B13">Fanjul-Moles and Prieto-Sagredo, 2003</xref>). As sensitivity to light varies between juvenile and adult crayfish (<xref ref-type="bibr" rid="B38">Ou and Liang, 2017</xref>), further studies are needed to explore how light influences their predation rhythms.</p>
<p>Juvenile crayfish showed similar feeding rate but a longer feeding period on <italic>S. mixtus</italic> compared to shrimps of similar length, indicating higher feeding capacity of this invasive species. In our study, the feeding rate of juvenile crayfish tended to be slightly lower during the day than at night. Shrimp <italic>E. modestu</italic>s mainly fed at night, which aligns with findings of other studies of diurnal variation in the feeding activity of another shrimp of the same genus (<italic>E. carinicauda</italic>) (<xref ref-type="bibr" rid="B55">Wang et&#xa0;al., 2023</xref>). For shrimp <italic>L. vannamei</italic>, the circadian rhythm of nocturnal feeding is driven by an endogenous clock and persist under different conditions (<xref ref-type="bibr" rid="B42">Santos et&#xa0;al., 2016</xref>). Juvenile crayfish fed continuously during the day and at night, showing no apparent circadian rhythm, which might be linked to the fact that crayfish rely on both eyesight and smell for foraging (<xref ref-type="bibr" rid="B67">Zhou and Zhao, 2007</xref>). The night-time feeding rates of juvenile crayfish were close to that of shrimp, indicating that juvenile crayfish has high catching ability on cladocerans (<xref ref-type="bibr" rid="B44">South et&#xa0;al., 2019</xref>). Cladocerans can identify predators with different feeding habitats and behaviors (<xref ref-type="bibr" rid="B12">Ekvall et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B31">Lee and Hansson, 2024</xref>). Juvenile crayfish are ambush predators, while shrimp swim at relatively constant speeds at night (<xref ref-type="bibr" rid="B23">Hu et&#xa0;al., 2001</xref>; <xref ref-type="bibr" rid="B40">Renai and Gherardi, 2004</xref>), which may also explain the observed differences in their predation rhythms on <italic>S. mixtus</italic>. Size of the predator influence the enzyme digestive activities, which indirectly influence the predation rates and frequency (<xref ref-type="bibr" rid="B17">Gilannejad et&#xa0;al., 2021</xref>). Juvenile shrimp at weight 0.4&#xa0;g showed relatively lower enzyme digestive activities than shrimp at weight 0.1-0.3&#xa0;g (<xref ref-type="bibr" rid="B56">Wang et&#xa0;al., 2010</xref>). For juvenile crayfish, enzyme digestive activities increase steadily through 42 days of development and remain high at weight 0.6&#xa0;g (<xref ref-type="bibr" rid="B20">Hammer et&#xa0;al., 2000</xref>). Our study on early stages of invasive crayfish and native shrimp supports the inherent superiority hypothesis that invasive species possess advantages over native species in feeding behaviors and capacity (<xref ref-type="bibr" rid="B28">Ju et&#xa0;al., 2013</xref>). Presence of crayfish has also been found to cause shift in the trophic niche of shrimp (<xref ref-type="bibr" rid="B4">Baudry et&#xa0;al., 2024</xref>). Moreover, adult and sub-adult crayfish have the potential to prey on shrimps (<xref ref-type="bibr" rid="B2">Banha and Anast&#xe1;cio, 2011</xref>), adding to their invasion success.</p>
<p>To conclude, juvenile crayfish and shrimp were found to consume cladocerans efficiently. Juvenile crayfish fed more at night than during the day and at a faster rate than sub-adult crayfish. Juvenile crayfish also fed for longer periods than shrimp, showing higher feeding capacity for invasive species than their native counterparts (<xref ref-type="bibr" rid="B15">Faria et&#xa0;al., 2025</xref>). Future studies are needed to investigate the differences between invasive crayfish and native shrimps in natural lakes, and to explore the overall impacts of decapods on the zooplankton community and the entire freshwater ecosystem.</p>
</sec>
</body>
<back>
<sec id="s5" sec-type="data-availability">
<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" sec-type="author-contributions">
<title>Author contributions</title>
<p>HZ: Conceptualization, Data curation, Formal Analysis, Funding acquisition, Methodology, Resources, Software, Supervision, Visualization, Writing &#x2013; original draft, Writing &#x2013; review &amp; editing. YL: Writing &#x2013; original draft, Formal Analysis, Investigation, Methodology, Resources. JG: Conceptualization, Funding acquisition, Project administration, Resources, Supervision, Validation, Writing &#x2013; review &amp; editing. ML: Investigation, Methodology, Resources, Writing &#x2013; review &amp; editing. HW: Investigation, Methodology, Resources, Writing &#x2013; review &amp; editing. YcJ: Investigation, Resources, Writing &#x2013; review &amp; editing. YyJ: Visualization, Writing &#x2013; review &amp; editing. LW: Investigation, Resources, Writing &#x2013; review &amp; editing. XZ: Investigation, Resources, Writing &#x2013; review &amp; editing. EJ: Supervision, Visualization, Writing &#x2013; review &amp; editing. FC: Supervision, Visualization, Writing &#x2013; review &amp; editing.</p></sec>
<ack>
<title>Acknowledgments</title>
<p>We are very grateful to Anne Mette Poulsen (Department of Ecoscience, Aarhus University, Aarhus) for linguistic assistance. We also thank Xiaofang Tian and Wei Liu for assistances in conducting the experiments.</p>
</ack>
<sec id="s8" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>The author(s) declared that this work 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="s9" sec-type="ai-statement">
<title>Generative AI statement</title>
<p>The author(s) declared that Generative AI was not used in the creation of this manuscript.</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p></sec>
<sec id="s10" 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>
<sec id="s11" sec-type="supplementary-material">
<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/fevo.2025.1744072/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fevo.2025.1744072/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Table1.docx" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document"/></sec>
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