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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Mar. Sci.</journal-id>
<journal-title>Frontiers in Marine Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Mar. Sci.</abbrev-journal-title>
<issn pub-type="epub">2296-7745</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fmars.2022.970781</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Marine Science</subject>
<subj-group>
<subject>Brief Research Report</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Molecular and biochemical effects on metabolism and immunity of <italic>Hyriopsis cumingii</italic> fed with four different microalgae</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Sun</surname>
<given-names>Yu</given-names>
</name>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Guo</surname>
<given-names>Kefan</given-names>
</name>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Yu</surname>
<given-names>Xiaobo</given-names>
</name>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Li</surname>
<given-names>Yanhong</given-names>
</name>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Yao</surname>
<given-names>Weizhi</given-names>
</name>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Wu</surname>
<given-names>Zhengli</given-names>
</name>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1868894"/>
</contrib>
</contrib-group>
<aff id="aff1">
<institution>College of Fisheries, Key Laboratory of Freshwater Fish Reproduction and Development, Ministry of Education, and Research Center of Fishery Resources and Environment, Southwest University</institution>, <addr-line>Chongqing</addr-line>, <country>China</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Dr. Shivendra Kumar, Dr. Rajendra Prasad Central Agricultural University, India</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Srijit Chakravarty, Central Institute of Fisheries Education (ICAR), India; Sarvendra Kumar, College of Fisheries Kishanganj, India</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Zhengli Wu, <email xlink:href="mailto:zh20140202@swu.edu.cn">zh20140202@swu.edu.cn</email>
</p>
</fn>
<fn fn-type="other" id="fn002">
<p>This article was submitted to Aquatic Physiology, a section of the journal Frontiers in Marine Science</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>04</day>
<month>08</month>
<year>2022</year>
</pub-date>
<pub-date pub-type="collection">
<year>2022</year>
</pub-date>
<volume>9</volume>
<elocation-id>970781</elocation-id>
<history>
<date date-type="received">
<day>16</day>
<month>06</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>11</day>
<month>07</month>
<year>2022</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2022 Sun, Guo, Yu, Li, Yao and Wu</copyright-statement>
<copyright-year>2022</copyright-year>
<copyright-holder>Sun, Guo, Yu, Li, Yao and Wu</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>
<italic>Hyriopsis cumingii</italic> has attracted attention because of its pearl production performance and water purification capacity. Realizing sustainable industrialized culture of <italic>H. cumingii</italic> or applying it to bivalve biomanipulation for controlling water eutrophication needs urgent studies about the selection of suitable algae and the effects of different microalgae on mussel physiology. To contrast molecular and biochemical effects of high-quality microalgal diets (<italic>Chlorella vulgaris</italic>, <italic>Navicula pelliculosa</italic>, and <italic>Cyclotella</italic> sp.) with toxic <italic>Microcystis aeruginosa</italic> on metabolism and immune physiology of <italic>H. cumingii</italic>, levels of related enzymes and genes were analyzed during the 28-day exposure period. Results showed that the <italic>Cyclotella</italic> sp. diet could significantly (<italic>p</italic> &lt; 0.05) maintain higher levels of metabolic enzymes (glutamic oxaloacetate transaminase (GOT), glutamic pyruvate transaminase (GPT), pyruvate kinase (PK), and hexokinase (HK)) and genes (CPT1 and LDLR). <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic> treatments significantly (<italic>p</italic> &lt; 0.05) reduced activities of these metabolic parameters. The <italic>M. aeruginosa</italic> treatment significantly (<italic>p</italic> &lt; 0.05) enhanced levels of immune enzymes (alkaline phosphatase (AKP), superoxide dismutase (SOD), and catalase (CAT)) and genes (HcIL-17 and IAP) on day 1 or 7, and there was a significant (<italic>p</italic> &lt; 0.05) reduction on day 28. Results suggested that <italic>Cyclotella</italic> sp. was the suitable algae for <italic>H. cumingii</italic>, followed by <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic>, and toxic algae caused metabolic disorders, immune injury, and poor physiological status. The study has practical significance in the sustainable cultivation of <italic>H. cumingii</italic> and provides a theoretical basis for bivalve biomanipulation in eutrophic water.</p>
</abstract>
<kwd-group>
<kwd>
<italic>hyriopsis cumingii</italic>
</kwd>
<kwd>microalgae</kwd>
<kwd>metabolism</kwd>
<kwd>non-specific immunity</kwd>
<kwd>gene expression</kwd>
</kwd-group>
<counts>
<fig-count count="4"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="29"/>
<page-count count="9"/>
<word-count count="4731"/>
</counts>
</article-meta>
</front>
<body>
<sec id="s1">
<title>Introduction</title>
<p>Global freshwater pearl production accounting for more than 75% is achieved by the triangle sail mussel <italic>Hyriopsis cumingii</italic> from China (<xref ref-type="bibr" rid="B22">Tang et&#xa0;al., 2015</xref>). On the one hand, water pollution, disease outbreaks, and benthic ecological destruction often occur in the traditional cultivation of <italic>H. cumingii</italic> because of the use of massive amounts of organic and chemical fertilizers (<xref ref-type="bibr" rid="B11">Hu et&#xa0;al., 2015</xref>). The development and exploitation of a new sustainable cultivation mode such as industrialized culture are urgent, and the selection of microalgae with high quality and nutritional value is the key. On the other hand, freshwater bivalves have been considered a biomanipulation tool to control water eutrophication based on ecological functions such as biofiltration, biodeposition, and bioturbation (<xref ref-type="bibr" rid="B6">Gulati et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B7">Gu et&#xa0;al., 2020</xref>). In small-scale bivalve biomanipulation experiments, <italic>H. cumingii</italic> can effectively reduce concentrations of total suspended solids and the number of cyanobacteria, increase transparency, and change the community structure of phytoplankton in water (<xref ref-type="bibr" rid="B9">He et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B24">Wang et&#xa0;al., 2018</xref>). Toxic algae <italic>Microcystis aeruginosa</italic> is the most common species from cyanobacterial blooms, which causes adverse effects on the physiological responses of <italic>H. cumingii</italic> (<xref ref-type="bibr" rid="B12">Hu et&#xa0;al., 2016</xref>). Therefore, urgent studies about contrasting molecular and biochemical effects of high-quality microalgal diets with the toxic <italic>M. aeruginosa</italic> on the metabolism and immune physiology of <italic>H. cumingii</italic> are needed.</p>
<p>As the main food for bivalves, algae is the natural nutritional base and primary source of nutrients. Diatoms such as <italic>Navicula</italic> sp., <italic>Cyclotella</italic> sp., and green algae <italic>Chlorella vulgaris</italic>, which are rich in nutrients including carbohydrate, lipid, and protein, have been applied to bivalve culture. Previous studies have shown that different algae affect the growth, pearl production, fatty acid composition, and energy metabolism of <italic>H. cumingii</italic> (<xref ref-type="bibr" rid="B3">Chen et&#xa0;al., 2021</xref>). Mussels have sensitive physiological responses such as changes in enzyme and gene levels to different algal species or concentrations (<xref ref-type="bibr" rid="B2">Blanco-Rayon et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B21">Sun et&#xa0;al., 2021</xref>). Metabolic enzymes including glutamic oxaloacetate transaminase (GOT), glutamic pyruvate transaminase (GPT), pyruvate kinase (PK), and hexokinase (HK) have a key role in protein, carbohydrate, and glucose metabolism (<xref ref-type="bibr" rid="B27">Xia et&#xa0;al., 2015</xref>). Low-density lipoprotein receptor (LDLR) and carnitine palmitoyltransferase 1 (CPT1) have a crucial function in lipid uptake, transport, and catabolic metabolism (<xref ref-type="bibr" rid="B15">Liu et&#xa0;al., 2018</xref>). Hydrolases alkaline phosphatase (AKP) and antioxidase superoxide dismutase (SOD), and catalase (CAT), as non-specific humoral immune factors, participate in immune responses (<xref ref-type="bibr" rid="B11">Hu et&#xa0;al., 2015</xref>). Interleukin-17 (HcIL-17) and inhibitor of apoptosis protein (IAP) have crucial functions in the inflammatory reaction, immune responses, and defense of bivalves (<xref ref-type="bibr" rid="B19">Rosani et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B29">Zhu et&#xa0;al., 2021</xref>). Bivalve gill is the tissue that first comes into contact with foreign particles, and changes in the hemolymph can reflect the process of oxidative damage and the metabolism of pollutants (<xref ref-type="bibr" rid="B17">Pan et&#xa0;al., 2006</xref>). Functional features of the bivalve liver include the metabolic reserve site and the helper of transferring these reserves to other organs (<xref ref-type="bibr" rid="B1">Albentosa et&#xa0;al., 2012</xref>).</p>
<p>Therefore, detecting the above molecular and biochemical parameters could reflect the health and physiology status of mussels when exposed to three microalgal diets and the toxic <italic>M. aeruginosa</italic>. This study provides new considerations for technical issues such as the sustainable cultivation of bivalves and the implementation of bivalve biomanipulation in eutrophic water.</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<title>Materials and methods</title>
<sec id="s2_1">
<title>Experimental mussels and microalgal cultivation</title>
<p>One-year-old and unisex triangle sail mussels <italic>H. cumingii</italic> (8.26 &#xb1; 0.46&#xa0;cm in shell length and 48.54 &#xb1; 4.02&#xa0;g in wet weight with shell) were obtained from the laboratory culture base (Dahonghu lake, Changshou, Chongqing, China). Healthy mussels after removing shell surface attachments were placed in 20-L aquarium tanks (18 mussels in each tank, 12 tanks in total) with aeration indoors. Mussels were subjected to starvation treatment for 2 days at 23.0&#xb0;C &#xb1; 0.2&#xb0;C, pH 7.8 &#xb1; 0.3, and DO 8.0 &#xb1; 0.2 mg L<sup>&#x2212;1</sup>. Full water was changed daily.</p>
<p>Microalgae was bought from the Freshwater Algae Culture Collection of the Institute of Hydrobiology, Chinese Academy of Sciences, Wuhan, China. <italic>C. vulgaris</italic> (clone FACHB-8) and <italic>M. aeruginosa</italic> (clone FACHB-315) used BG11 medium; <italic>Navicula pelliculosa</italic> (clone FACHB-2262) and <italic>Cyclotella</italic> sp. (clone FACHB-1638) used CSI medium. Microalgae was cultured in 0.45-&#x3bc;m, filtered, natural freshwater, at 25&#xb0;C with a 12-h light:12-h dark cycle. Algal cells had been harvested during the late exponential growth phase, and algal cell densities were counted using a hemocytometer under a light microscope.</p>
</sec>
<sec id="s2_2">
<title>Experimental design</title>
<p>To select the optimal microalgal diet and contrast the physiological effects of different microalgae on the metabolism and immunity of <italic>H. cumingii</italic>, a single-factor experiment had been performed involving four microalgal treatments, with three replicates (i.e., three tanks) per treatment (the culture conditions were the same as above performed during the acclimatization period). Green algae <italic>C. vulgaris</italic> commonly used in production, diatoms <italic>N. pelliculosa</italic> and <italic>Cyclotella</italic> sp. with high nutritional value, and toxic cyanobacteria <italic>M. aeruginosa</italic> forming algal blooms had been adopted in this study. According to previous research data from our laboratory (in the treatment of biomass at 12.5 mg L<sup>&#x2212;1</sup>, mussels of this size produced more real feces and a small amount of pseudo-feces after 1 day) (<xref ref-type="bibr" rid="B21">Sun et&#xa0;al., 2021</xref>), each treatment was reared with the suitable microalgae concentration (<italic>C. vulgaris</italic>, 6.2 &#xd7; 10<sup>5</sup> cells ml<sup>&#x2212;1</sup>; <italic>N. pelliculosa</italic>, 4.0 &#xd7; 10<sup>4</sup> cells ml<sup>&#x2212;1</sup>; <italic>Cyclotella</italic> sp., 3.1 &#xd7; 10<sup>4</sup> cells ml<sup>&#x2212;1</sup>; <italic>M. aeruginosa</italic>, 4.5 &#xd7; 10<sup>6</sup> cells ml<sup>&#x2212;1</sup>; ca. 12.5 mg L<sup>&#x2212;1</sup>). Full water renewal and microalgae additions were conducted once a day at 9:00 a.m. Three mussels from each tank were collected for molecular and biochemical measurements on days 1, 7, 14, 21, and 28. Growth data were measured at the 28th day including shell length and wet weight of mussels (<xref ref-type="supplementary-material" rid="SM1">
<bold>Table S2</bold>
</xref> in the <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Material</bold>
</xref>).</p>
</sec>
<sec id="s2_3">
<title>Sample collection</title>
<p>Gill and liver tissues of mussels had been collected on ice, after the collection of hemolymph from the adductor muscle sinus. Samples were immediately frozen in liquid nitrogen, transported, and stored at &#x2212;80&#xb0;C for further enzyme activities and gene expression analysis. Tissues were later defrosted on ice and homogenized at a ratio of 1:10 (w/v) of saline solution in an ice bath, using a hand-held glass homogenizer. The homogenized sample was centrifuged at 8,000 &#xd7; <italic>g</italic> for 10&#xa0;min at 4&#xb0;C. The supernatant was used for the determination of parameters.</p>
</sec>
<sec id="s2_4">
<title>Determination of molecular and biochemical parameters</title>
<p>Metabolic and immune enzyme activities were respectively evaluated by commercial test kits (Nanjing Jiancheng Bioengineering Institute, Jiangsu, China) (<xref ref-type="bibr" rid="B28">Yang et&#xa0;al., 2021</xref>) following the manufacturer&#x2019;s protocols.</p>
<p>Quantitative PCR was used to analyze relative expression levels of metabolic genes such as CPT1 and LDLR, and immune genes HcIL-17 and IAP in the liver of mussels. The qPCR was performed in a CFX96 Real-Time PCR Detection System (Bio-Rad, Hercules, CA, USA) using Hieff UNICON<sup>&#xae;</sup> Universal Blue qPCR SYBR Green Master Mix (Yeasen, Shanghai, China) to detect double-stranded cDNA synthesis. Reactions were performed in a volume of 20 &#x3bc;l containing 10 &#x3bc;l of qPCR SYBR Green Master Mix, 0.4 &#x3bc;l of 10 mM of each forward and reverse primer (<xref ref-type="supplementary-material" rid="SM1">
<bold>Table S1</bold>
</xref> in the <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Material</bold>
</xref>), and 2 &#x3bc;l of cDNA and 7.2 &#x3bc;l of RNAse-free water. Each qRT-PCR assay was performed in triplicate for analysis, and dissociation curves for each amplicon were carefully examined to confirm the specificity of the primer pairs used. The mean PCR efficiency per pair of primers, the threshold cycle (Ct) value per sample, and the fluorescence threshold set to determine the Ct value were performed using the LinRegPCR software (<xref ref-type="bibr" rid="B20">Ruijter et&#xa0;al., 2009</xref>). Relative expression levels for each sample were obtained using the comparative Ct method. The Ct value obtained after each reaction was normalized to the Ct value of EF1a, whose expression was consistent across all conditions. Relative expression levels were obtained by calibrating &#x394;&#x394;Ct values.</p>
</sec>
<sec id="s2_5">
<title>Statistical analysis</title>
<p>Statistical analysis was performed using SPSS 26 software (SPSS Inc., Chicago, IL, USA). Values of tested parameters were means of three replicates expressed as mean &#xb1; SD. One-way ANOVA was used to evaluate the effects of four algae on mussels, followed by a Student&#x2019;s t-test to determine significant variation among different groups. The significance was set at <italic>p</italic> &lt; 0.05. Principal component analysis (PCA) was visualized using XLSTAT<sup>&#xae;</sup>2020 (Addinsoft Inc., New York, NY, USA).</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<title>Results</title>
<sec id="s3_1">
<title>Effects of four microalgae on metabolic-related enzymes and genes in <italic>Hyriopsis cumingii</italic>
</title>
<p>Higher GOT activities were observed from the <italic>Cyclotella</italic> sp. treatment (7.50 &#xb1; 0.23 U g protein<sup>&#x2212;1</sup>) on days 7, 14, 21, and 28 (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1A</bold>
</xref>). On day 28, the GOT activity of the <italic>M. aeruginosa</italic> treatment (3.56 &#xb1; 0.28 U g protein<sup>&#x2212;1</sup>) was the lowest. GOT activities of <italic>C. vulgaris</italic> and <italic>M. aeruginosa</italic> treatments gradually reduced along with time during the experimental period. GPT activities (6.41 &#xb1; 0.17 U g protein<sup>&#x2212;1</sup>) of the <italic>Cyclotella</italic> sp. treatment were significantly (<italic>p</italic> &lt; 0.05) higher than other treatments on days 14, 21, and 28 (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref>). The lowest GPT activity was observed from the <italic>M. aeruginosa</italic> treatment on day 28 (3.09 &#xb1; 0.05 U g protein<sup>&#x2212;1</sup>). There was a significant reduction in GPT activities of <italic>C. vulgaris</italic>, <italic>N. pelliculosa</italic>, and <italic>M. aeruginosa</italic> treatments over time.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>Activities of metabolic enzymes in liver of <italic>Hyriopsis cumingii</italic>. Mussels exposed to four different microalgae treatments on days 1, 7, 14, 21, and 28. <bold>(A)</bold> GOT, <bold>(B)</bold> GPT, <bold>(C)</bold> PK, and <bold>(D)</bold> HK. The asterisk (*) indicates significant differences between four microalgae treatments at each sampling time (Tukey test, <italic>p</italic> &lt; 0.05). Values are expressed as mean &#xb1; SD (n = 3). GOT, glutamic oxaloacetate transaminase; GPT, glutamic pyruvate transaminase; PK, pyruvate kinase; HK, hexokinase. The symbols *, ** , *** and **** represent p &lt; 0.05, p &lt; 0.01, p &lt; 0.001 and p &lt; 0.0001 respectively.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-09-970781-g001.tif"/>
</fig>
<p>Higher PK activities were observed from the <italic>Cyclotella</italic> sp. treatment (13.37 &#xb1; 0.24 U mg protein<sup>&#x2212;1</sup>) during the experimental period (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1C</bold>
</xref>). The PK activity of mussels in the <italic>M. aeruginosa</italic> treatment (8.92 &#xb1; 0.69 U mg protein<sup>&#x2212;1</sup>) significantly (<italic>p</italic> &lt; 0.05) decreased after day 1. HK activities of mussels in the <italic>Cyclotella</italic> sp. treatment (13.37 &#xb1; 0.24 U mg protein<sup>&#x2212;1</sup>) were significantly (<italic>p</italic> &lt; 0.05) higher than in other treatments on days 21 and 28 (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1D</bold>
</xref>). The lowest HK activity was observed from the <italic>M. aeruginosa</italic> treatment on day 28 (4.35 &#xb1; 0.05 U mg protein<sup>&#x2212;1</sup>).</p>
<p>As shown in <xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>, transcript levels of metabolism-related genes such as CPT1 and LDLR in the liver of mussels were significantly (<italic>p</italic> &lt; 0.05) affected by four algae treatments on days 1, 14, and 28. Consistent with the results of metabolic enzyme activities, there were no significant (<italic>p</italic> &lt; 0.05) differences in relative expression levels of CPT1 and LDLR among all treatments on day 1 (<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2A, B</bold>
</xref>). Relative expression levels on days 14 and 28 could be arranged in the following order: <italic>Cyclotella</italic> sp. treatment &gt; <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic> treatments &gt; <italic>M. aeruginosa</italic> treatment. In the <italic>M. aeruginosa</italic> treatment, CPT1 expression levels reduced along with time. Relative expression levels of LDLR in <italic>C. vulgaris</italic>, <italic>N. pelliculosa</italic>, and <italic>M. aeruginosa</italic> treatments on day 28 significantly (<italic>p</italic> &lt; 0.05) decreased as compared with expression levels on day 1.</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Relative expression levels of metabolic and immune-related genes in liver of <italic>Hyriopsis cumingii</italic>. Mussels exposed to four different microalgae treatments on days 1, 14, and 28. Metabolic genes: <bold>(A)</bold> CPT1 and <bold>(B)</bold> LDLR. Immune genes: <bold>(C)</bold> HcIL-17 and <bold>(D)</bold> IAP. The asterisk (*) indicates significant differences between four microalgae treatments at each sampling time (Tukey test, <italic>p</italic> &lt; 0.05). Values are expressed as mean &#xb1; SD (n = 3).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-09-970781-g002.tif"/>
</fig>
</sec>
<sec id="s3_2">
<title>Effects of four microalgae on immune-related enzymes and genes in <italic>Hyriopsis cumingii</italic>
</title>
<p>AKP activities in the serum of the <italic>C. vulgaris</italic> treatment on days 7, 14, and 28 were significantly (<italic>p</italic> &lt; 0.05) lower than those of the <italic>Cyclotella</italic> sp. treatment (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3A</bold>
</xref>). AKP activities in the serum of the <italic>N. pelliculosa</italic> treatment decreased on day 7 and then recovered. The AKP activity in the serum of the <italic>M. aeruginosa</italic> treatment on day 7 (2.46 &#xb1; 0.11 U ml<sup>&#x2212;1</sup>) was significantly (<italic>p</italic> &lt; 0.05) higher than in the other three treatments. On day 28, the AKP activity in the serum of the <italic>Cyclotella</italic> sp. treatment (2.05 &#xb1; 0.09 U ml<sup>&#x2212;1</sup>) was higher than that of <italic>C. vulgaris</italic> (1.64 &#xb1; 0.19 U ml<sup>&#x2212;1</sup>) and <italic>M. aeruginosa</italic> (1.60 &#xb1; 0.03 U ml<sup>&#x2212;1</sup>) treatments. AKP activities in the gill of <italic>C. vulgaris</italic>, <italic>N. pelliculosa</italic>, and <italic>Cyclotella</italic> sp. treatments were significantly (<italic>p</italic> &lt; 0.05) higher than the <italic>M. aeruginosa</italic> treatment on days 14, 21, and 28 (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3B</bold>
</xref>).</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Activities of immune enzymes in serum and gill of <italic>Hyriopsis cumingii</italic>. Mussels exposed to four different microalgae treatments on days 1, 7, 14, 21, and 28. Immune enzyme activities in serum: <bold>(A)</bold> AKP, <bold>(C)</bold> SOD, and <bold>(E)</bold> CAT. Immune enzyme activities in gill: <bold>(B)</bold> AKP, <bold>(D)</bold> SOD, and <bold>(F)</bold> CAT. The asterisk (*) indicates significant differences between four microalgae treatments at each sampling time (Tukey test, <italic>p</italic> &lt; 0.05). Values are expressed as mean &#xb1; SD (n = 3). AKP, alkaline phosphatase; SOD, superoxide dismutase; CAT, catalase. The symbols *, ** , *** and **** represent p &lt; 0.05, p &lt; 0.01, p &lt; 0.001 and p &lt; 0.0001 respectively.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-09-970781-g003.tif"/>
</fig>
<p>The SOD activity in the serum of the <italic>M. aeruginosa</italic> treatment on day 7 (2.58 &#xb1; 0.07 U ml<sup>&#x2212;1</sup>) was significantly (<italic>p</italic> &lt; 0.05) higher than in the other three treatments (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3C</bold>
</xref>). SOD activities in the serum of the <italic>C. vulgaris</italic> treatment on days 7 and 21 and the <italic>M. aeruginosa</italic> treatment on days 14, 21, and 28 were lower than those of the <italic>Cyclotella</italic> sp. treatment. The SOD activity in the gill of the <italic>M. aeruginosa</italic> treatment on day 1 (20.84 &#xb1; 1.18 U mg protein<sup>&#x2212;1</sup>) was significantly (<italic>p</italic> &lt; 0.05) higher than that of <italic>C. vulgaris</italic> (17.66 &#xb1; 0.46 U mg protein<sup>&#x2212;1</sup>) and <italic>Cyclotella</italic> sp. (18.84 &#xb1; 0.28 U mg protein<sup>&#x2212;1</sup>) treatments. SOD activities in the gill of <italic>C. vulgaris</italic>, <italic>N. pelliculosa</italic>, and <italic>Cyclotella</italic> sp. treatments were significantly (<italic>p</italic> &lt; 0.05) higher than those of the <italic>M. aeruginosa</italic> treatment on days 14, 21, and 28 (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3D</bold>
</xref>).</p>
<p>CAT activities in the serum of the <italic>M. aeruginosa</italic> treatment on days 1 and 7 were significantly (<italic>p</italic> &lt; 0.05) higher than those of the other three treatments (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3E</bold>
</xref>). On day 28, there was a significant reduction in CAT activities in the serum of the <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic> treatments, and the CAT activity in the serum of the <italic>Cyclotella</italic> sp. treatment (2.24 &#xb1; 0.24 U ml<sup>&#x2212;1</sup>) was higher than that of the other three treatments. CAT activities in the gill of the <italic>M. aeruginosa</italic> treatment on days 1 and 7, the <italic>N. pelliculosa</italic> treatment on day 7, and the <italic>C. vulgaris</italic> treatment on day 14 were higher than those of the other treatments at the same sampling time (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3F</bold>
</xref>). The CAT activity in the gill of the <italic>M. aeruginosa</italic> treatment on day 28 (0.92 &#xb1; 0.26 U mg protein<sup>&#x2212;1</sup>) was significantly (<italic>p</italic> &lt; 0.05) lower than that of the other three treatments.</p>
<p>Transcript levels of immune-related genes such as HcIL-17 and IAP in the liver of mussels were significantly (<italic>p</italic> &lt; 0.05) affected by four algae treatments during the experimental period (<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2C, D</bold>
</xref>). Relative expression levels of HcIL-17 and IAP in the <italic>M. aeruginosa</italic> treatment increased on day 1 but gradually decreased on days 14 and 28 (significantly lower than other treatments). Time had no effects on HcIL-17 and IAP expression levels in <italic>C. vulgaris</italic>, <italic>N. pelliculosa</italic>, and <italic>Cyclotella</italic> sp. treatments during the experimental period.</p>
</sec>
</sec>
<sec id="s4">
<title>Discussion</title>
<p>The cultivation mode of <italic>H. cumingii</italic> urgently needs transformation and upgrading, and industrialized culture has become a new direction for the sustainable development of freshwater shellfish in the future because of its characteristics of environmental protection, high yield, and easy operation. The key to success in industrialized culture is the exploration of preferred microalgal diets of <italic>H. cumingii</italic>. In our study, enzyme and gene expression levels of digestion (showed in <xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S1</bold>
</xref> in the <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Material</bold>
</xref>), metabolism and immunity in <italic>H. cumingii</italic> maintained higher levels in the <italic>Cyclotella</italic> sp. treatment on day 28, indicating that <italic>Cyclotella</italic> sp. was suitable algae for <italic>H. cumingii</italic>, and mussels in this treatment had better metabolic abilities, immune function, and physiological status. In <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic> treatments, enzyme and gene expression levels of metabolism were lower than those in the <italic>Cyclotella</italic> sp. treatment. This is because the effects of algal species on bivalves are critically related to their abilities to supply essential nutrients to bivalves, in addition to physical properties of algae such as size and shape. The nutritional value of algae is mainly reflected in differences in biochemical components, and compared with proteins and carbohydrates, the lipid composition is more likely to lead to differences (<xref ref-type="bibr" rid="B5">Geng et&#xa0;al., 2016</xref>). Because of the low ability to synthesize and biotransform essential fatty acids, bivalves must obtain these nutrients from diets. Similar to our findings, a study proves that <italic>Cyclotella</italic> sp. is the optimum microalgal diet for <italic>H. cumingii</italic> from the perspective of the greatest increases in growth and pearl weight, saturated fatty acids, and monounsaturated fatty acids of mussels.</p>
<p>In addition to physical and chemical methods, different nature-based biomanipulation methods are used in a large number of practical cases to control algal blooms (<xref ref-type="bibr" rid="B23">Triest et&#xa0;al., 2016</xref>). With the emergence of shortcomings in fish manipulation (an inadequate reduction in the standing stock of planktivorous fish and the inability of piscivorous fish to control small fish) (<xref ref-type="bibr" rid="B6">Gulati et&#xa0;al., 2008</xref>), utilizing interactions of bivalves and algae makes bivalves a potential biomanipulation tool to effectively control eutrophication of water bodies. In small-scale bivalve biomanipulation experiments for mostly less than 30 days, freshwater bivalves can effectively reduce concentrations of total suspended solids, chlorophyll content, and concentrations of total phosphorus and increase transparency and concentrations of soluble reactive phosphorus in water (<xref ref-type="bibr" rid="B26">Wu et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B7">Gu et&#xa0;al., 2020</xref>). A 14-day exposure experiment of <italic>M. aeruginosa</italic> (1.7 &#xd7; 10<sup>7</sup> cells ml<sup>&#x2212;1</sup>) found that short-term ingestion of toxic <italic>M. aeruginosa</italic> is not fatal to <italic>H. cumingii</italic> and that mussels also can recover to health (<xref ref-type="bibr" rid="B16">Liu et&#xa0;al., 2020</xref>). In our study, <italic>M. aeruginosa</italic> stimulates immune responses of <italic>H. cumingii</italic> in a short-term exposure (7 days), and there was a significant reduction in the metabolism and immune abilities of mussels on the 28th day of this treatment. On the one hand, there were no dead mussels, and the concentration of <italic>M. aeruginosa</italic> used in the experiment (4.5 &#xd7; 10<sup>6</sup> cells ml<sup>&#x2212;1</sup>) was higher than that in natural environment (about 2 &#xd7; 10<sup>5</sup> cells ml<sup>&#x2212;1</sup> in China Lake Taihu and Dianchi), indicating that <italic>H. cumingii</italic> has a high tolerance to <italic>M. aeruginosa</italic> and the ability to control eutrophication in the natural environment. On the other hand, it should deserve attention that the toxic <italic>M. aeruginosa</italic> exhibits negative effects on the physiology such as the clearance rate and absorption efficiency of bivalves (<xref ref-type="bibr" rid="B12">Hu et&#xa0;al., 2016</xref>). The same as the results of our study, exposure to <italic>M. aeruginosa</italic> still influences the metabolism and the immunological mechanism of bivalves (<xref ref-type="bibr" rid="B11">Hu et&#xa0;al., 2015</xref>). Therefore, more studies are needed to use <italic>H. cumingii</italic> for bivalve biomanipulation. The purpose of this study was to help screen suitable algal diets for <italic>H. cumingii</italic> in industrialized cultures and provide supporting theories for bivalve biomanipulation by contrasting the effects of high-quality microalgal diets and the toxic <italic>M. aeruginosa</italic> on the physiological state of <italic>H. cumingii</italic>. The following is a specific analysis of how these microalgae affected the metabolism, immune enzyme, and gene expression levels of <italic>H. cumingii</italic>.</p>
<p>Transaminases have a key role in mobilizing amino acids for gluconeogenesis and function in carbohydrate and protein metabolism (<xref ref-type="bibr" rid="B18">Ramaswamy et&#xa0;al., 1999</xref>). Levels of GOT and GPT can reflect the turnover efficiency of amino acids, and they are usually used as biochemical markers to determine tissue damage in the liver when aquatic animals face changes in physiology and pathology induced by environmental conditions (<xref ref-type="bibr" rid="B10">Hong et&#xa0;al., 2015</xref>). The ability of aquatic animals to use carbohydrates depends on their ability of glucose oxidation, glycogen biosynthesis, and lipogenesis (<xref ref-type="bibr" rid="B8">Guo et&#xa0;al., 2006</xref>). HK and PK are two key glycolytic regulatory enzymes, and they can reflect the capacity to metabolize glucose in aquatic animals (<xref ref-type="bibr" rid="B27">Xia et&#xa0;al., 2015</xref>). A study about effects on aminotransferases activities of sea cucumber <italic>Apostichopus japonicus</italic> fed with different diets such as brown algae, red algae, and green algae and addition of benthic matter (composed of benthic diatoms, dinoflagellates, detritus, and fine clay particles) for 70 days shows that the mixture of red algae and benthic matter significantly increases GOT and GPT activities, transamination, and protein metabolism, and <italic>A. japonicus</italic> has a higher specific growth rate (<xref ref-type="bibr" rid="B25">Wen et&#xa0;al., 2016</xref>). To assess the influence of food type on biomarkers, the PK activity of mussels <italic>Mytilus galloprovincialis</italic> fed with commercial food is much lower than those fed with live microalgae (<italic>Isochrysis galbana</italic> and <italic>Tetraselmis chuii</italic>), suggesting decreased aerobic scope, increased gluconeogenesis, and lower nutritional status of mussels (<xref ref-type="bibr" rid="B2">Blanco-Rayon et&#xa0;al., 2019</xref>). In our study, GOT, GPT, PK, and HK activities of mussels in the <italic>Cyclotella</italic> sp. treatment remained stable and were significantly higher than those in <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic> treatments after 7 days. The 28-day toxic <italic>M. aeruginosa</italic> treatment significantly reduced these metabolic enzyme activities in the liver of <italic>H. cumingii</italic>. Results suggested that mussels in the <italic>Cyclotella</italic> sp. treatment had a higher capacity to metabolize protein and glucose, and decreased metabolic enzyme activities in mussels from the <italic>M. aeruginosa</italic> treatment might be caused by liver tissue damage.</p>
<p>LDLR has a crucial function in lipid uptake and transport into liver cells, then lipids are targeted to catabolic and anabolic pathways, and CPT1 has a key role in lipid catabolic metabolism (<xref ref-type="bibr" rid="B15">Liu et&#xa0;al., 2018</xref>). Similar to the results of the above metabolize enzymes, mussels in the <italic>Cyclotella</italic> sp. treatment had higher expression levels of LDLR and CPT1 than mussels in <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic> treatments, suggesting that these mussels had higher lipid uptake and metabolic efficiency. The 28-day toxic <italic>M. aeruginosa</italic> treatment led to metabolism dysfunction and affected the expression of related genes in mussels.</p>
<p>How to boost the immunity of mussels through nutritional methods should be a concern. Bivalves rely on innate immunity to provide defense, and this immunity involves both cell-mediated and humoral systems. The phosphomonoesterase AKP has a crucial function in the digestion and degradation of foreign proteins, carbohydrates, and lipids in the lysosome, participating in non-specific immune actions of aquatic animals (<xref ref-type="bibr" rid="B14">Liang et&#xa0;al., 2014</xref>). Under oxidative stress, when the production of free radicals exceeds the level of natural antioxidant defense regulation, it triggers the oxidation of DNA, protein, and lipids, resulting in multiple disease conditions (<xref ref-type="bibr" rid="B13">Ighodaro and Akinloye, 2018</xref>). Antioxidant enzymes such as SOD and CAT are the first and most important line of defense in the antioxidant system, respectively, dismutase superoxide radicals into H<sub>2</sub>O<sub>2</sub> and water and breakdown of H<sub>2</sub>O<sub>2</sub> into O<sub>2</sub> and water. Hydrolases AKP and antioxidase SOD and CAT, as non-specific humoral immune factors, participate in immune responses, and they are often used as reliable indicators in assessing the immune status of bivalves (<xref ref-type="bibr" rid="B11">Hu et&#xa0;al., 2015</xref>). Our results showed that AKP, SOD, and CAT activities of <italic>H. cumingii</italic> in the <italic>Cyclotella</italic> sp. treatment remained stable, and mussels in this treatment had higher immunity. The fluctuation of these immune enzyme activities in <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic> treatments may be related to changes in immune responses and physiological instability of <italic>H. cumingii</italic> caused by these algae. Similar to our study, after 45 days, feeding diets such as <italic>Chlorella</italic> sp. powder and <italic>Spirulina platensis</italic> powder significantly increased AKP, SOD, and CAT activities and absolute growth rates of pearl oyster <italic>Pinctada fucata martensii</italic> as compared with the corn gluten diet, suggesting that immunity of <italic>P. f. martensii</italic> can be improved by these algal diets. However, most AKP, SOD, and CAT activities in the <italic>M. aeruginosa</italic> treatment significantly increased at first and then decreased. It suggested that toxic algae stimulated immune responses of mussels in a short time (<xref ref-type="bibr" rid="B11">Hu et&#xa0;al., 2015</xref>) and then caused immune damage and enzyme inactivation.</p>
<p>HcIL-17 is a key inducer of proinflammatory cytokine secretion, IAP has a crucial function in regulating apoptosis and immune defense, and these genes have been verified to be involved in the bivalve immune responses (<xref ref-type="bibr" rid="B19">Rosani et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B29">Zhu et&#xa0;al., 2021</xref>). HcIL-17 and IAP expression levels of <italic>H. cumingii</italic> in the <italic>M. aeruginosa</italic> treatment increased on day 1 and then decreased after 14 days. Toxic algae created an inflammatory milieu in liver tissues and stimulated the immune response of mussels (<xref ref-type="bibr" rid="B4">Dou et&#xa0;al., 2020</xref>), and long-term stress of toxic algae caused immune disorders and metabolic imbalance and reduced the expression of related immune genes at last.</p>
<p>Results of PCA (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>) visually supported that the suitable algal diet played a significant role in metabolic abilities, immune function, and physiological status, shown by the strong clustering of the side with higher enzyme activities in the <italic>Cyclotella</italic> sp. treatment during the experimental period. When accompanied with the 28-day toxic <italic>M. aeruginosa</italic> treatment, the clustering effect weakened, suggesting that toxic algae caused metabolic disorders, immune injury, and poor physiological status.</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Biplot of principal component analysis (PCA) integrating metabolic and immune enzyme activities of <italic>Hyriopsis cumingii</italic>. <bold>(A)</bold> PCA for metabolic enzymes in liver, <bold>(B)</bold> PCA for immune enzymes in serum, and <bold>(C)</bold> PCA for immune enzymes in gill. Metabolic enzymes: GOT, GPT, PK, and HK. Immune enzymes: AKP, SOD, and CAT. Four microalgae treatments: <italic>Chlorella vulgaris</italic>, <italic>Navicula pelliculosa</italic>, <italic>Cyclotella</italic> sp., and <italic>Microcystis aeruginosa</italic>. Sampling time points: days 1, 7, 14, 21, and 28. GOT, glutamic oxaloacetate transaminase; GPT, glutamic pyruvate transaminase; PK, pyruvate kinase; HK, hexokinase; AKP, alkaline phosphatase; SOD, superoxide dismutase; CAT, catalase.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-09-970781-g004.tif"/>
</fig>
</sec>
<sec id="s5" sec-type="conclusions">
<title>Conclusions</title>
<p>Metabolism, immune enzyme, and gene expression levels in <italic>H. cumingii</italic> had no significant changes and remained at a high level in the <italic>Cyclotella</italic> sp. treatment on day 28, suggesting that <italic>Cyclotella</italic> sp. was the suitable algae for <italic>H. cumingii</italic>, followed by <italic>C. vulgaris</italic> and <italic>N. pelliculosa</italic>. The toxic <italic>M. aeruginosa</italic> treatment resulted in metabolic disorders and immune injury, though no mussels died. These findings provide basic information on metabolism and immune mechanisms in <italic>H. cumingii</italic> exposed to different algae. How the suitable algae can apply to practices of the long-term industrialized culture of <italic>H. cumingii</italic> by considering mussel growth and the pearl quality should be studied in the future. How to apply <italic>H. cumingii</italic> to bivalve biomanipulation in a large-scale or whole ecosystem needs more studies about the tolerance of mussels to <italic>M. aeruginosa</italic>, specific stocking methods, and adjusting measures to local conditions.</p>
</sec>
<sec id="s6" 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">
<bold>Supplementary Material</bold>
</xref>. Further inquiries can be directed to the corresponding author.</p>
</sec>
<sec id="s7" sec-type="ethics-statement">
<title>Ethics statement</title>
<p>All applicable international, national, and/or institutional guidelines for the care and use of animals were followed by the authors.</p>
</sec>
<sec id="s8" sec-type="funding-information">
<title>Funding</title>
<p>This work was supported by the earmarked fund for CARS (Grant No. CARS-49), the National Natural Science Foundation of China (Grant No. 31770965), and the Chongqing Natural Science Foundation Project (Grant No. cstc2020jcyj-msxmX0971).</p>
</sec>
<sec id="s9" 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="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>
</body>
<back>
<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/fmars.2022.970781/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2022.970781/full#supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet_1.docx" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document"/>
</sec>
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