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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.2021.728890</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Marine Science</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Elucidation of the Algicidal Mechanism of the Marine Bacterium <italic>Pseudoruegeria</italic> sp. M32A2M Against the Harmful Alga <italic>Alexandrium catenella</italic> Based on Time-Course Transcriptome Analysis</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Cho</surname> <given-names>Suhyung</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
<xref ref-type="author-notes" rid="fn002"><sup>&#x2020;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1334512/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Cho</surname> <given-names>Sang-Hyeok</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="author-notes" rid="fn002"><sup>&#x2020;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1232401/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Ko</surname> <given-names>So-Ra</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1451526/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Jeong</surname> <given-names>Yujin</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/343423/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Lee</surname> <given-names>Eunju</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Jin</surname> <given-names>Sangrak</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/849237/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Jeong</surname> <given-names>Bo-Seong</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Oh</surname> <given-names>Byung-Ha</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Oh</surname> <given-names>Hee-Mock</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Ahn</surname> <given-names>Chi-Yong</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/673913/overview"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Cho</surname> <given-names>Byung-Kwan</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c002"><sup>&#x002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/104384/overview"/>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Department of Biological Sciences and KI for the BioCentury, Korea Advanced Institute of Science and Technology</institution>, <addr-line>Daejeon</addr-line>, <country>South Korea</country></aff>
<aff id="aff2"><sup>2</sup><institution>Biological Resource Center, Korea Research Institute of Bioscience and Biotechnology</institution>, <addr-line>Daejeon</addr-line>, <country>South Korea</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Irene Wagner-Doebler, Helmholtz Center for Infection Research, Helmholtz Association of German Research Centers (HZ), Germany</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Chih-Ching Chung, National Taiwan Ocean University, Taiwan; David H. Green, Scottish Association for Marine Science, United Kingdom; Christopher John Stanley Bolch, University of Tasmania, Australia</p></fn>
<corresp id="c001">&#x002A;Correspondence: Suhyung Cho, <email>shcho95@kaist.ac.kr</email></corresp>
<corresp id="c002">Byung-Kwan Cho, <email>bcho@kaist.ac.kr</email></corresp>
<fn fn-type="equal" id="fn002"><p><sup>&#x2020;</sup>These authors have contributed equally to this work</p></fn>
<fn fn-type="other" id="fn004"><p>This article was submitted to Marine Molecular Biology and Ecology, a section of the journal Frontiers in Marine Science</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>29</day>
<month>09</month>
<year>2021</year>
</pub-date>
<pub-date pub-type="collection">
<year>2021</year>
</pub-date>
<volume>8</volume>
<elocation-id>728890</elocation-id>
<history>
<date date-type="received">
<day>22</day>
<month>06</month>
<year>2021</year>
</date>
<date date-type="accepted">
<day>08</day>
<month>09</month>
<year>2021</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2021 Cho, Cho, Ko, Jeong, Lee, Jin, Jeong, Oh, Oh, Ahn and Cho.</copyright-statement>
<copyright-year>2021</copyright-year>
<copyright-holder>Cho, Cho, Ko, Jeong, Lee, Jin, Jeong, Oh, Oh, Ahn and Cho</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 marine dinoflagellate <italic>Alexandrium</italic> is associated with harmful algal blooms (HABs) worldwide, causing paralytic shellfish poisoning (PSP) in humans. We found that the marine bacterium <italic>Pseudoruegeria</italic> sp. M32A2M exhibits algicidal activity against <italic>Alexandrium catenella</italic> (Group I), inhibiting its motility and consequently inducing cell disruption after 24 h of co-culture. To understand the communication between the two organisms, we investigated the time-course cellular responses through genome-wide transcriptome analysis. Functional analysis of differentially expressed genes revealed that the core reactions of the photosystem in <italic>A. catenella</italic> were inhibited within 2 h, eventually downregulating the entire pathways of oxidative phosphorylation and carbon fixation, as well as associated metabolic pathways. Conversely, <italic>Pseudoruegeria</italic> upregulated its glycolysis, tricarboxylic acid cycle, and oxidative phosphorylation pathways. Also, the transporters for nutrients such as C3/C4 carbohydrates and peptides were highly upregulated, leading to the speculation that nutrients released by disrupted <italic>A. catenella</italic> cells affect the central metabolism of <italic>Pseudoruegeria</italic>. In addition, we analyzed the secondary metabolite-synthesizing clusters of <italic>Pseudoruegeria</italic> that were upregulated by co-culture, suggesting their potential roles in algicidal activity. Our time-course transcriptome analysis elucidates how <italic>A. catenella</italic> is affected by algicidal bacteria and how these bacteria obtain functional benefits through metabolic pathways.</p>
</abstract>
<kwd-group>
<kwd>harmful algae</kwd>
<kwd><italic>Alexandrium</italic></kwd>
<kwd>transcriptome</kwd>
<kwd>algicidal bacteria</kwd>
<kwd>symbiosis</kwd>
</kwd-group>
<contract-sponsor id="cn001">National Research Foundation of Korea<named-content content-type="fundref-id">10.13039/501100003725</named-content></contract-sponsor>
<contract-sponsor id="cn002">National Research Foundation of Korea<named-content content-type="fundref-id">10.13039/501100003725</named-content></contract-sponsor>
<contract-sponsor id="cn003">National Research Foundation of Korea<named-content content-type="fundref-id">10.13039/501100003725</named-content></contract-sponsor>
<counts>
<fig-count count="6"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="86"/>
<page-count count="15"/>
<word-count count="11416"/>
</counts>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="S1">
<title>Introduction</title>
<p>Over the last several decades, harmful algal blooms (HABs) have been arising globally in both marine and freshwater bodies, causing severe ecological and economic damage to aquatic ecosystems and related industries (<xref ref-type="bibr" rid="B10">Asakawa et al., 2005</xref>; <xref ref-type="bibr" rid="B61">Peperzak, 2005</xref>; <xref ref-type="bibr" rid="B8">Anderson et al., 2008</xref>; <xref ref-type="bibr" rid="B24">Furuya et al., 2018</xref>). The representative microorganisms causing HABs are dinoflagellates or diatoms (<xref ref-type="bibr" rid="B6">Anderson, 1998</xref>; <xref ref-type="bibr" rid="B32">Heil et al., 2001</xref>; <xref ref-type="bibr" rid="B69">Shin et al., 2018</xref>), and dinoflagellates are known to account for 75% of all harmful algal species that cause HABs (<xref ref-type="bibr" rid="B70">Smayda, 1997</xref>).</p>
<p>In particular, the <italic>Alexandrium</italic> species complex of dinoflagellates, which includes <italic>A. tamarense</italic>, <italic>A. fundyense</italic>, and <italic>A. catenella</italic>, produces toxic molecules such as saxitoxins that cause paralytic shellfish poisoning (PSP) (<xref ref-type="bibr" rid="B7">Anderson et al., 2012</xref>). The blooms by <italic>Alexandrium</italic> species have been reported from coasts worldwide including the United States (<xref ref-type="bibr" rid="B5">Anderson, 1997</xref>), Europe (<xref ref-type="bibr" rid="B29">Hakanen et al., 2012</xref>), and Asia (<xref ref-type="bibr" rid="B30">Han et al., 1992</xref>; <xref ref-type="bibr" rid="B79">Wang and Wu, 2009</xref>; <xref ref-type="bibr" rid="B36">Ishikawa et al., 2014</xref>). In particular, blooms of <italic>A. catenella</italic> (Group I) have been observed regularly during the spring season along the Asian coast, and the southeastern coastal areas of Korea have been reported as hotspots for monitoring PSP (<xref ref-type="bibr" rid="B68">Shin et al., 2017</xref>).</p>
<p>Marine microorganisms form intricate interaction networks with other neighboring species beyond the predator&#x2013;prey relationship (<xref ref-type="bibr" rid="B4">Amin et al., 2012</xref>). Microorganisms communicate and interact by secreting various molecules within the phycosphere, although they are not bound directly to each other (<xref ref-type="bibr" rid="B66">Seymour et al., 2017</xref>). Recent studies are emphasizing the importance of biotic relationships between harmful algae and other microorganisms, such as bacteria (<xref ref-type="bibr" rid="B80">Yang et al., 2014</xref>), grazers (<xref ref-type="bibr" rid="B37">Jeong et al., 2008</xref>), and parasites (<xref ref-type="bibr" rid="B54">Lu et al., 2016</xref>; <xref ref-type="bibr" rid="B42">Kim et al., 2017</xref>). In a mutualistic relationship, phytoplankton provide diverse organic matters to bacteria, including carbon, nitrogen, and phosphorus. For example, organic sulfur in the form of dimethylsulfoniopropionate or dimethyl sulfide influences the metabolic activity and proliferation of bacteria (<xref ref-type="bibr" rid="B26">Gonzalez et al., 1999</xref>; <xref ref-type="bibr" rid="B11">Azam and Malfatti, 2007</xref>; <xref ref-type="bibr" rid="B38">Jiao et al., 2010</xref>). The phytoplankton-associated bacterium <italic>Roseobacter</italic> takes up heme from algal cellular debris for its iron requirements (<xref ref-type="bibr" rid="B33">Hogle et al., 2017</xref>). In return, algae acquire vitamins B1, B7, and B12 from bacteria for the regulation of cellular metabolic pathways and cell propagation, as well as signaling molecules such as indole-3-acetic acid, which promote cell division (<xref ref-type="bibr" rid="B19">Croft et al., 2005</xref>, <xref ref-type="bibr" rid="B20">2006</xref>; <xref ref-type="bibr" rid="B72">Tang et al., 2010</xref>; <xref ref-type="bibr" rid="B3">Amin et al., 2015</xref>).</p>
<p>Meanwhile, some bacteria are detrimental to diatoms/dinoflagellates owing to the release of algicidal molecules, proteases, nucleases, biosurfactants, siderophores for chelating Fe<sup>3+</sup> ions, and quorum-sensing molecules such as N-acyl homoserine lactones (<xref ref-type="bibr" rid="B35">Imamura et al., 2000</xref>; <xref ref-type="bibr" rid="B48">Lee et al., 2002</xref>; <xref ref-type="bibr" rid="B1">Ahn et al., 2003</xref>; <xref ref-type="bibr" rid="B60">Paul and Pohnert, 2011</xref>; <xref ref-type="bibr" rid="B4">Amin et al., 2012</xref>; <xref ref-type="bibr" rid="B63">Qi and Han, 2018</xref>). Recent studies have suggested that heterotrophic marine bacteria often affect marine phytoplankton blooms or bloom decline, playing a key role in balancing primary productivity in the marine ecosystem (<xref ref-type="bibr" rid="B14">Buchan et al., 2014</xref>; <xref ref-type="bibr" rid="B34">Hogle et al., 2016</xref>). <italic>Alexandrium</italic> is reported to be associated with <italic>Proteobacteria</italic> and <italic>Bacteroidetes</italic> at the phylum level and with multiple genera of <italic>Flavobacteriales</italic> at the order level during bloom peaks (<xref ref-type="bibr" rid="B31">Hattenrath-Lehmann and Gobler, 2017</xref>). Some bacteria under the <italic>Roseobacter</italic> lineage are known to interact mutualistically with phytoplankton for the transformation of carbon, nitrogen, phosphorus, and sulfur; however, these bacteria sometimes secrete pathogenic compounds when nutrient resources are limited, terminating algal blooms (<xref ref-type="bibr" rid="B2">Amaro et al., 2005</xref>; <xref ref-type="bibr" rid="B78">Wagner-Dobler and Biebl, 2006</xref>). Therefore, many marine bacteria showing algicidal effects have been currently recognized as potential tools to control HABs (<xref ref-type="bibr" rid="B43">Kim et al., 1998</xref>; <xref ref-type="bibr" rid="B56">Mayali and Azam, 2004</xref>; <xref ref-type="bibr" rid="B82">Zhang et al., 2014a</xref>).</p>
<p>Understanding the mutual associations of marine organisms between dinoflagellates/diatom and bacteria has becomes important; therefore, community analyses of phytoplankton and bacteria have been intensively performed through metagenome analyses (<xref ref-type="bibr" rid="B31">Hattenrath-Lehmann and Gobler, 2017</xref>; <xref ref-type="bibr" rid="B86">Zhou et al., 2018</xref>; <xref ref-type="bibr" rid="B21">Cui et al., 2020</xref>). Metagenome analyses demonstrate changes in the diversity of bacterial community caused by various biotic and abiotic factors, including HABs. Bacterial community data provide comprehensive information to analyze the characteristics of abundant bacteria during blooms; however, the information remains insufficient to understand specific functional interactions and underlying mechanisms.</p>
<p>To understand the cellular functions of dinoflagellates or cohabiting bacteria, transcriptome analyses of <italic>Alexandrium</italic> strains have been performed in optimized media or under nutrient deficiency (<xref ref-type="bibr" rid="B84">Zhang et al., 2014b</xref>; <xref ref-type="bibr" rid="B57">Meng et al., 2019</xref>; <xref ref-type="bibr" rid="B77">Vingiani et al., 2020</xref>), which have enabled the identification of functional characteristics or functional changes in different culture conditions. In addition, the transcriptome analysis of the marine bacterium <italic>Ruegeria pomeroyi</italic>, a member of the <italic>Roseobacter</italic> clade, has been performed in a co-culture with the dinoflagellate <italic>A. tamarense</italic> and diatom <italic>Thalassiosira pseudonana</italic> (<xref ref-type="bibr" rid="B46">Landa et al., 2017</xref>). Despite these advances, few studies have systematically elucidated the mutual interaction between <italic>Alexandrium</italic> and bacteria from the perspective of the metatranscriptome.</p>
<p>In this study, we found that the marine bacterium <italic>Pseudoruegeria</italic> sp. M32A2M exhibits algicidal activity against <italic>A. catenella</italic> (Group I). <italic>Pseudoruegeria</italic> sp. is representative of the marine <italic>Roseobacter</italic> group, which has been reported to appear frequently in various regions, including seas in East Asia and the North Sea (<xref ref-type="bibr" rid="B58">Park et al., 2014</xref>; <xref ref-type="bibr" rid="B62">Pohlner et al., 2017</xref>; <xref ref-type="bibr" rid="B85">Zhang et al., 2017</xref>). However, its function and characteristics as an algicidal bacterium are unknown. We monitored the sequential changes of the metatranscriptome occurring under the co-culture of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. Through differentially expressed gene (DEG) analysis, we elucidated how <italic>A. catenella</italic> is affected by <italic>Pseudoruegeria</italic> sp. and vice versa, with respect to various functional changes in metabolic pathways.</p>
</sec>
<sec id="S2" sec-type="materials|methods">
<title>Materials and Methods</title>
<sec id="S2.SS1">
<title><italic>A. catenella</italic> Pyrosequencing and BLASTN Analysis</title>
<p>Prior to cell culture, pyrosequencing of the 18S rRNA (3&#x2032; end), internal transcribed spacer 1 (ITS1), 5.8S rRNA, ITS2, and large subunit (LSU) rRNA genes was performed to identify the <italic>Alexandrium</italic> strain with the following paired primers: (i) ITS_F (GAGGAAGGAGAAGTCGTAACAAGG) and R732 (CCTTGGTCCGTGTTTCAAGAC), (ii) F341 (AGCGCA CAAGTACCATGAGG) and R1344 (TTCGGCAGGTGAG TTGTTACACAC), (iii) F918 (AGGTTCGTATCGATACTGACG TGC) and R2242 (CAGAGCACTGGGCAGAAATCAC), (iv) F1976 (GAAAAGGATTGGCTCTGAGG) and R3016 (AAACTAACCTTCTCACGACGGTC), and (v) F2843 (TTAC CACAGGGATAACTGGCTTG) and ETS_R (GCAGGGACA TAATCAGCACAC). Further, BLASTN analysis was performed using the pyrosequencing results (<xref ref-type="supplementary-material" rid="DS3">Supplementary Table 1</xref>).</p>
</sec>
<sec id="S2.SS2">
<title>Cell Culture</title>
<p><italic>A. catenella</italic> (Group I) collected from the South Sea in South Korea, was isolated using the micropipetting method, and maintained in sterilized Guillard&#x2019;s (F/2) medium (Sigma, St. Louis, MO, United States) with Red sea salt of 31 PSU (Red Sea, Houston, TX, United States), and subcultured with a 1/10 dilution approximately 40 times under a light&#x2013;dark cycle (12 h each) with 50 &#x03BC;mol&#x22C5;m<sup>&#x2013;2</sup>&#x22C5;s<sup>&#x2013;1</sup> photons at 20&#x00B0;C &#x00B1; 1&#x00B0;C. <italic>Pseudoruegeria</italic> sp. M32A2M was isolated from surface water of the South Sea in South Korea, where HABs of <italic>Alexandrium</italic> are frequently observed (<xref ref-type="bibr" rid="B16">Cho et al., 2020</xref>). <italic>Pseudoruegeria</italic> sp. was primarily cultured on marine agar 2216 plates (BD, Franklin Lakes, NJ, United States) at 25&#x00B0;C for 2 days. The cells scraped from agar plates were resuspended using gentle pipetting in F/2 media with Red sea salt and incubated for 2 days at 20&#x00B0;C &#x00B1; 1&#x00B0;C for adaptation in liquid media prior to co-culture with <italic>A. catenella</italic>. Thereafter, the <italic>Pseudoruegeria</italic> sp. culture medium was filtered through a 20 &#x03BC;m nylon net by gravity to remove some aggregated cells. Then, the OD<sub>600nm</sub> of filtrated cells was measured before inoculation into <italic>A. catenella</italic> cell medium. For this study, a total of 10 L of <italic>A. catenella</italic> (2,000 cells&#x22C5;mL<sup>&#x2013;1</sup>) and 1 L of <italic>Pseudoruegeria</italic> sp. (OD 0.3 at 600 nm) were cultured in F/2 medium.</p>
<p>For the co-culture of the two microorganisms, 100 mL of <italic>Pseudoruegeria</italic> sp. culture (OD 0.3 at 600 nm) estimated to be 6 &#x00D7; 10<sup>10</sup> cells in total, were each loaded into nine flasks containing 1 L of <italic>A. catenella</italic> culture (2,000 cells&#x22C5;mL<sup>&#x2013;1</sup>) of 2 &#x00D7; 10<sup>6</sup> cells in total. Three sets of flasks with three biological replicates were exposed to light for 2, 6, and 12 h with 50 &#x03BC;mol&#x22C5;m<sup>&#x2013;2</sup>&#x22C5;s<sup>&#x2013;1</sup> photons at 20&#x00B0;C &#x00B1; 1&#x00B0;C, respectively. As control groups, 100 mL of fresh medium was added into 1 L of pure-cultured <italic>A. catenella</italic> (2,000 cells&#x22C5;mL<sup>&#x2013;1</sup>), and 1 L of fresh medium was added into 100 mL of <italic>Pseudoruegeria</italic> sp. medium. Then, diluted cells were collected again using centrifugation prior to sequencing preparation.</p>
</sec>
<sec id="S2.SS3">
<title>Photosynthetic Pigment Assay</title>
<p>Chlorophyll-a (Chl-a) and carotenoid were extracted from <italic>A. catenella</italic> with 90% ethanol overnight at 4&#x00B0;C. These compounds were measured spectrophotometrically as follows: Chl-a (mg&#x22C5;L<sup>&#x2013;1</sup>) = (12.7 &#x00D7; A<sub>665</sub>) - (2.69 &#x00D7; A<sub>645</sub>), and carotenoid (mg&#x22C5;L<sup>&#x2013;1</sup>) = (1,000 &#x00D7; A<sub>470</sub> - 2.05 &#x00D7; C<sub>Chl&#x2013;a</sub>)/245 (where A<sub>665</sub>, A<sub>645</sub>, and A<sub>470</sub> indicate the absorbance at wavelengths of 665, 645, and 470 nm, respectively, and C<sub>Chl&#x2013;a</sub> represents the Chl-a content) (<xref ref-type="bibr" rid="B51">Li et al., 2015a</xref>).</p>
</sec>
<sec id="S2.SS4">
<title>Cell Separation</title>
<p>The co-cultured <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. mixtures were separated through 20 &#x03BC;m nylon net filter membranes (Merck Millipore, Burlington, MA, United States) by vacuum to avoid cross contamination of mRNA and to further construct clearer sequencing libraries. Then, the membrane was washed with 200 mL of fresh F/2 medium. The <italic>A. catenella</italic> collected on a filter membrane was resuspended with 50 mL of F/2 medium and centrifuged at 1,503 &#x00D7; <italic>g</italic> at 4&#x00B0;C for 10 min. The bacterial cells filtrated through the membrane were centrifuged at a high g-force of 3,381 &#x00D7; <italic>g</italic> for 10 min to collect the bacterial cells. The centrifugation at a high g-force for bacterial cells also helped disrupt the fragile cell membrane of a few residual <italic>A. catenella</italic>. <italic>A. catenella</italic> and bacterial cell pellets were resuspended with RNAlater<sup>TM</sup> (Invitrogen, Carlsbad, CA, United States) and incubated at 4&#x00B0;C for 1 h. Each pellet was stored at -80&#x00B0;C until further experiments.</p>
</sec>
<sec id="S2.SS5">
<title>Library Preparation for High-Throughput Sequencing</title>
<p>For total RNA extraction, cells were washed with extraction buffer comprising 200 mM Tris&#x2013;HCl (pH 7.5), 25 mM EDTA, 250 mM NaCl, and 0.5% SDS. Then, each pellet was instantly frozen using liquid nitrogen and ground to a fine powder. For RNA extraction of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp., TRIzol (Invitrogen) and phenol (Sigma) at 65&#x00B0;C were added to the powdered pellet, and this was immediately followed by ethanol precipitation.</p>
<p>The RNA-seq library was constructed using the TruSeq mRNA Sample Prep Kit (Illumina, San Diego, CA, United States) according to the manufacturer&#x2019;s instructions. Briefly, the poly-A-tailed mRNA of <italic>A. catenella</italic> was purified with oligo-dT magnetic beads. High-throughput sequencing with 100 bp single-end reads technically requires at least 100 bp RNA fragments. However, it is important to mention that RNA fragmentation causes a broad length distribution. To account for this, the purified mRNAs were further fragmented for 2 min to obtain RNA fragments with a median value of about 150 bp. cDNAs synthesized from the fragmented RNAs were ligated to adaptors and then amplified using qPCR.</p>
<p>For bacterial mRNA preparation, rRNAs from purified total RNAs (4 &#x03BC;g) were first depleted using the Ribo-zero<sup>TM</sup> rRNA Removal Kit for Epidemiology according to the manufacturer&#x2019;s instructions (Illumina). After ethanol precipitation of mRNAs (&#x223C;0.4 &#x03BC;g), the rRNA removal was confirmed using a TapeStation system 2200 (Agilent, Santa Clara, CA, United States). Then, the bacterial mRNAs were also fragmented to lengths of a median value of about 150 bp using a TruSeq mRNA Sample Prep Kit (Illumina), followed by ethanol precipitation.</p>
<p>The total library length for <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. was approximately 250&#x2013;300 bp by adaptor ligation and overlap extension qPCR for sequencing. The resulting library was sequenced by a HiSeq 2500 instrument with 100 bp single-end reads (Illumina).</p>
</sec>
<sec id="S2.SS6">
<title><italic>De novo</italic> Transcriptome Assembly and Differential Expression Analysis</title>
<p>After RNA-seq raw reads of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. were obtained from Illumina sequencing, the adapter sequences and low-quality sequences were trimmed using IlluQC software included in the NGSQCToolkit (<xref ref-type="bibr" rid="B59">Patel and Jain, 2012</xref>) and CLC Genomics Workbench 6.5.1 (CLCbio, Denmark) with the default setting. Then, <italic>de novo</italic> transcriptome assembly from RNA-seq raw reads of pure-cultured <italic>A. catenella</italic> was performed using Trinity v 2.0.6, with default settings for strand-specific RNA reads (<xref ref-type="bibr" rid="B27">Grabherr et al., 2011</xref>).</p>
<p>The RNA-seq reads from <italic>A. catenella</italic> were then aligned to the Trinity-assembled transcriptome by Bowtie2 to remove the misassembled sequences and their abundance was calculated using RNA-seq by Expectation Maximization (RSEM) (<xref ref-type="bibr" rid="B49">Li and Dewey, 2011</xref>; <xref ref-type="bibr" rid="B47">Langmead and Salzberg, 2012</xref>). RSEM results were transformed to fragments per kilobase of transcript per million (FPKM) values, and mis-assembled transcripts (FPKM cut-off = 1) were filtered out (<xref ref-type="bibr" rid="B74">Trapnell et al., 2010</xref>). Further, redundant isoform unigenes were removed by clustering with the BLAST-like alignment tool (BLAT) using tileSize = 8 and stepSize = 5, with other parameters set to default (<xref ref-type="bibr" rid="B41">Kent, 2002</xref>; <xref ref-type="bibr" rid="B84">Zhang et al., 2014b</xref>). Because this process results in a non-redundant set of the longest representative transcripts (i.e., unigenes), the analysis for various RNA isoforms by the alternative splicing or alternative polyadenylation was excluded.</p>
<p>From the unigene reference, the coding regions of the assembled transcript sequences were predicted using TransDecoder<sup><xref ref-type="fn" rid="footnote1">1</xref></sup> with the assistance of UniProt, BLASTP, Pfam, and HMMscan (HMMER v.3.2.1) (<xref ref-type="bibr" rid="B28">Haas et al., 2013</xref>; <xref ref-type="bibr" rid="B22">El-Gebali et al., 2018</xref>). For function annotation from coding sequences, BLASTx alignment was performed against the UniProt database with an E-value threshold of 10<sup>&#x2013;6</sup> (<xref ref-type="bibr" rid="B15">Camacho et al., 2009</xref>; <xref ref-type="bibr" rid="B75">UniProt: a hub for protein information, 2014</xref>). In addition, Gene Ontology (GO) functional annotation was performed based on the annotated UniProt ID (<xref ref-type="bibr" rid="B25">Gene Ontology Consortium, 2014</xref>). Together, Kyoto Encyclopedia of Genes and Genomes (KEGG) Ortholog ID and EuKaryotic Orthologous Groups (KOG) categorization were conducted (<xref ref-type="bibr" rid="B44">Koonin et al., 2004</xref>; <xref ref-type="bibr" rid="B40">Kanehisa et al., 2015</xref>).</p>
<p>Raw RNA reads from <italic>Pseudoruegeria</italic> sp. were mapped against the <italic>Pseudoruegeria</italic> sp. M32A2M reference genome in DDBJ/ENA/GenBank (GenBank assembly accession, <ext-link ext-link-type="DDBJ/EMBL/GenBank" xlink:href="GCA_010374725.1">GCA_010374725.1</ext-link>) using the CLC Genomics Workbench (version 6.5.1) (similarity score = 0.9 and length fraction = 0.9). GFF files were visualized using SignalMap software v.2.0.0.5 (Roche, Pleasanton, CA). Further, KEGG Ortholog ID and Clusters of Orthologous Groups (COG) categorization was performed based on the genome sequence of <italic>Pseudoruegeria</italic> sp. (<xref ref-type="bibr" rid="B73">Tatusov et al., 2000</xref>; <xref ref-type="bibr" rid="B40">Kanehisa et al., 2015</xref>).</p>
<p>For quantitative analysis of RNA expression, the expression levels of the unigenes of <italic>A. catenella</italic> and transcripts of <italic>Pseudoruegeria</italic> sp. were normalized by DESeq2 and calculated as reads per million (<xref ref-type="bibr" rid="B53">Love et al., 2014</xref>). Differentially expressed genes (DEGs) were classified when the fold change in the normalized RNA expression value of the co-cultured cells against that of the pure-cultured cells was more than twofold (|log<sub>2</sub>Fold change (FC)| &#x2265; 1) with a low <italic>p</italic>-value (DESeq <italic>P</italic> &#x003C; 0.05). Transcripts with low expression levels &#x003C; 50 reads per million in the pure-cultured cells were excluded for DEG analysis to avoid over-interpretation. GO enrichment analysis with DEGs was conducted using the BiNGO Cytoscape application (<xref ref-type="bibr" rid="B55">Maere et al., 2005</xref>).</p>
</sec>
</sec>
<sec sec-type="results" id="S3">
<title>Results</title>
<sec id="S3.SS1">
<title>Algicidal Effect of <italic>Pseudoruegeria</italic> sp. on <italic>A. catenella</italic></title>
<p>First, we identified the <italic>Alexandrium</italic> strain to be used in this study through the pyrosequencing of the LSU rRNA gene and the 18S rRNA fragment (<xref ref-type="supplementary-material" rid="DS3">Supplementary Table 1</xref>). We found that the <italic>Alexandrium</italic> strain was highly matched with the top four <italic>A. catenella</italic> strains screened in South Korea (DQ785887.1, DQ785886.1, AY347308.2, and DQ785885.1) in terms of total score from BLASTN analysis (<xref ref-type="supplementary-material" rid="DS3">Supplementary Table 1</xref>). In a previous study, we screened the marine bacterium <italic>Pseudoruegeria</italic> sp. M32A2M from regions where <italic>A. catenella</italic> was frequently found, and we characterized its genomic information through 16S rRNA sequencing and genome sequencing (<xref ref-type="bibr" rid="B16">Cho et al., 2020</xref>).</p>
<p>To investigate the algicidal activity of <italic>Pseudoruegeria</italic> sp., the Chl-a and carotenoid concentrations in <italic>A. catenella</italic> were measured according to the time of co-culture with <italic>Pseudoruegeria</italic> sp. (<xref ref-type="fig" rid="F1">Figure 1A</xref>). The Chl-a and carotenoid levels started to decrease from 2 h of co-culture and decreased significantly at 12 h of co-culture to 38.7 and 28.5% of the corresponding levels in pure-cultured cells, respectively. In pure culture, <italic>A. catenella</italic> had an integrated membrane with four chains; however, the cells began to remarkably lose membrane integrity following 24 h of co-culture (<xref ref-type="fig" rid="F1">Figure 1B</xref>). <italic>A. catenella</italic> has highly active flagella, as indicated by the phylum name Dinoflagellata. <italic>A. catenella</italic> showed highly active motility in pure culture (<xref ref-type="supplementary-material" rid="DS1">Supplementary Video 1</xref>), but after 24 h of co-culture, its motility was greatly decreased (<xref ref-type="supplementary-material" rid="DS2">Supplementary Video 2</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption><p>Co-culture of <italic>Alexandrium catenella</italic> and <italic>Pseudoruegeria</italic> sp. <bold>(A)</bold>. Changes in Chl-a and carotenoid concentrations in <italic>A. catenella</italic> were measured at 0 (pure), 2, 6, and 12 h of co-culture. <bold>(B)</bold> The morphological changes of <italic>A. catenella</italic> were observed before and after treatment with <italic>Pseudoruegeria</italic> sp. (after 24 h).</p></caption>
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</fig>
</sec>
<sec id="S3.SS2">
<title>Transcriptome Analysis of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp.</title>
<p>To understand how <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. communicate with each other during co-culture and how their cellular functions have been altered, we investigated the changes in the cellular transcriptomes in both organisms with the passage of co-culture time. As a control, pure-cultured <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. were used for subsequent comparison with co-cultured cells (<xref ref-type="fig" rid="F2">Figure 2A</xref>). For co-culture, the two microorganisms were incubated together for 2, 6, and 12 h with light exposure. Mixed cells with a large difference in size were isolated using a net membrane filter (<xref ref-type="fig" rid="F2">Figure 2A</xref>), because <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. lengths are 20&#x2013;48 &#x03BC;m and 1&#x2013;5 &#x03BC;m, respectively (<xref ref-type="bibr" rid="B23">Fukuyo, 1985</xref>; <xref ref-type="bibr" rid="B16">Cho et al., 2020</xref>). From the two isolated organisms, mRNAs for eukaryotes and bacteria were individually purified and sequenced using high-throughput sequencing (<xref ref-type="fig" rid="F2">Figure 2A</xref> and <xref ref-type="supplementary-material" rid="DS3">Supplementary Table 2</xref>). Consequently, the total mapped reads from <italic>A. catenella</italic> in high-throughput sequencing were 252,490,204 (<xref ref-type="fig" rid="F2">Figure 2B</xref>). The genome sequencing of <italic>A. catenella</italic>, which has a large genome size of more than hundreds of giga base pairs, is challenging. Therefore, to create the reference for <italic>A. catenella</italic>, the RNA-seq raw reads from pure-cultured <italic>A</italic>. <italic>catenella</italic> were <italic>de novo</italic> assembled using Trinity V 2.0.6. The total number of assembled transcripts was 245,489 (<xref ref-type="fig" rid="F2">Figure 2B</xref>). After the exclusion of isoforms by BLAT, 173,134 unigenes were obtained. Among the unigenes, 39,759 genes were functionally annotated through the functional retrieval procedures based on UniProt, GO, KEGG, and KOG (<xref ref-type="supplementary-material" rid="DS1">Supplementary Dataset 1</xref> and <xref ref-type="fig" rid="F2">Figure 2B</xref>).</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption><p>Transcriptome analysis of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. <bold>(A)</bold> Scheme of the transcriptome analysis process. <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. were each pure- cultured as the control. For the co-culture of the two organisms, 1 L of <italic>A. catenella</italic> (2,000 cells&#x22C5;mL<sup>&#x2013;1</sup>) and 100 mL of <italic>Pseudoruegeria</italic> sp. (OD<sub>600 nm</sub> 0.3) were cultured together for 2, 6, and 12 h with light exposure. All cultures had three experimental replicates. After co-culture, the two organisms were again isolated using filtration and then collected separately for RNA extraction. Finally, the purified mRNA was sequenced using RNA-seq. <bold>(B)</bold> Pipeline for transcriptome analysis of <italic>A. catenella</italic>. <bold>(C,D)</bold> Pearson&#x2019;s correlation analysis <bold>(C)</bold> and principal component analysis of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. <bold>(D)</bold> were performed from the transcriptomes of pure-cultured cells and co-cultured cells for 2, 6, and 12 h.</p></caption>
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</fig>
<p>The transcriptomes for pure-cultured and co-cultured (2, 6, and 12 h) <italic>Pseudoruegeria</italic> sp. were analyzed for the reference contigs (4,979 genes) (<xref ref-type="bibr" rid="B16">Cho et al., 2020</xref>; <xref ref-type="supplementary-material" rid="DS2">Supplementary Dataset 2</xref>). To verify experimental reproducibility between three biological replicates and to observe transcriptome changes in different culture conditions, we calculated Pearson&#x2019;s correlation coefficient for the unigene reference genes using the mapped read counts normalized by DESeq2. As a result, both <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. showed high Pearson&#x2019;s correlation coefficient of over 0.99 between three biological replicates (<xref ref-type="fig" rid="F2">Figure 2C</xref>). When observed between incubation times, <italic>A. catenella</italic> showed slight transcriptome variations for 2 h and 6 h but significant changes after 12 h (<xref ref-type="fig" rid="F2">Figure 2C</xref>). On the other hand, the transcriptome of <italic>Pseudoruegeria</italic> sp. started to change significantly from 2 h of co-culture. Similarly, in the principal component analysis, <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. showed distinct transcriptome changes according to the co-culture time with high reproducibility (<xref ref-type="fig" rid="F2">Figure 2D</xref>). Taken together, the cellular transcriptomes of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. affected each other and showed drastic changes at 12 h of co-culture.</p>
</sec>
<sec id="S3.SS3">
<title>Differentially Expressed Genes During the Co-culture of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp.</title>
<p>To investigate the reciprocal responding genes by co-culture, we selected the DEGs that satisfied the transcriptional changes over twofold with low <italic>p</italic>-values (DESeq <italic>P</italic> &#x003C; 0.05) after co-culture (see volcano plots in <xref ref-type="supplementary-material" rid="DS3">Supplementary Figure 1</xref>). Consequently, for <italic>A. catenella</italic>, among 39,759 genes, 1,716 (4.3%) and 2,602 (6.5%) genes were found to be upregulated and downregulated, respectively (<xref ref-type="fig" rid="F3">Figure 3A</xref>). In particular, 120 genes were commonly downregulated at 2, 6, and 12 h. For <italic>Pseudoruegeria</italic> sp., more than 20% of 4,246 genes were differentially regulated, i.e., 904 (21.3%) and 946 (22.3%) were upregulated and downregulated, respectively (<xref ref-type="fig" rid="F3">Figure 3B</xref>).</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption><p>Collection and grouping of differentially expressed genes (DEGs) during the co-culture of <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. <bold>(A,B)</bold>. The number of upregulated and downregulated genes from the gene dataset satisfying the DEG condition (|log<sub>2</sub> (Normalized RPM<sub>coculture</sub>/Normalized RPM<sub>pure&#x2013;culture</sub>)| &#x2265; 1 and low <italic>p</italic>-value (DESeq <italic>P</italic> &#x003C; 0.05), reads per million &#x003E; 50 in pure cells) were counted for <italic>A. catenella</italic> <bold>(A)</bold> and <italic>Pseudoruegeria</italic> sp. <bold>(B)</bold> according to the co-culture time. <bold>(C)</bold> DEGs of <italic>A. catenella</italic> were classified into 12 groups according to the RNA expression profile and are displayed using a heatmap. The RPM fold change of the genes in the 12th group are separately shown using a heatmap. An asterisk (&#x002A;) indicates cell wall-associated hydrolase- coding genes; double asterisks (&#x002A;&#x002A;) indicate a putative blue light receptor-coding gene; and triple asterisks (&#x002A;&#x002A;&#x002A;) indicate uncharacterized protein-coding genes. <bold>(D)</bold> The DEGs of <italic>Pseudoruegeria</italic> sp. were also classified into 12 groups according to the RNA expression profile. For example, the tripartite tricarboxylate transporter cluster (<italic>tctC-B-A</italic>) and DUF2282 domain containing membrane protein-coding genes were assigned in the 12th cluster, and their expression fold changes after co-culture are displayed using a heatmap. The expression profiles of the <italic>tct</italic> gene cluster at the pure-culture and co-cultures for 2, 6, and 12 h are displayed using SignalMap.</p></caption>
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</fig>
<p>The transcriptomes of <italic>Pseudoruegeria</italic> sp. and <italic>A. catenella</italic> also remarkably changed at 12 h of co-culture. To examine the patterns of transcriptome changes by co-culture time, all DEGs of both microorganisms were classified into 12 groups according to their fold change and expression pattern (<xref ref-type="supplementary-material" rid="DS1">Supplementary Datasets 1</xref>, <xref ref-type="supplementary-material" rid="DS2">2</xref>) and were visualized using heatmaps (<xref ref-type="fig" rid="F3">Figures 3C,D</xref>). For example, the 12th group of <italic>A. catenella</italic>, which showed a highly increased expression pattern only at 12 h of co-culture, consisted of transcripts for three cell wall-associated hydrolases (<sup>&#x2217;</sup>), which may cause membrane destruction; a blue light receptor (<sup>&#x2217;&#x2217;</sup>); and uncharacterized proteins (<sup>&#x2217;&#x2217;&#x2217;</sup>). For <italic>Pseudoruegeria</italic> sp., the tripartite tricarboxylated transporter clusters (<italic>tctC-tctB-tctA</italic>) and DUF2282 domain containing predicted integral membrane proteins were assigned to the 12th group, which showed rapid increase at 12 h of co-culture, suggesting that the uptake of short carbohydrates can be active at 12 h of co-culture (<xref ref-type="fig" rid="F3">Figure 3D</xref>).</p>
</sec>
<sec id="S3.SS4">
<title>Functional Analysis of DEGs of <italic>A. catenella</italic> During Co-culture</title>
<p>To systematically investigate the cellular functions of genes changed by the co-culture of the two organisms, the DEGs in <italic>A. catenella</italic> were classified through GO enrichment analysis (<xref ref-type="supplementary-material" rid="DS3">Supplementary Table 3</xref>). Interestingly, the genes involved in the photosynthetic electron transport chain and PSII started to be downregulated from 2 h (Cluster 1/1) (<xref ref-type="fig" rid="F4">Figure 4A</xref>). At 12 h, downregulation expanded to genes related to carbohydrate metabolism (Cluster 1/13); phosphorus/phosphate metabolic processes (Cluster 2/13); and the detection of external stimuli, including light- and abiotic factor-related genes (Cluster 3/13), as well as photosynthesis. In addition, the genes related to the movement of microtubules, which are associated with cell motility and division, as a part of the cytoskeleton (<xref ref-type="bibr" rid="B76">Vale, 2003</xref>), were jointly downregulated (<xref ref-type="supplementary-material" rid="DS3">Supplementary Table 3</xref>). These results are consistent with the drastic decrease in Chl-a and carotenoids, which are important for photosynthesis, and reduced motility and membrane disintegration of <italic>A. catenella</italic>. For upregulated clusters, the transcription of macromolecule biosynthetic process/metabolic pathways, ribosome assembly, and translation-associated genes increased from 2 h (<xref ref-type="supplementary-material" rid="DS3">Supplementary Table 3</xref>). At 12 h, the transcription levels of RNA synthesis/processing/modification and ribonucleotide/nucleoside-related processes markedly increased.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption><p>Functional analysis of downregulated genes in <italic>A. catenella</italic> by co-culture. <bold>(A)</bold> Functional clustering through GO enrichment analysis was executed by co-culture time (2, 6, and 12 h) from downregulated DEGs in <italic>A. catenella</italic>, among which core clusters are displayed according to gene abundance. The node size indicates the gene number, and the color key indicates the log<sub>10</sub> <italic>p</italic>-value of DEG. <bold>(B)</bold> KEGG analysis results from the DEGs in <italic>A. catenella</italic> are also shown by co-culture time. <bold>(C)</bold> Transcriptome changes after co-culture in the genes of photosystem II (PSII), cytochrome b6f, PSI, and ATP synthase in the oxidative phosphorylation pathway are displayed using a heatmap, according to the co-culture time. FC indicates the fold change in transcriptome after co-culture.</p></caption>
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</fig>
<p>Furthermore, the functional changes from the perspective of metabolic pathway were investigated through KEGG analysis. As the reference genome for KEGG analysis, the first fully genome-sequenced eukaryotic marine phytoplankton, <italic>Thalassiosira pseudonana</italic>, was used (<xref ref-type="bibr" rid="B9">Armbrust et al., 2004</xref>). Overall, <italic>A. catenella</italic> expressed a drastically changed transcriptome at 12 h (<xref ref-type="fig" rid="F4">Figure 4B</xref>). However, energy metabolism-associated genes, including photosynthesis and oxidative phosphorylation, uniquely began to be downregulated continuously from 2 h, and the number of downregulated genes gradually increased with co-culture time (<xref ref-type="fig" rid="F4">Figure 4B</xref> and <xref ref-type="supplementary-material" rid="DS3">Supplementary Figure 2A</xref>). At 12 h, energy metabolism genes associated with carbon fixation, nitrogen metabolism, and sulfur metabolism were additionally downregulated (<xref ref-type="fig" rid="F4">Figure 4B</xref> and <xref ref-type="supplementary-material" rid="DS3">Supplementary Figure 2A</xref>). Furthermore, carbohydrate metabolism genes associated with glycolysis, the tricarboxylic acid (TCA) cycle, and the pentose phosphate pathway were intensively downregulated at 12 h (<xref ref-type="fig" rid="F4">Figure 4B</xref> and <xref ref-type="supplementary-material" rid="DS3">Supplementary Figure 3</xref>).</p>
<p>The results of GO and KEGG analysis together show that the transcription of genes associated with photosynthesis and oxidative phosphorylation in <italic>A. catenella</italic> is primarily deactivated by co-culture with <italic>Pseudoruegeria</italic> sp., which seems to significantly affect carbon fixation- and carbohydrate-associated metabolism upon long-term exposure. In detail, we investigated the transcriptomic changes in photosynthesis-related oxidative phosphorylation among metabolic pathways at the gene level (<xref ref-type="fig" rid="F4">Figure 4C</xref>). Among photosynthesis pathways, PSII is the first light-dependent oxygenic protein complex (<xref ref-type="supplementary-material" rid="DS3">Supplementary Figure 3</xref>). It consists of D1 protein (PsbA), which binds chlorophyll P680, and D2 proteins (PsbD) as reaction-center proteins. It is also surrounded by a CP43/CP47 (PsbB/PsbC) core complex of antenna and light-harvesting complexes to employ chlorophyll and pigments to absorb light. It also forms a complex with Cyt b559 subunits (PsbE/PsbF), oxygen-evolving complex (PsbO and PsbP), and other complex proteins. The transcription levels of <italic>psbA</italic>, <italic>psbB</italic>, <italic>psbC</italic>, <italic>psbD</italic>, and <italic>psbE</italic> in the PSII complex were very high, ranking as 1st, 2nd, 13th, 22nd, and 30th, respectively, in the overall transcript expression profile (<xref ref-type="supplementary-material" rid="DS1">Supplementary Dataset 1</xref>); however, they were all significantly downregulated upon short-term exposure to <italic>Pseudoruegeria</italic> sp. (<xref ref-type="fig" rid="F4">Figure 4C</xref>). The core <italic>petB</italic> (cyt b<italic><sub>6</sub></italic>) and <italic>petD</italic> (cyt b<italic><sub>6</sub></italic>f-IV) subunits of the cytochrome b<italic><sub>6</sub></italic>f complex that transfers electrons from PSII to PSI (<xref ref-type="bibr" rid="B45">Kurisu et al., 2003</xref>) were gradually downregulated with an increase in co-culture time (<xref ref-type="fig" rid="F4">Figure 4C</xref> and <xref ref-type="supplementary-material" rid="DS3">Supplementary Figure 3</xref>). Consecutively, similar to PSII, PSI reduced the transition from NADP to NADPH through light-driven reactions of photosynthesis. PsaA (A1) and PsaB (A2), which are photosynthetic reaction center proteins among the PSI complex, were also downregulated upon co-culture (<xref ref-type="fig" rid="F4">Figure 4C</xref>). This is consistent with the downregulation pattern of PSII center proteins (D1 and D2 proteins). The downregulation of the center proteins in the two photosystems can inhibit the assembly of the complex, including the antenna proteins and pigments. In addition, the transcription of <italic>atpA</italic> and <italic>atpB</italic> of F1, which is responsible for hydrolyzing ATP in the ATP synthase complex, was highly downregulated (<xref ref-type="fig" rid="F4">Figure 4C</xref>). ATP from ATP synthase and NADPH from PSI are necessary for carbon fixation. As a result, the downregulation of photosynthesis-associated core genes consequently led to the downregulation of carbon fixation metabolic processes, including rubisco, glycolysis, and pentose phosphate pathways (<xref ref-type="supplementary-material" rid="DS3">Supplementary Figure 3</xref>).</p>
</sec>
<sec id="S3.SS5">
<title>Functional Analysis of the Differentially Expressed Genes of <italic>Pseudoruegeria</italic> sp. During Co-culture</title>
<p>The DEGs in <italic>Pseudoruegeria</italic> sp. were functionally classified through GO enrichment analysis (<xref ref-type="supplementary-material" rid="DS3">Supplementary Table 4</xref>). In particular, translation-associated genes (Cluster 1/3) and electron transport chain genes (Cluster 2/3) were continuously upregulated from 2 h onward (<xref ref-type="fig" rid="F5">Figure 5A</xref>). Unlike the observations in <italic>A. catenella</italic>, ATP biosynthetic process genes (Cluster 1/7) and energy generation by respiration and TCA genes (Cluster 2/7) were highly upregulated at 12 h. However, genes for biosynthetic processes of vitamins/porphyrins were downregulated at 2 and 6 h of co-culture, and genes for transmembrane transport and some response networks to external stimuli were also downregulated at 12 h of co-culture (<xref ref-type="supplementary-material" rid="DS3">Supplementary Table 4</xref>).</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption><p>Functional changes in <italic>Pseudoruegeria</italic> sp. by co-culture. <bold>(A)</bold> Functional clustering through GO enrichment analysis from upregulated DEGs in <italic>Pseudoruegeria</italic> sp. are displayed by culture time. The node size indicates the gene number, and the color key indicates the log<sub>10</sub> <italic>p</italic>-value of DEG. <bold>(B)</bold> KEGG analysis from the DEGs in <italic>Pseudoruegeria</italic> sp. are also shown during co-culture. <bold>(C,D)</bold> Transcriptome fold changes (FC) of the genes related to oxidative phosphorylation <bold>(C)</bold> and membrane transport <bold>(D)</bold> are displayed by the co-culture time using a heatmap. <bold>(E)</bold> RNA expression and its changes in secondary metabolite-synthesizing gene clusters in <italic>Pseudoruegeria</italic> sp. are shown using a heatmap, according to the co-culture time. <bold>(F)</bold> Transcriptome fold changes of the bacterial secretion systems, the Sec-dependent secretion (Sec) and twin-arginine targeting (Tat) systems, are shown by co-culture time using a heatmap. FC indicates the fold change in transcriptome after co-culture.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-08-728890-g005.tif"/>
</fig>
<p>Furthermore, the DEGs in <italic>Pseudoruegeria</italic> sp. were classified using KEGG, with the reference being <italic>Ruegeria pomeroyi</italic>, which is a member of the marine <italic>Roseobacter</italic> clade and is phylogenetically close to <italic>Pseudoruegeria</italic> sp. (<xref ref-type="bibr" rid="B58">Park et al., 2014</xref>). Carbohydrate metabolism genes involved in glyoxylate and dicarboxylate metabolism, TCA cycle, and glycolysis were particularly highly upregulated (<xref ref-type="fig" rid="F5">Figure 5B</xref> and <xref ref-type="supplementary-material" rid="DS3">Supplementary Figures 2B</xref>, <xref ref-type="supplementary-material" rid="DS3">4</xref>). Furthermore, energy metabolism, amino acid metabolism, membrane transport, and cellular community-associated genes were together highly upregulated upon co-culture (<xref ref-type="fig" rid="F5">Figure 5B</xref>). Especially, the transcriptomes of the genes associated with oxidative phosphorylation among the category of energy metabolism, such as NADH dehydrogenase (<italic>Nuo</italic>), succinate dehydrogenase (<italic>Sdh</italic>), cytochrome C reductase (Pet), cytochrome C oxidase (<italic>Cta</italic>), and F-type ATPase (<italic>Atp</italic>), significantly increased after co-culture with <italic>A. catenella</italic> (<xref ref-type="fig" rid="F5">Figure 5C</xref>).</p>
<p>In addition, the transcription levels of membrane transport genes were observed to be highly upregulated following 2 h of co-culture (<xref ref-type="fig" rid="F5">Figure 5D</xref>). In particular, the genes associated with branched-chain amino acid (BCAA) ABC transporter (<italic>livG-F-H-M-K</italic>); microcin C transporter (<italic>yejA-B-E-F</italic>); and oligopeptide transporter (<italic>oppA-B-C-D-F</italic>), which play a role in transferring dipeptides, branched-chain amino acids, oligopeptides, and proteins into the cytoplasm, were highly upregulated (<xref ref-type="fig" rid="F5">Figure 5D</xref>). In addition, tripartite ATP-independent periplasmic (TRAP) transporter (<italic>dctP-Q-M</italic>) and tricarboxylate transporter (<italic>tctA-B-C</italic>) genes used for the uptake of tricarboxylates such as citrate and C4-dicarboxylates as metabolites in the TCA cycle, were also substantially upregulated (<xref ref-type="fig" rid="F5">Figure 5D</xref>).</p>
<p>In both KEGG and GO analyses, genes associated with vitamins and the metabolism of cofactors were downregulated or upregulated according to the type of vitamin. Several genes for porphyrin and chlorophyll metabolism for cobalamin (vitamin B12) biosynthesis and the metabolism of thiamine (vitamin B1), pyridoxine (vitamin B6), and nicotinamide (vitamin B3) were downregulated (<xref ref-type="fig" rid="F5">Figure 5E</xref> and <xref ref-type="supplementary-material" rid="DS3">Supplementary Figures 2B, 5</xref>).</p>
</sec>
<sec id="S3.SS6">
<title>Transcriptome Analysis of the Clusters for Secondary Metabolite Synthesis/Secretion System</title>
<p>Interestingly, algicidal effect by co-culture with <italic>Pseudoruegeria</italic> sp. was also observed in the supernatant after the removal of cells from co-culture, indicating that <italic>Pseudoruegeria</italic> sp. secretes algicidal compounds into the extracellular environment. To predict the metabolites secreted by <italic>Pseudoruegeria</italic> sp. that could cause this algicidal effect, we searched the secondary metabolite synthesis clusters, which had been predicted using Antismash (<xref ref-type="bibr" rid="B16">Cho et al., 2020</xref>). As a result, several secondary metabolite-synthesizing gene clusters encoding bacteriocin, NRPS/T1PKS, terpene, &#x03B2;-lactone, ectoine, <sc>L</sc>-homoserine lactone, and lasso peptide were found from the <italic>Pseudoruegeria</italic> sp. genome sequences (<xref ref-type="fig" rid="F5">Figure 5E</xref> and <xref ref-type="supplementary-material" rid="DS3">Supplementary Table 5</xref>). Further, when the transcriptome changes of these clusters were examined, the core genes of the peptide toxin bacteriocin, which is known to be harmful to some mammals and other bacteria (<xref ref-type="bibr" rid="B17">Cornut et al., 2008</xref>; <xref ref-type="bibr" rid="B18">Cotter et al., 2013</xref>), and the lasso peptide gene cluster, which encodes a type of bacteriocin, were highly upregulated under co-culture. In addition, the clusters associated with the synthesis of &#x03B2;-lactone, which is known as a natural algicidal molecule, showed high RNA expression levels and significantly increased transcriptomic expression during co-culture (<xref ref-type="fig" rid="F5">Figure 5E</xref>).</p>
<p>If the algicidal molecule secreted from bacteria is a peptide or protein-based molecule, the bacteria may also use their own secretion system. Accordingly, we monitored the transcription of bacterial secretion systems, including the sec-dependent system, e.g., <italic>secA</italic>, <italic>secDF</italic>, <italic>secYEG</italic>, <italic>secB</italic>, <italic>yajC</italic>, <italic>ftsY</italic>, and <italic>ffh</italic>, and the twin-arginine translocation system, e.g., <italic>tatA</italic> and <italic>tatBC</italic>, for the secretion of peptides/proteins such as bacteriocin. The transcription of such genes also started to increase from 2 h of co-culture and indicated the highest change at 12 h of co-culture (<xref ref-type="fig" rid="F5">Figure 5F</xref>).</p>
</sec>
</sec>
<sec sec-type="discussion" id="S4">
<title>Discussion</title>
<p>Molecular understanding of the relationship between HABs and algicidal bacteria remains insufficient. In this study, we observed that <italic>A. catenella</italic> exhibited a noticeable decrease in motility and thereafter lost membrane integrity after 24 h of co-culture with <italic>Pseudoruegeria</italic> sp. M32A2M. Through interactive transcriptome analysis at different time points of co-culture, we further investigated how <italic>A. catenella</italic> was affected by co-culture and how <italic>Pseudoruegeria</italic> would benefit from the association.</p>
<p>Although the phenotype of <italic>A. catenella</italic> showed no significant changes at 6 h, the cellular transcriptomes of a few genes began to change within 2 h. These were photosynthesis-associated genes for oxidative phosphorylation; photosynthetic reaction center proteins, including <italic>psbAB</italic> of PSII, <italic>psaAB</italic> of PSI, <italic>petBD</italic> of Cyt b6f, and <italic>atpAB</italic> of ATP synthase. The photosynthesis-related genes started to be uniquely downregulated from 2 h of co-culture and showed the highest down-regulation at 12 h of co-culture (<xref ref-type="fig" rid="F6">Figure 6</xref>). Meanwhile, the down-regulation of carbohydrates metabolism related genes was noticeably detected only at 12 h of co-culture. Time-course transcriptome analysis using GO enrichment and KEGG analysis reflected that the rapid down-regulation of photosynthetic genes affect the deactivation of carbon fixation, glycolysis, and its associated pathways; DNA topological changes; and a decrease in microtubule-based movement at 12 h (<xref ref-type="fig" rid="F6">Figure 6</xref>). These results were in accordance with our observations in <xref ref-type="fig" rid="F1">Figure 1</xref> that Chl-a and carotenoid concentrations of <italic>A. catenella</italic> started to be downregulated from 2 h of co-culture and were noticeably the lowest at 12 h of co-culture.</p>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption><p>Changes in metabolic pathways by communication between <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. <bold>(A,B)</bold> A scheme for the communication of <italic>A. catenella</italic> <bold>(A)</bold> and <italic>Pseudoruegeria</italic> sp. <bold>(B)</bold> during co-culture is displayed based on transcriptome analysis. Blue and red arrows indicate the downregulated (&#x2193;) and upregulated (&#x2191;) genes, respectively. The dashed line indicates multiple reaction steps.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-08-728890-g006.tif"/>
</fig>
<p>When cells are disrupted, many cellular nutrients are released into the environment, and the surrounding microorganisms can use these nutrients. Interestingly, in case of <italic>Pseudoruegeria</italic> sp., the transcription of transporters for the uptake of organic matters, such as C4-dicarboxylate transporter for malate, fumarate, and oxaloacetate and tricarboxylate transporter for citrate, which are core metabolites for the TCA cycle, was substantially increased after co-culture. In addition, the transporters for amino acids, dipeptides and oligopeptides, and proteins were also upregulated from 2 h of co-culture. The upregulation of various transporters for nutrient uptake seems to be closely related with the upregulation of its central metabolism, including the TCA cycle and oxidative phosphorylation pathways, by NADH dehydrogenase (Complex I), fumarate reductase (Complex II), cytochrome bc1 complex (Complex III), cytochrome c oxidase (Complex IV), and ATP synthase (Complex V) on the membrane after co-culture with <italic>A. tamarense</italic> (<xref ref-type="fig" rid="F6">Figure 6</xref>).</p>
<p>Further, the secondary metabolite biosynthesis gene clusters were found in <italic>Pseudoruegeria</italic> sp. Among several clusters, the transcriptomes of bacteriocin- and lasso peptide-synthesizing related genes were specifically upregulated. Bacteriocin and lasso peptide are known to be harmful to some mammals and other bacteria (<xref ref-type="bibr" rid="B17">Cornut et al., 2008</xref>; <xref ref-type="bibr" rid="B18">Cotter et al., 2013</xref>). In addition, the transcription of the &#x03B2;-lactone gene cluster significantly increased during co-culture. <italic>Ruegeria pomeroyi</italic>, a member of the <italic>Roseobacter</italic> clade, like <italic>Pseudoruegeria</italic> sp., produces lactones showing algicidal activity, suggesting the important ecological role of lactone in the interaction between these bacteria and algae (<xref ref-type="bibr" rid="B65">Riclea et al., 2012</xref>). Therefore, the increase in the transcription levels of the bacteriocin, the lasso peptide, and the &#x03B2;-lactone cluster implies their potential as algicides. Furthermore, we observed the increase in the transcriptome of the Sec and Tat bacterial secretion systems for unfolded proteins and folded protein secretion, respectively. This suggests that <italic>Pseudoruegeria</italic> sp. may use these secretion systems for the secretion of extracellular molecules such as peptide toxins during co-culture with <italic>A. catenella</italic> (<xref ref-type="fig" rid="F6">Figure 6</xref>).</p>
<p>However, the cofactors and vitamins B1, B3, B6, and B12, necessary for the cellular regulation and propagation of dinoflagellates, were extremely downregulated. Dinoflagellates such as <italic>A. catenella</italic> are known to require vitamins B1, B7, and B12 for their viability (<xref ref-type="bibr" rid="B71">Tandon et al., 2017</xref>). <italic>Ruegeria</italic> supplies these vitamins to vitamin-auxotroph algae under commensal relationships (<xref ref-type="bibr" rid="B19">Croft et al., 2005</xref>, <xref ref-type="bibr" rid="B20">2006</xref>; <xref ref-type="bibr" rid="B71">Tandon et al., 2017</xref>). However, the synthesis of vitamins B1 and B12 in <italic>Pseudoruegeria</italic> sp. was downregulated upon co-culture with <italic>A. catenella</italic>, supporting that it might not have a commensal relationship with <italic>A. catenella</italic> based on vitamin supply. Overall, our results indicate that <italic>Pseudoruegeria</italic> sp. exhibits a typical algicidal effect that inactivates the photosystems and disrupts cell membranes, ultimately leading to the death of <italic>A. catenella</italic>. However, it is not clear yet whether the inactivation of the photosystems is due to direct targeting of the algicides or an indirect result through the inhibition of the photosystem precursor metabolic pathway. Nevertheless, the unique downregulation of photosystems among all metabolic pathways at 2 h of co-culture suggests that the algicides from <italic>Pseudoruegeria</italic> sp. may closely participate in the initiative process of photosynthesis. In fact, there are known herbicides or algicides that target photosystem II, e.g., triazine, diuron, ametryn, atrazine, tebuthiuron, hexazinone, DCMU (3-(3,4-dichlorophenyl)-1,1-dimethylurea), and terbutryn. These compounds inhibit the photosynthesis by blocking electron transfer from Q<sub>A</sub> to Q<sub>B</sub>, by substituting the plastoquinone binding site on the D1 protein of PSII (<xref ref-type="bibr" rid="B67">Shaw et al., 2010</xref>; <xref ref-type="bibr" rid="B13">Broser et al., 2011</xref>). Accordingly, we surmise that the algicides secreted by <italic>Pseudoruegeria</italic> sp., may play a role similar to that of herbicides that block the Q<sub>B</sub> plastoquinone binding site of PSII. Further research on the algicides secreted from <italic>Pseudoruegeria</italic> sp. is expected to provide a more comprehensive explanation of the relationship between <italic>A. catenella</italic> and algicidal bacteria.</p>
<p>As we mentioned earlier, the use of algicidal bacteria, with various reported algicidal mechanisms, has been proposed as a biological control method against HABs. Li et al. isolated an algicidal bacterium, <italic>Altererythrobacter</italic> sp. LY02, which acts against <italic>A. tamarense</italic> (<xref ref-type="bibr" rid="B50">Li et al., 2016</xref>). They suggested that the active substance causes severe morphological and structural damage to the cells and organelles. They also found another algicidal bacterium of <italic>A. tamarense</italic>, <italic>Deinococcus xianganensis</italic>, which produces deinoxanthin (<xref ref-type="bibr" rid="B52">Li et al., 2015b</xref>). Deinoxanthin induces the production of reactive oxygen species (ROS) in <italic>A. tamarense</italic>, resulting in serious damage to the structure of organelles, including the chloroplasts and mitochondria. <xref ref-type="bibr" rid="B80">Yang et al. (2014)</xref> reported that the algicidal bacterium <italic>Joostella</italic> sp. DH77-1 can kill <italic>A. tamarense</italic>. The substance secreted by this bacterium was found to affect membrane integrity and the activity of antioxidant enzymes, such as superoxide dismutase and peroxidase; protein production; and pigment contents. Antioxidant defense enzymes, such as superoxide dismutases (SOD), catalase, glutathione peroxidase, and peroxiredoxin, can be induced by the generation of ROS that promotes the apoptosis by extrinsic and intrinsic signaling pathways (<xref ref-type="bibr" rid="B64">Redza-Dutordoir and Averill-Bates, 2016</xref>).</p>
<p>Accordingly, we examined the transcriptome of ROS-related genes in <italic>A. catenella</italic> when co-cultured with <italic>Pseudoruegeria</italic> sp. Interestingly, at 12 h of co-culture, we observed the 12 upregulated ROS-related genes (log<sub>2</sub>FC &#x003E; 1), including glutathione S-transferase, RAC serin/threonine-protein kinase, arsenite methyltransferase, and soluble epoxide hydrolase/lipid-phosphate phosphatase, when mapped against the total reference genome database in KEGG. To speculate whether the increase of ROS in <italic>A. catenella</italic> affects the apoptosis, the transcriptional changes of apoptosis-related genes in <italic>A. catenella</italic> were further investigated after co-culture. In fact, the apoptosis mechanism is well described in mammals but is not well-known in algae. Recently, a marine bacterium, <italic>Phaeobacter inhibens</italic>, was reported to induce the apoptosis-like programmed cell death through cellular caspase like molecules in <italic>Emiliania huxleyi</italic>, which forms expansive blooms (<xref ref-type="bibr" rid="B12">Bramucci and Case, 2019</xref>). We also found that the apoptosis-related cathepsin or cathepsin like proteases, cathepsin B, cathepsin D, cathepsin F, and cathepsin X, were particularly upregulated at 12 h of co-culture. Especially, lysosomal hydrolases, a cathepsin family of proteases, is known to promote the lysosomal damage and determine the cell fate (<xref ref-type="bibr" rid="B39">Johansson et al., 2010</xref>). This suggests that <italic>A. catenella</italic> may induce its apoptosis through the activation of corresponding proteases promoted by ROS during co-culture with algicidal bacteria, and finally induce the destruction of the membrane after 24 h of long-term co-culture (<xref ref-type="fig" rid="F6">Figure 6</xref>). However, it is still not clear whether <italic>A. catenella</italic> uses a similar mechanism for apoptosis because cathepsin is a usual protease found in mammalian cells.</p>
<p><xref ref-type="bibr" rid="B83">Zhang et al. (2018)</xref> isolated the marine bacterium <italic>Paracoccus</italic> sp. strain Y42, which acts against the HAB-causing dinoflagellate <italic>Prorocentrum donghaiense</italic>. Y42 primarily targets dinoflagellates, showing algicidal activities against <italic>A. minutum</italic>, <italic>Scrippsiella trochoidea</italic>, and <italic>Skeletonema costatum</italic>. The potential algicides from Y42 have been found to cause the loss of photosynthetic pigments and the decline of photosynthesis efficiency and electron transport rate, ultimately leading to death. Although the algicide structure of Y42 has not been identified, the algicidal activity seems to be similar with our changes in that it inhibits the photosynthesis and electron transport. In plant, microorganisms sometimes induce the ubiquitination-mediated protein degradation (<xref ref-type="bibr" rid="B81">Zeng et al., 2006</xref>). Ubiquitination system is important for developmental processes and responses to abiotic and biotic stresses. Uniquely at 12 h of co-culture, <italic>A catenella</italic> showed the upregulation in the transcriptome of the ubiquitin mediated proteolysis related genes. It suggests that <italic>A. catenella</italic> may utilize a defense system such as ubiquitination system against the algicidal bacterium <italic>Pseudoruegeria</italic> sp. similarly to plant-microbe interactions.</p>
<p>HABs caused by the dinoflagellate <italic>Alexandrium</italic> species are a major issue worldwide, and the phenomenon is being accelerated by increasing water temperatures and by the flow of excess nutrients from land into water bodies and oceans. To account for this, many marine bacteria showing algicidal effects have been recognized as a potential tool to control HABs (<xref ref-type="bibr" rid="B43">Kim et al., 1998</xref>; <xref ref-type="bibr" rid="B56">Mayali and Azam, 2004</xref>; <xref ref-type="bibr" rid="B82">Zhang et al., 2014a</xref>). Accordingly, the biotic relationships between HABs and algicidal bacteria are becoming more important. Hence, in this study, the algicidal mechanism through the metatranscriptome analysis was systematically analyzed between <italic>A. catenella</italic> and its algicidal bacterium <italic>Pseudoruegeria</italic> sp. Our time-course transcriptome analysis elucidates how <italic>A. catenella</italic> is affected by algicidal bacteria and how these bacteria obtain functional benefits through metabolic pathways.</p>
</sec>
<sec sec-type="data-availability" id="S5">
<title>Data Availability Statement</title>
<p>The sequencing datasets for this study are available under GenBank BioProject PRJNA604093. Biosample accession numbers for <italic>A. catenella</italic> and <italic>Pseudoruegeria</italic> sp. are <ext-link ext-link-type="DDBJ/EMBL/GenBank" xlink:href="SAMN13951753">SAMN13951753</ext-link> and <ext-link ext-link-type="DDBJ/EMBL/GenBank" xlink:href="SAMN15903161">SAMN15903161</ext-link>, respectively.</p>
</sec>
<sec id="S6">
<title>Author Contributions</title>
<p>SC, C-YA, and B-KC conceived, designed, and supervised the study. SC, S-RK, YJ, S-HC, EL, SJ, and B-SJ, performed the experiments. SC, YJ, S-HC, B-HO, H-MO, C-YA, and B-KC analyzed the data. SC and B-KC wrote the manuscript. All authors contributed to the article and approved the submitted version.</p>
</sec>
<sec sec-type="COI-statement" id="conf1">
<title>Conflict of Interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="disclaimer" id="S7">
<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 sec-type="funding-information" id="S8">
<title>Funding</title>
<p>This work was supported by the Basic Core Technology Development Program for the Oceans and the Polar Regions (2016M1A5A1027455 to SC, 2016M1A5A1027453 to C-YA, and 2016M1A5A1027458 to B-KC) through the National Research Foundation (NRF), funded by the Ministry of Science and ICT (MSIT).</p>
</sec>
<sec id="S9" 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.2021.728890/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2021.728890/full#supplementary-material</ext-link></p>
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