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<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Microbiol.</journal-id>
<journal-title>Frontiers in Microbiology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Microbiol.</abbrev-journal-title>
<issn pub-type="epub">1664-302X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fmicb.2021.637834</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Microbiology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Surface Topography, Bacterial Carrying Capacity, and the Prospect of Microbiome Manipulation in the Sea Anemone Coral Model Aiptasia</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Costa</surname> <given-names>R&#x00FA;ben M.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/368744/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>C&#x00E1;rdenas</surname> <given-names>Anny</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/446768/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Loussert-Fonta</surname> <given-names>C&#x00E9;line</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/673171/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Toullec</surname> <given-names>Ga&#x00EB;lle</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Meibom</surname> <given-names>Anders</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/400920/overview"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Voolstra</surname> <given-names>Christian R.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/117188/overview"/>
</contrib>
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<aff id="aff1"><sup>1</sup><institution>Division of Biological and Environmental Science and Engineering, Red Sea Research Center, King Abdullah University of Science and Technology</institution>, <addr-line>Thuwal</addr-line>, <country>Saudi Arabia</country></aff>
<aff id="aff2"><sup>2</sup><institution>Department of Biology, University of Konstanz</institution>, <addr-line>Konstanz</addr-line>, <country>Germany</country></aff>
<aff id="aff3"><sup>3</sup><institution>Laboratory for Biological Geochemistry, School of Architecture, Civil and Environmental Engineering, &#x00C9;cole Polytechnique F&#x00E9;d&#x00E9;rale de Lausanne</institution>, <addr-line>Lausanne</addr-line>, <country>Switzerland</country></aff>
<aff id="aff4"><sup>4</sup><institution>Center for Advanced Surface Analysis, Institute of Earth Sciences, University of Lausanne</institution>, <addr-line>Lausanne</addr-line>, <country>Switzerland</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Aram Mikaelyan, North Carolina State University, United States</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Brittany Leigh, Vanderbilt University, United States; Elizabeth Hambleton, University of Vienna, Austria</p></fn>
<corresp id="c001">&#x002A;Correspondence: Christian R. Voolstra, <email>chris.voolstra@gmail.com</email></corresp>
<fn fn-type="other" id="fn004"><p>This article was submitted to Microbial Symbioses, a section of the journal Frontiers in Microbiology</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>08</day>
<month>04</month>
<year>2021</year>
</pub-date>
<pub-date pub-type="collection">
<year>2021</year>
</pub-date>
<volume>12</volume>
<elocation-id>637834</elocation-id>
<history>
<date date-type="received">
<day>04</day>
<month>12</month>
<year>2020</year>
</date>
<date date-type="accepted">
<day>19</day>
<month>02</month>
<year>2021</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2021 Costa, C&#x00E1;rdenas, Loussert-Fonta, Toullec, Meibom and Voolstra.</copyright-statement>
<copyright-year>2021</copyright-year>
<copyright-holder>Costa, C&#x00E1;rdenas, Loussert-Fonta, Toullec, Meibom and Voolstra</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>Aiptasia is an emerging model organism to study cnidarian symbioses due to its taxonomic relatedness to other anthozoans such as stony corals and similarities of its microalgal and bacterial partners, complementing the existing <italic>Hydra</italic> (Hydrozoa) and <italic>Nematostella</italic> (Anthozoa) model systems. Despite the availability of studies characterizing the microbiomes of several natural Aiptasia populations and laboratory strains, knowledge on basic information, such as surface topography, bacterial carrying capacity, or the prospect of microbiome manipulation is lacking. Here we address these knowledge gaps. Our results show that the surface topographies of the model hydrozoan <italic>Hydra</italic> and anthozoans differ substantially, whereas the ultrastructural surface architecture of Aiptasia and stony corals is highly similar. Further, we determined a bacterial carrying capacity of &#x223C;10<sup>4</sup> and &#x223C;10<sup>5</sup> bacteria (i.e., colony forming units, CFUs) per polyp for aposymbiotic and symbiotic Aiptasia anemones, respectively, suggesting that the symbiotic status changes bacterial association/density. Microbiome transplants from <italic>Acropora humilis</italic> and <italic>Porites</italic> sp. to gnotobiotic Aiptasia showed that only a few foreign bacterial taxa were effective colonizers. Our results shed light on the putative difficulties of transplanting microbiomes between cnidarians in a manner that consistently changes microbial host association at large. At the same time, our study provides an avenue to identify bacterial taxa that exhibit broad ability to colonize different hosts as a starting point for cross-species microbiome manipulation. Our work is relevant in the context of microbial therapy (probiotics) and microbiome manipulation in corals and answers to the need of having cnidarian model systems to test the function of bacteria and their effect on holobiont biology. Taken together, we provide important foundation data to extend Aiptasia as a coral model for bacterial functional studies.</p>
</abstract>
<kwd-group>
<kwd>coral model system</kwd>
<kwd><italic>Exaiptasia diaphana</italic></kwd>
<kwd>metaorganism</kwd>
<kwd>holobiont</kwd>
<kwd>microbiome</kwd>
<kwd>symbiosis</kwd>
<kwd>gnotobiotic</kwd>
<kwd>axenic</kwd>
</kwd-group><counts>
<fig-count count="5"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="97"/>
<page-count count="16"/>
<word-count count="0"/>
</counts>
</article-meta>
</front>
<body>
<sec id="S1">
<title>Introduction</title>
<p>Corals constitute the foundation species of reef ecosystems that provide a habitat for about a third of all marine life (<xref ref-type="bibr" rid="B27">Fisher et al., 2015</xref>), but anthropogenic-driven climate change is now one of the main drivers of coral reef loss (<xref ref-type="bibr" rid="B45">Hughes et al., 2017b</xref>, <xref ref-type="bibr" rid="B42">2018a</xref>,<xref ref-type="bibr" rid="B43">b</xref>): about half of the Great Barrier Reef corals were lost over the last 30 years (<xref ref-type="bibr" rid="B23">Dietzel et al., 2020</xref>) and a 70&#x2013;99% coral reef decline is projected even under a 1.5&#x2013;2&#x00B0;C warming, one of the more benign climate change scenarios (<xref ref-type="bibr" rid="B4">Allen et al., 2018</xref>). Therefore, it is important to find solutions that can improve coral resilience and mitigate the negative effects of ongoing ocean warming, ocean acidification, and ocean deoxygenation (<xref ref-type="bibr" rid="B3">Allemand and Osborn, 2019</xref>; <xref ref-type="bibr" rid="B41">Hughes et al., 2020</xref>). Importantly, corals are cnidarian holobionts that consist of the coral animal host, intracellular microalgal symbionts (Symbiodiniaceae), and associated bacteria among many other organisms that all contribute to the stress tolerance and resilience of this metaorganism (<xref ref-type="bibr" rid="B73">Rohwer et al., 2002</xref>; <xref ref-type="bibr" rid="B75">Rosenberg et al., 2007</xref>; <xref ref-type="bibr" rid="B7">Bang et al., 2018</xref>; <xref ref-type="bibr" rid="B50">LaJeunesse et al., 2018</xref>; <xref ref-type="bibr" rid="B66">Pogoreutz et al., 2020</xref>; <xref ref-type="bibr" rid="B88">Voolstra and Ziegler, 2020</xref>). Besides the broad importance of Symbiodiniaceae, which reside within the coral cells and cover almost the entire energy needs of the coral host through provision of photosynthates (<xref ref-type="bibr" rid="B58">Muscatine, 1990</xref>; <xref ref-type="bibr" rid="B84">Trench, 1993</xref>), bacteria presumably play important roles in metabolism, immunity, and environmental adaptation of the coral host (<xref ref-type="bibr" rid="B97">Ziegler et al., 2017</xref>; <xref ref-type="bibr" rid="B96">Ziegler et al., 2019</xref>; <xref ref-type="bibr" rid="B69">Robbins et al., 2019</xref>; <xref ref-type="bibr" rid="B88">Voolstra and Ziegler, 2020</xref>). However, functional studies that detail the specific contributions of specific microbial taxa are still rare, partially due to methodological limitations (<xref ref-type="bibr" rid="B18">Cooke et al., 2019</xref>; <xref ref-type="bibr" rid="B69">Robbins et al., 2019</xref>). One suggested avenue to elucidate host-bacteria interactions in cnidarians is the use of model organisms, in particular using gnotobiotic (i.e., bearing few remaining known bacteria) or axenic (i.e., bacteria-/germ-free) host systems that allow controlled exposure or provision of cultured bacterial isolates (<xref ref-type="bibr" rid="B46">Jaspers et al., 2019</xref>).</p>
<p>Among Cnidarians, the hydrozoan <italic>Hydra</italic> is one of the few models where a germ-free (axenic) closed life cycle is available, which allows the detailed study of associated bacteria and the functions they contribute to the metaorganism, demonstrating the power of such systems to elucidate host-bacterial interactions (<xref ref-type="bibr" rid="B31">Fraune and Bosch, 2007</xref>; <xref ref-type="bibr" rid="B32">Fraune et al., 2009</xref>; <xref ref-type="bibr" rid="B30">Fraune et al., 2014</xref>; <xref ref-type="bibr" rid="B29">Franzenburg et al., 2013b</xref>; <xref ref-type="bibr" rid="B6">Augustin et al., 2017</xref>; <xref ref-type="bibr" rid="B91">Wein et al., 2018</xref>). Similarly, the anthozoan <italic>Nematostella vectensis</italic> is becoming established as a cnidarian model to study host-bacterial interactions (<xref ref-type="bibr" rid="B39">Har et al., 2015</xref>; <xref ref-type="bibr" rid="B24">Domin et al., 2018</xref>). However, both systems lack the ability to engage in symbioses with microalgal symbionts of the family Symbiodiniaceae (<xref ref-type="bibr" rid="B50">LaJeunesse et al., 2018</xref>). Therefore, they may not comprise an ideal model for corals, since association with Symbiodiniaceae affects bacterial assemblage (<xref ref-type="bibr" rid="B2">Ainsworth et al., 2015</xref>; <xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>; <xref ref-type="bibr" rid="B51">Lawson et al., 2018</xref>; <xref ref-type="bibr" rid="B52">Maire et al., 2021</xref>). To this end, the sea anemone Aiptasia is gaining increasing traction as a coral model due to harboring the same or similar Symbiodiniaceae as scleractinian corals, its simplicity of culturing and clonal propagation, and the fact that Aiptasia anemones can be kept indefinitely in symbiotic and aposymbiotic states (i.e., with and without their microalgal partners) (<xref ref-type="bibr" rid="B92">Weis et al., 2008</xref>; <xref ref-type="bibr" rid="B86">Voolstra, 2013</xref>), allowing to study the mechanistic underpinnings of the cnidarian-dinoflagellate symbiosis in detail (<xref ref-type="bibr" rid="B8">Baumgarten et al., 2015</xref>; <xref ref-type="bibr" rid="B11">Biquand et al., 2017</xref>; <xref ref-type="bibr" rid="B20">Cziesielski et al., 2018</xref>; <xref ref-type="bibr" rid="B67">R&#x00E4;decker et al., 2018</xref>; <xref ref-type="bibr" rid="B34">Gegner et al., 2019</xref>; <xref ref-type="bibr" rid="B83">Simona et al., 2019</xref>). Of note, the name Aiptasia refers to the colloquial model system name, given that different researchers across the world use different strains, and likely species (<xref ref-type="bibr" rid="B92">Weis et al., 2008</xref>; <xref ref-type="bibr" rid="B8">Baumgarten et al., 2015</xref>; <xref ref-type="bibr" rid="B62">Oakley et al., 2015</xref>; <xref ref-type="bibr" rid="B11">Biquand et al., 2017</xref>; <xref ref-type="bibr" rid="B25">Dungan et al., 2020</xref>). The current proposed species name <italic>is Exaiptasia diaphana</italic> (<xref ref-type="bibr" rid="B25">Dungan et al., 2020</xref>), previously <italic>Exaiptasia pallida</italic> (<xref ref-type="bibr" rid="B36">Grajales and Rodr&#x00ED;guez, 2014</xref>). Following the notion of Aiptasia as a model to study the coral-algal symbiosis (<xref ref-type="bibr" rid="B8">Baumgarten et al., 2015</xref>), its suitability as a model to study coral-bacterial interactions was suggested (<xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>). Studies that describe bacterial association of several wild-type and lab-cultured strains could show that (i) microbial assemblages of lab-cultured Aiptasia are comparable, (ii) bacterial associations are somewhat &#x201C;plastic&#x201D; pending environmental differences and association with or without algal symbionts, and (iii) an overall similarity in the taxonomic composition of microbiomes of corals and Aiptasia (<xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>; <xref ref-type="bibr" rid="B14">Brown et al., 2017</xref>; <xref ref-type="bibr" rid="B40">Herrera et al., 2017</xref>; <xref ref-type="bibr" rid="B25">Dungan et al., 2020</xref>). However, a detailed examination of the surface ectoderm topography, bacterial carrying capacity, and the prospect of microbiome manipulation (e.g., in the form of microbiome transplants) to highlight similarities to corals and demonstrate the efficacy of the Aiptasia system as a tool to study bacterial interactions was missing.</p>
<p>In the current work, our aim was to address these knowledge gaps and provide a foundation for Aiptasia to be used as a model for the study of coral-bacterial interactions. To do this, we characterized tissue surface topographies of Aiptasia and the <italic>Hydra</italic> and <italic>Nematostella</italic> cnidarian model systems and subsequently compared them to three scleractinian corals, in the context of the surface ectoderm as a bacterial habitat. In addition, we determined the bacterial carrying capacity in symbiotic and aposymbiotic Aiptasia anemones as a frame of comparison to reef-building corals and to provide a scale of reference for sequencing-based bacterial community studies. Last, using bacteria-depleted sea anemones, we conducted microbiome transplant experiments using coral microbiomes to assess the suitability of this method as a tool to study function of coral-associated bacteria and as a means to assess the ability of changing microbial host association to aid environmental adaptation of coral holobionts.</p>
</sec>
<sec id="S2" sec-type="materials|methods">
<title>Materials and Methods</title>
<sec id="S2.SS1">
<title>Animal Rearing</title>
<p>Aposymbiotic and symbiotic Aiptasia of the clonal strain CC7 were generated and reared as described previously (<xref ref-type="bibr" rid="B8">Baumgarten et al., 2015</xref>) with some modifications. Aposymbiotic animals were generated through repeated 4 h cold&#x2212;shocks at 4&#x00B0;C and treatment with 50 &#x03BC;M of the photosynthetic inhibitor diuron (Sigma&#x2212;Aldrich, United States). Aposymbiotic animals were maintained in the dark for &#x003E;3 years and are routinely inspected by fluorescence microscopy (Leica DMI3000 B) to confirm the absence of Symbiodiniaceae. Symbiotic anemones were generated by infecting aposymbiotic animals with strain SSB01 (<italic>Breviolum minutum</italic>, former Clade B) (<xref ref-type="bibr" rid="B94">Xiang et al., 2013</xref>). Of note, the algal symbiont strain SSB01 is not the native symbiont of Aiptasia CC7 but has been previously used as a stable and characterized Aiptasia host-algal symbiont combination (<xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>; <xref ref-type="bibr" rid="B93">Wolfowicz et al., 2016</xref>; <xref ref-type="bibr" rid="B83">Simona et al., 2019</xref>). To obtain symbiotic CC7-SSB01 Aiptasia, individual anemones were exposed to 10<sup>5</sup> Symbiodiniaceae cells/ml for 24 h, fed with <italic>Artemia</italic> nauplii after 48 h, and seawater was exchanged thereafter. All Aiptasia anemones were kept in autoclaved natural seawater and reared in 1 L tanks at a 12 h:12 h light:dark cycle at 20&#x2013;40 &#x03BC;mol photons m<sup>2</sup> s<sup>1</sup> of photosynthetically active radiation at 25&#x00B0;C in an I-36LLVL incubator (Percival Scientific Inc., United States). <italic>Nematostella vectensis</italic> polyps were reared in half liter tanks in half strength artificial seawater at room temperature. Polyps of <italic>Hydra magnipapillata</italic> strain 105 were reared in half liter tanks in commercial spring water at room temperature. <italic>Nematostella</italic> and <italic>Hydra</italic> animals were fed <italic>Artemia</italic> nauplii twice a week.</p>
</sec>
<sec id="S2.SS2">
<title>Ectoderm Surface Analysis Using Electron Microscopy</title>
<p>We compared ectoderm surface topography of different cnidarian classes, namely Anthozoa (corals, Aiptasia, <italic>Nematostella vectensis</italic>) with Hydrozoa (<italic>Hydra magnipapillata</italic>), using Scanning Electron Microscopy (SEM). Coral colony fragments of <italic>Stylophora pistillata</italic>, <italic>Acropora humilis</italic>, and <italic>Porites</italic> sp. were collected from the central Red Sea at 6 m depth at the Al Fahal forereef (22&#x00B0;15.100&#x2032;N, 38&#x00B0;57.386&#x2032;E) by SCUBA and maintained in an open water aquaria system until use (CMOR, KAUST), whereas Aiptasia, <italic>N. vectensis</italic>, and <italic>H. magnipapillata</italic> animals were available from cultured lab strains. Three fragments (in the case of corals) or three polyps (in the case of Aiptasia, <italic>Nematostella</italic>, <italic>Hydra</italic>) were transferred to 24-well plates for processing. Coral fragments and model system cnidarians were left to expand in &#x223C;2% magnesium chloride in artificial seawater (ASW) or fresh water for <italic>Hydra</italic>, or half strength ASW for <italic>Nematostella</italic> for 15 min, respectively. After that, specimens were fixed in &#x223C;2.5% glutaraldehyde in 0.1 M cacodylate buffer at 4&#x00B0;C overnight. Samples were then washed in 0.1 M cacodylate buffer (pH 7.2&#x2013;7.4) thrice for 15 min each and post fixed in 1% osmium tetroxide solution in 0.1 M cacodylate buffer for 1 h in the dark. Samples were further washed thrice in ddH2O for 15 min each and proceeded for dehydration in an EtOH gradient: 30, 50, 70, 90, and 100%, 15 min each step, with two final incubations in 100% EtOH, also for 15 min. The drying process was initiated by transferring the samples to a 1:2 solution of hexamethyldisilazane (HMDS):100% EtOH (v/v) for 20 min, then to a fresh solution of 2:1 HMDS:100% EtOH for 20 min, 100% HMDS for 20 min, and a final incubation in 100% HMDS. Samples were left to dry loosely covered in the chemical hood for the HMDS to slowly evaporate overnight. Each fragment was then mounted on an SEM specimen mount head pin and sputter coated with 4 nm of platinum/palladium or Iridium. All samples were imaged using a Teneo Volume Scope electron microscope (FEI, United States) operating at 1&#x2013;3 kV.</p>
<p>Complementary to the SEM analyses, we imaged Aiptasia specimens by Transmission Electron Microscopy (TEM). Briefly, Aiptasia polyps were fixed in 2.5% glutaraldehyde in 0.1 M cacodylate buffer (pH 7.4) for 12 h at 4&#x00B0;C and post fixed with 1% osmium tetroxide in 0.1 M cacodylate buffer for 1 h in the dark at 4&#x00B0;C. After three washes in ddH2O, the sample blocks were dehydrated through EtOH and acetone, infiltrated with a mixture of epoxy resin (Electron Microscopy Sciences, United States) and acetone, followed by a final embedding in pure resin. A Leica EM UC6 Ultramicrotome (Leica Microsystems, Germany) was used to cut 150 nm thin sections from the resin block. Finally, thin sections were collected on a 200 mesh copper grid, stained with 1% uranyl acetate (Electron Microscopy Sciences, United States) and Reynold&#x2019;s lead citrate (Electron Microscopy Sciences, United States). Images were acquired using a Titan CT transmission electron microscope (Thermo Fisher Scientific, United States) operating at 300 kV.</p>
<p>To investigate the presence of bacteria inside the mucus layer using TEM, we modified the standard resin embedding protocol by introducing an agarose embedding step with subsequent cryosectioning of the specimens. Aiptasia anemones were prepared as follows: Individual polyps were chemically fixed in phosphate buffer (0.1 M pH 7.4) with 9% sucrose, containing 4% formaldehyde and 2.5% glutaraldehyde. Fixation was done at room temperature for 2 h after which samples were embedded in 4% aqueous agarose to ease the manipulation. Then, polyps were cut into &#x223C;4 mm<sup>3</sup> pieces and post stained in 2% osmium aqueous solution for 1 h in the dark. After rinsing in water, samples were dehydrated in a series of ethanol concentrations, ranging from 10 to 100%, then infiltrated with EPON resin (Electron Microscopy Sciences, United States), before polymerization at 60&#x00B0;C for 48 h. Thin sections of 80 nm were cut and mounted onto a Formvar film-coated, carbon-stabilized 100 mesh copper finder grid (Electron Microscopy Sciences, United States). Sections were post stained with UranyLess (Electron Microscopy Sciences, United States) and lead citrate (Electron Microscopy Sciences, United States) before being imaged with a Tecnai-12 transmission electron microscope (Thermo Fisher Scientific, United States) operating at 100 kV with a FEI eagle camera (Thermo Fisher Scientific, United States) using TIA software (Thermo Fisher Scientific, United States). Contrast, brightness, and sharpness of acquired images were adjusted using Adobe Photoshop.</p>
</sec>
<sec id="S2.SS3">
<title>Generation of Gnotobiotic Aiptasia</title>
<p>Bacteria-depleted Aiptasia polyps were generated using a previously developed protocol consisting of a depletion priming step, followed by an antibiotic treatment, and subsequent recovery from the antibiotic cocktail (<xref ref-type="bibr" rid="B19">Costa et al., 2019</xref>). For the depletion priming step, polyps were transferred to 500 ml plastic tanks, reared in 0.22 &#x03BC;m filtered ASW (same light and temperature regime as described above) and fed with sterile decapsulated <italic>Artemia</italic> nauplii for 4 weeks. For the antibiotic treatment, anemones were transferred to petri dishes and washed repeatedly with ASW individually and incubated in antibiotic solution (50 &#x03BC;g/ml of Carbenicillin, Chloramphenicol, Rifampicin, and Nalidixic acid in ASW) for 15 min. Polyps were then transferred to 24-well tissue culture plates (Corning Costar, United States), one polyp per well, under sterile conditions, and incubated with antibiotic solution for 7 days, with daily media exchange, at a 12 h:12 h light/dark cycle in an incubator (20&#x2013;40 &#x03BC;mol photons m<sup>&#x2013;2</sup> s<sup>&#x2013;1</sup> of photosynthetically active radiation) at 25&#x00B0;C. After 7 days, anemones were given 24 h for recovery in ASW before microbiome inoculation (see below). Effective bacterial depletion using this protocol was validated using culture-dependent and -independent techniques (<xref ref-type="bibr" rid="B19">Costa et al., 2019</xref>): bacterial depletion of treated Aiptasia polyps was confirmed by absence of colony forming units (CFUs) after plating anemone lysates on Marine Agar and subsequent incubation for at least 5 days. In addition, DNA extracted using the DNeasy Blood &#x0026; Tissue Kit (Qiagen, Germany) from treated Aiptasia anemone lysates were used for PCR amplification of the 16S rRNA gene (95&#x00B0;C for 15 min, followed by 30 cycles of 30 s at 95&#x00B0;C, 90 s at 55&#x00B0;C, and 90 s at 72&#x00B0;C, followed by a final extension for 10 min at 72&#x00B0;C using the 16S universal primer pair 27F-1492R) and subsequent confirmation of absence of a PCR product by means of electrophoresis on an agarose gel.</p>
</sec>
<sec id="S2.SS4">
<title>Microbial Carrying Capacity</title>
<p>We determined microbial carrying capacity of apo- and symbiotic control Aiptasia polyps (i.e., untreated) as well as of anemones after antibiotic treatment and microbiome transplants. To do this, single polyps from all experimental conditions were placed in 1.5 ml tubes under sterile conditions and 300 &#x03BC;l of ASW were added before the polyps were lysed using a motorized pestle and mortar. Animal lysates and ASW (negative control) were diluted 10-, 100-, and 1000-fold, and 50 &#x03BC;l were plated on Marine Agar (Difco Marine Agar 2216, BD Biosciences, United States) and incubated at 25&#x00B0;C for 24&#x2013;48 h or 5 days in the case of antibiotic treated anemones, with subsequent counting of bacterial colonies. For statistical analysis, colony counts were log-transformed, normality was tested using the Shapiro&#x2013;Wilk test, and a one-way ANOVA was conducted. In case of statistical significance, a Dunnett <italic>post hoc</italic> test was conducted. An unpaired <italic>t</italic>-test was used to assess for significant differences between aposymbiotic and symbiotic control conditions. In order to account for putative polyp size differences, CFU counts per polyp were normalized to the host total protein for each polyp, determined using a Micro BCA protein assay kit (Pierce, United States), and the same statistical analysis as above was conducted.</p>
</sec>
<sec id="S2.SS5">
<title>Microbiome Inocula</title>
<p>Fragments of <italic>Acropora humilis</italic> and <italic>Porites sp.</italic> were collected from the nearshore reef Tahala (22&#x00B0;15.7812&#x2032;N, 39&#x00B0;3.099&#x2032;E) (central Red Sea, Saudi Arabia) and processed on the same day. Fragments from three colonies per coral species were collected and combined prior to inoculation (see below). Each coral fragment was placed in a sterile Ziploc bag with 10 ml of ASW, and coral tissue was air blasted off the skeleton using a sterile 1 ml barrier tip inserted to a rubber hose connected to a bench air-pressure outlet. The slurry obtained from fragments from a given coral species were combined and transferred to a 50 ml polypropylene tube and the volume was adjusted to 50 ml with ASW to reduce viscosity. The slurry was homogenized for 30 s using an Ultra Turrax T18 homogenizer (IKA, Germany) and split in 25 ml preparations per tube. Control inocula were prepared using between 10 and 15 apo- and symbiotic Aiptasia polyps, respectively, in 30 ml of ASW, homogenized as described above, and homogenized a second time with a MicroDisTec homogenizer 125 (Thermo Fisher Scientific, United States) to ensure complete maceration. The final volume of the lysate was adjusted to 50 ml with ASW and split in 25 ml preparations.</p>
<p>Microbiome inocula were further processed in a biosafety cabinet, using sterile work practices. Lysates were centrifuged using a swing-bucket rotor at 500 <italic>g</italic> for 5 min to pellet zooxanthellae. The supernatant was collected and an aliquot was taken for visual inspection on an inverted epifluorescence microscope. All lysates were centrifuged once, except for the <italic>Porites</italic> sp. inoculum, which had one extra centrifugation step to completely remove visible traces of the zooxanthellae. The supernatants were pooled for each inoculum type and centrifuged at 3220 <italic>g</italic> for 30 min to pellet bacteria. The resulting pellet was resuspended in 25 ml of ASW and centrifuged twice. Pellets were resuspended in 15 ml of ASW and a 1 ml aliquot was set aside for quantification of bacteria.</p>
<p>Bacteria were quantified using BacLight Red Bacterial stain (Thermo Fisher Scientific, United States). Aliquots from each inoculum were stained using 1 &#x03BC;M of dye for 10 min and counted using a BD FACSCanto II flow cytometer (BD Biosciences, United States). Gates for bacterial counts were first defined using 1 &#x03BC;m and 2 &#x03BC;m reference beads (Thermo Fisher Scientific, United States) in forward scatter (FSC) vs. side scatter (SSC) and then by using Aiptasia bacterial cultures stained with BacLight Red and acquired in the PerCP-PI channel. Bacterial numbers were calculated after gravimetric calibration of the flow rates and using the positive events acquired using the defined gating strategy. Based on determined counts, inocula were diluted to 5 &#x00D7; 10<sup>5</sup> bacterial cells/ml and 1 ml was used per polyp. In parallel to the flow cytometry-based bacterial counts, an aliquot of all final inocula was plated on Marine Agar (Difco Marine Agar 2216, BD Biosciences, United States) for CFU counts. Bacterial densities of inocula are provided in <xref ref-type="supplementary-material" rid="TS1">Supplementary Table 1</xref>.</p>
</sec>
<sec id="S2.SS6">
<title>Microbiome Transplants</title>
<p>For the microbiome transplants, we assessed 30 apo- and symbiotic anemones each across five experimental conditions using six biological replicates (60 anemones in total). Experimental conditions were as follows: (1) untreated control anemones from rearing tanks (APO and SYM), (2) gnotobiotic anemones after 1 day of recovery from antibiotic treatment (APO_AB and SYM_AB), (3) <italic>Acropora</italic> microbiome inoculum (APO+ACRinoc and SYM+ACRinoc), (4) <italic>Porites</italic> microbiome inoculum (APO+PORinoc and SYM+PORinoc), (5) Aiptasia microbiome inoculum (APO+APOinoc and SYM+SYMinoc). Anemones were kept in 24-well plates, 1 polyp per well, and gnotobiotic anemones were inoculated by adding 1 ml of the respective microbiome inoculum to the well (final volume of 1 ml, 5 &#x00D7; 10<sup>5</sup> bacterial cells/ml) and subsequent incubation for 3 days. After that, anemones were washed twice with ASW and kept in ASW for 4 additional days before being collected (7 days after microbiome transplantation).</p>
</sec>
<sec id="S2.SS7">
<title>RNA Isolation, cDNA Synthesis, and 16S rRNA Amplicon Sequencing</title>
<p>RNA-based 16S rRNA amplicon sequencing was conducted on five biological replicates from each experimental condition and symbiotic state of the microbiome transplant experiment (see above), in addition to no template DNA extraction and no template PCR negative controls. For RNA isolation, the Qiagen AllPrep DNA/RNA kit (Qiagen, Germany) was used. Briefly, 600 &#x03BC;l of RLT Plus buffer were added to 150 &#x03BC;l of fresh lysate (or artificial seawater for the negative control) followed by snap freezing of the tubes in liquid nitrogen and storage at &#x2212;80&#x00B0;C until extraction, following the manufacturer&#x2019;s instructions. RNA quantity and integrity were determined using Qubit (Thermo Fisher Scientific, United States) and BioAnalyzer (Agilent Technologies, United States), respectively. Total RNA was DNase-treated prior to reverse-transcription using the SuperScript First-Strand Synthesis System (Invitrogen, United States), according to the manufacturer&#x2019;s instructions. For amplification of 16S rRNA amplicons from cDNA, the primers 784F and 1061R (<xref ref-type="bibr" rid="B5">Andersson et al., 2008</xref>; <xref ref-type="bibr" rid="B9">Bayer et al., 2013</xref>) with MiSeq 16S adapter sequences were used (forward: 5&#x2032;-<underline>TCGTCGGCAGCGTCAGATGTGTATAAGAGACAG</underline>AGGA TTAGATACCCTGGTA-3&#x2032;; reverse: 5&#x2032;-<underline>GTCTCGTGGGCTCGG</underline> <underline>A&#x2006;GA&#x2006;TGT&#x2006;GTA&#x2006;TA&#x2006;AG&#x2006;A&#x2006;G&#x2006;A&#x2006;C&#x2006;A&#x2006;G</underline>&#x2006;CR&#x2006;R&#x2006;C&#x2006;A&#x2006;C&#x2006;GA&#x2006;G&#x2006;CTGACGAC&#x2006;-3&#x2032;; Illumina overhang adaptor sequences are underlined). PCR reactions were performed in triplicate using the Qiagen Multiplex PCR kit (Qiagen, Germany) with 2 &#x03BC;l of cDNA and a primer concentration of 0.5 &#x03BC;M in a reaction volume of 20 &#x03BC;L. PCRs were performed as follows: 1 cycle at 95&#x00B0;C for 15 min, 27 cycles each at 95&#x00B0;C for 30 s, 55&#x00B0;C for 90 s, and 72&#x00B0;C for 30 s, followed by a final extension step at 72&#x00B0;C for 10 min. Triplicate PCRs for each sample were pooled and cleaned with Illustra ExoProStar (GE Healthcare, United States). Samples were subsequently indexed (eight PCR cycles) using Nextera XT barcode sequencing adapters (Illumina, United States). Indexed PCR products were normalized using Invitrogen SequalPrep normalization plates (Thermo Fisher Scientific, United States) and pooled in equimolar ratios. Pooled samples were checked for the presence of primer dimers on a BioAnalyzer (Agilent Technologies, United States) before sequencing. The library was sequenced at the KAUST Bioscience Core Lab using 2 &#x00D7; 300 bp at 6 pM with 20% phiX on the Illumina MiSeq (version 3 chemistry) according to the manufacturer&#x2019;s specifications.</p>
</sec>
<sec id="S2.SS8">
<title>16S rRNA Amplicon Analysis</title>
<p>Sequence reads were demultiplexed and adapters and barcodes were removed. Resulting sequences were then processed using mothur v.1.39.5 (<xref ref-type="bibr" rid="B80">Schloss et al., 2009</xref>). Briefly, paired-end sequences were assembled using the &#x201C;make.contigs&#x201D; command, subsequently trimmed to exclude sequences &#x003C;200 bp, and rare sequences (appearing once across the entire sequencing dataset) were removed. The remaining sequences were then aligned to the SILVA database (version 132) using &#x201C;align.seqs,&#x201D; then pre-clustered allowing a 2 nt difference, and finally chimeric sequences were removed using VSEARCH (<xref ref-type="bibr" rid="B72">Rognes et al., 2016</xref>). Taxonomical classification was done using the Greengenes (release gg_13_5_99, May 2013) and SILVA (release 138, December 2016) databases. Eukaryotic, archaeal, mitochondrial, and chloroplast sequences were removed prior to OTU clustering using a 97% similarity cutoff. Putative contaminants were determined based on their abundance in negative controls and removed from all samples. An OTU was considered a contaminant if: [&#x03A3; relative abundance OTU<sub><italic>i</italic></sub> in negative controls]/[&#x03A3; relative abundance OTU<sub><italic>i</italic></sub> in all samples] &#x003E; 0.1. Beta diversity was examined via principal coordinate analysis (PCoA) of Bray-Curtis dissimilarity distances of log<sub>10</sub>(x + 1) OTU abundances (<xref ref-type="supplementary-material" rid="DS1">Supplementary Data 1</xref>) using the <italic>phyloseq</italic> package (<xref ref-type="bibr" rid="B57">McMurdie and Holmes, 2013</xref>). A permutational multivariate analysis of variance (PERMANOVA) was carried out using the &#x201C;adonis&#x201D; function on dissimilarity Bray-Curtis distances of relative OTU abundances to test for differences between conditions and across symbiotic states. Pairwise PERMANOVA tests were conducted using an R wrapper function for multilevel pairwise comparisons (<xref ref-type="bibr" rid="B53">Martinez Arbizu, 2019</xref>). To determine overlap of bacterial taxa across microbiome transplants, we determined OTUs that were present across all samples for a given experimental treatment (i.e., APO, APO+APOinoc, ACR+ACRinoc, APO+PORinoc, SYM, SYM+SYMinoc, SYM+ACRinoc, and SYM+PORinoc) and overlapping taxa were represented using the package <italic>VennDiagram</italic> (<xref ref-type="bibr" rid="B17">Chen and Boutros, 2011</xref>).</p>
</sec>
</sec>
<sec id="S3">
<title>Results</title>
<sec id="S3.SS1">
<title>Distinct Ectoderm Surface Topographies Across Cnidarians</title>
<p>We compared surface topographies using scanning electron microscopy (SEM) of three model system cnidarians (<italic>Hydra</italic>, <italic>Nematostella</italic>, and Aiptasia) and three coral species (<italic>Stylophora pistillata</italic>, <italic>Acropora humilis</italic>, <italic>Porites</italic> sp.) as a first proxy to determine microbial association (<xref ref-type="fig" rid="F1">Figure 1</xref>). The ectodermal epithelium of the hydrozoan <italic>Hydra</italic> was composed of a smooth surface with few cilia (i.e., 5&#x2013;10 &#x03BC;m long hair-like plasma membrane projections, made of microtubules in a 9 + 2 ultrastructure arrangement) (<xref ref-type="fig" rid="F1">Figure 1A</xref>). By comparison, <italic>Hydra</italic> tentacles showed increased ciliation (and a higher density of villi), coinciding with increased mucus and detritus retention, but also exhibited smooth(er) tissue patches scattered across the tentacles, where some bacteria were found to be attached (<xref ref-type="fig" rid="F1">Figure 1B</xref>). The ectodermal epithelium surfaces of column and tentacle of <italic>N. vectensis</italic> and Aiptasia were highly similar (<xref ref-type="fig" rid="F1">Figures 1C&#x2013;F</xref>). We observed extensive villi (i.e., smaller, numerous plasma membrane projections, lacking microtubules) coverage in the body column of both polyps, with villi protruding from ectodermal cells ranging between 1 and 2 &#x03BC;m in length (<xref ref-type="fig" rid="F1">Figures 1C,E</xref>) and bigger cilia ranging from 4 to 6 &#x03BC;m in the tentacle region (<xref ref-type="fig" rid="F1">Figures 1D,F</xref>). In contrast to <italic>Hydra</italic>, we did not detect any bacteria on the column surface or tentacle regions. This suggests two things: (1) bacteria are rather rare on the surface ectoderm and may be largely constrained to the surface mucus layer in anthozoans, and (2) bacteria may be more abundant on the surface ectoderm in the hydrozoan <italic>Hydra</italic> than in anthozoans. This is corroborated by a complementary TEM analysis of the Aiptasia ectoderm, showing bacteria above the ciliary/villi band, inside the electron dense mucus layer (<xref ref-type="fig" rid="F2">Figure 2</xref> and <xref ref-type="supplementary-material" rid="FS1">Supplementary Figure 1</xref>). The preserved surface mucus layer was estimated around 5&#x2013;15 &#x03BC;m, extending beyond the villi. Of further note, the surface ectoderms of apo- and symbiotic Aiptasia were indiscriminate (<xref ref-type="supplementary-material" rid="FS1">Supplementary Figure 2</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption><p>Ultrastructural comparison of the surface topography of <italic>Hydra</italic> and Anthozoans. Representative scanning electron microscopy (SEM) images of three model cnidarians <bold>(A&#x2013;F)</bold> and three reef building corals <bold>(G&#x2013;L)</bold> show differences between the hydrozoan <italic>Hydra</italic> and anthozoans, but an overall similar topography across anthozoans. <bold>(A,B)</bold> <italic>Hydra</italic> column and tentacle surface topography. <bold>(C,D)</bold> <italic>Nematostella</italic> column and tentacle surface topography. <bold>(E,F)</bold> Aposymbiotic Aiptasia column and tentacle surface topography. <bold>(G,H)</bold> <italic>Stylophora pistillata</italic> coenenchyme and tentacle. <bold>(I,J)</bold> <italic>Acropora humilis</italic> coenenchyme and tentacle. Noticeable are the discharged cnidocysts in the tentacle. <bold>(K,L)</bold> <italic>Porites</italic> sp. coenenchyme and fouled surface topography. Note the presence of microeukaryotes trapped in the fouled region, to which bacteria seem attached. Dashed line boxes denote regions where bacteria can be seen (black asterisks). Black arrows denote mechanoreceptor bundles. Scale bars: <bold>(A&#x2013;K)</bold>: 10 &#x03BC;m; <bold>(L)</bold>: 100 &#x03BC;m; boxes in <bold>(B,F,L)</bold>: 5 &#x03BC;m.</p></caption>
<graphic xlink:href="fmicb-12-637834-g001.tif"/>
</fig>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption><p>Cross section of the surface ectoderm of Aiptasia. Representative transmission electron microscopy (TEM) micrograph of Aiptasia shows the villi coverage on the epidermis and the interspace between villi and the surface mucus layer (SML), where a bacterium can be identified. b, bacterium; c, cilia; cn, cnidocyte; ec, ectoderm; is, Ectoderm-mucus interspace; mt, mitochondria; n, nucleus; sml, surface mucus layer; v, villus. Scale bar- 1 &#x03BC;m.</p></caption>
<graphic xlink:href="fmicb-12-637834-g002.tif"/>
</fig>
<p>We also analyzed the ectodermal epithelium topography of the tentacles and coenenchyme (i.e., coral tissue between the polyps) of the three scleractinian corals <italic>Stylophora pistillata</italic>, <italic>Acropora humilis</italic>, and <italic>Porites</italic> sp. (<xref ref-type="fig" rid="F1">Figures 1G&#x2013;I</xref>). We observed extensive villi coverage with longer cilia ranging from 4 to 6 &#x03BC;m extending from the epidermis in all corals. Surface topographies were similar to <italic>N. vectensis</italic> and Aiptasia, but distinct from <italic>Hydra</italic>. In the case of <italic>Porites</italic> sp., a thick mucus sheet was visible on top of the coenenchyme, intercalated with fouled areas (<xref ref-type="supplementary-material" rid="FS1">Supplementary Figure 3</xref>). Further, the surface mucus layer of <italic>Porites</italic> sp. seemed distinct from <italic>S. pistillata</italic> and <italic>A. humilis</italic>, creating a more compact mucus sheet that persisted chemical fixation and several washing steps. Such sheet-like mucus appearances are described for <italic>Porites compressa</italic>, as well as the observation of the presence of fouled regions (<xref ref-type="bibr" rid="B47">Johnston and Rohwer, 2007</xref>). Contrary to the coral surface ectoderm that seemed devoid of bacteria, many bacteria were found attached to the smooth epithelial surfaces of other eukaryotes that aggregated in fouled regions of <italic>Porites</italic> sp. (<xref ref-type="fig" rid="F1">Figure 1L</xref>), corroborating the notion that the ciliated surface of anthozoans plays a role in preventing bacterial adhesion.</p>
</sec>
<sec id="S3.SS2">
<title>Distinct Bacterial Carrying Capacity of Apo- and Symbiotic Aiptasia</title>
<p>To determine the putative carrying capacity of Aiptasia anemones, we obtained CFU counts from apo- and symbiotic control anemones that were subsequently compared to the different experimental conditions, i.e., antibiotic treated and microbiome inoculated animals (<xref ref-type="fig" rid="F3">Figure 3</xref> and <xref ref-type="supplementary-material" rid="TS1">Supplementary Tables 2</xref>, <xref ref-type="supplementary-material" rid="TS1">3</xref>). The average carrying capacity of aposymbiotic Aiptasia anemones was determined as 4.25 &#x00D7; 10<sup>4</sup> CFUs/polyp (control animals). When normalized to protein biomass, we obtained 1.59 &#x00D7; 10<sup>5</sup> CFUs/mg host protein. The carrying capacity of symbiotic anemones was estimated at 2.02 &#x00D7; 10<sup>5</sup> CFUs/polyp and 1.10 &#x00D7; 10<sup>6</sup> CFUs/mg host protein, respectively (control animals). Thus, the number of CFUs was higher in symbiotic polyps by about an order of magnitude compared to aposymbiotic polyps (unpaired <italic>t</italic>-test, <italic>P</italic> = 0.025, <xref ref-type="supplementary-material" rid="TS1">Supplementary Table 4</xref>). We did not obtain CFUs from antibiotic-treated anemones, confirming successful bacterial depletion (<xref ref-type="fig" rid="F3">Figure 3B</xref>). Interestingly, in some cases (re-)infection of gnotobiotic Aiptasia with microbiome inocula of either aposymbiotic Aiptasia or corals increased the carrying capacity of aposymbiotic animals. For instance, aposymbiotic anemones exposed to <italic>Porites</italic> sp. inoculum exhibited a significant increase in CFU counts to an average of 1.85 &#x00D7; 10<sup>5</sup> CFUs/polyp (Dunnett&#x2019;s test <italic>P</italic> &#x003C; 0.05, <xref ref-type="fig" rid="F3">Figure 3B</xref> and <xref ref-type="supplementary-material" rid="TS1">Supplementary Tables 2</xref>, <xref ref-type="supplementary-material" rid="TS1">4</xref>). Conversely, inoculation of symbiotic anemones (SYM+ACRinoc and SYM+PORinoc) did not result in a significant increase in CFU counts (Dunnett&#x2019;s test <italic>P</italic> &#x003E; 0.3, <xref ref-type="fig" rid="F3">Figure 3B</xref> and <xref ref-type="supplementary-material" rid="TS1">Supplementary Tables 2</xref>, <xref ref-type="supplementary-material" rid="TS1">4</xref>). Overall, the carrying capacity of Aiptasia polyps with &#x223C;5 mm of oral disk was between 10<sup>4</sup> and 10<sup>5</sup> CFUs for apo- and symbiotic anemones, respectively. After microbiome inoculation the carrying capacity was at about 10<sup>5</sup> CFUs/polyp, irrespective of the symbiotic condition.</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption><p>Gnotobiotic Aiptasia, microbiome transplants, and carrying capacity of Aiptasia sea anemones. <bold>(A)</bold> Overview of the microbiome transplant experiment. Anemones underwent antibiotic treatment for 7 days, followed by a 1-day recovery. Animals were then inoculated with preparations of <italic>Acropora humilis</italic>, <italic>Porites</italic> sp., and Aiptasia microbiomes for 3 days, after which inocula were removed (water exchange) and animals were incubated for 4 additional days (total of 7 days). Dotted vertical lines denote a change in the external environment. <bold>(B)</bold> Carrying capacity of Aiptasia sea anemones. CFU counts were determined across all experimental conditions and for apo- <bold>(left)</bold> and symbiotic <bold>(right)</bold> anemones separately. Depicted is the mean and standard error for the respective experimental condition (&#x002A;<italic>P</italic> &#x2264; 0.05; &#x002A;&#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.0001). APO/SYM, apo- and symbiotic control anemones; APO_AB/SYM_AB, 7-day antibiotic-treated anemones with a subsequent 1-day recovery; APO+APOinoc, APO microbiome transplantation after antibiotic treatment; SYM+SYMinoc, SYM microbiome transplantation after antibiotic treatment; APO/SYM+ACRinoc, <italic>Acropora humilis</italic> microbiome transplantation after antibiotic treatment (7 days after inoculation); APO/SYM+PORinoc, <italic>Porites</italic> sp. microbiome transplantation after antibiotic treatment (7 days after inoculation).</p></caption>
<graphic xlink:href="fmicb-12-637834-g003.tif"/>
</fig>
</sec>
<sec id="S3.SS3">
<title>Bacterial Community Composition of Native and Inoculated Aiptasia</title>
<p>We employed RNA-based 16S amplicon sequencing to assess active bacterial community composition and dynamics (in contrast to the resident community based on DNA-based 16S sequencing) associated with Aiptasia under the various experimental treatments (<xref ref-type="fig" rid="F4">Figure 4</xref>). Bacterial community composition differed significantly between treatments (PERMANOVA, <italic>P</italic> = 0.001) (<xref ref-type="supplementary-material" rid="TS1">Supplementary Table 5</xref>). As previously reported based on DNA-based 16S marker gene sequencing (<xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>), bacterial communities of apo- and symbiotic Aiptasia anemones were different (PERMANOVA, <italic>P</italic> = 0.015, <xref ref-type="fig" rid="F4">Figure 4B</xref>). For this reason, we clustered apo- and symbiotic samples separate to resolve differences within apo- and symbiotic groups as a result of the treatments (<xref ref-type="fig" rid="F4">Figure 4A</xref>). For both groups, antibiotic-treated anemones (APO_AB and SYM_AB) were clearly separated from control anemones (APO and SYM) and both were different from gnotobiotic anemones re-inoculated with microbial communities (with the exception of SYM+SYMinoc that closely clustered with SYM anemones) (<xref ref-type="fig" rid="F4">Figure 4A</xref>).</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption><p>Bacterial community composition and dynamics of Aiptasia polyps 7 days after microbiome transplantation. <bold>(A)</bold> Principal Coordinate Analysis (PCoA) based on Bray-Curtis distances of OTU log<sub>10</sub>(x + 1)-transformed abundances. <bold>(B)</bold> 16S rRNA amplicon-based active bacterial community composition at the OTU level. Depicted are the 20 most abundant (i.e., active) OTUs across all samples (refer to <xref ref-type="fig" rid="F3">Figure 3A</xref> for an overview over time points sampled). Remaining OTUs are grouped as &#x201C;Others.&#x201D; APO/SYM, apo- and symbiotic control anemones; APO_AB/SYM_AB, 7-day antibiotic-treated anemones with a subsequent 1-day recovery; APO+APOinoc, APO microbiome inoculation after antibiotic treatment; SYM+SYMinoc, SYM microbiome inoculation after antibiotic treatment; APO/SYM+ACRinoc, <italic>Acropora humilis</italic> microbiome inoculation after antibiotic treatment (7 days after inoculation); APO/SYM+PORinoc, <italic>Porites</italic> sp. microbiome inoculation after antibiotic treatment (7 days after inoculation).</p></caption>
<graphic xlink:href="fmicb-12-637834-g004.tif"/>
</fig>
<p>The bacterial assemblage of antibiotic-treated anemones (APO_AB and SYM_AB) was markedly different from the microbiomes of other anemones in that it was considerably less complex. This was highlighted by the notion that &#x003E;90% of the active community in apo- and symbiotic anemones was comprised of the same three bacterial taxa (OTU0002, OTU0003, and OTU0006) affiliated to the order Rhizobiales and the genera <italic>Marinobacter</italic> and <italic>Alcanivorax</italic> (<xref ref-type="fig" rid="F4">Figure 4B</xref>). Conversely, 75% of the active community of aposymbiotic control anemones was comprised of only six bacterial taxa (OTUs 0005, 0012, 0013, 0014, 0015, 0018, <xref ref-type="fig" rid="F4">Figure 4B</xref>), which were largely absent in the antibiotic treated Aiptasia. Notably, &#x003E;70% of the bacterial communities of all inoculated aposymbiotic anemones were dominated by the same taxa regardless of the inoculum. The dominant bacterial taxa were representatives of the order Alteromonadales (OTU0001, OTU0004, OTU0007, OTU0008), which were barely detected in aposymbiotic control anemones. For the symbiotic anemones, the active bacterial community of control polyps was dominated by a few bacterial taxa of the order Alteromonadales and the genera <italic>Glaciecola</italic> and <italic>Thalassomonas</italic> (<xref ref-type="fig" rid="F4">Figure 4B</xref>). Similarly, microbiome transplanted symbiotic Aiptasia resembled each other and were dominated by bacteria of the order Alteromonadales (OTU0001, OTU0004, OTU0007, OTU0008, OTU0009), just as the microbiome transplanted aposymbiotic Aiptasia. Thus, despite the differences in microbial community composition of apo- and symbiotic control anemones, microbiome transplanted gnotobiotic apo- and symbiotic anemones look much more alike with regard to their microbiome.</p>
<p>To get better insight into the bacterial taxa that were present in Aiptasia after microbiome transplantation, we compared the active bacterial community of control conditions (APO/SYM) and treatment conditions (<xref ref-type="fig" rid="F5">Figure 5</xref> and <xref ref-type="supplementary-material" rid="TS1">Supplementary Table 6</xref>). This comparison shows that all inoculated anemones (+APOinoc, +SYMinoc, +ACRinoc, and +PORinoc) harbored bacterial taxa that were already present (active) in control anemones as well as &#x201C;novel&#x201D; (i.e., previously undetected) bacteria. This may point to potential carryover from gnotobiotic anemones (not all bacteria were depleted). In the case of coral microbiome inoculations, we observed association with novel bacteria from the coral microbiomes (as determined by the comparison to APO and SYM anemones, <xref ref-type="fig" rid="F5">Figure 5</xref> and <xref ref-type="supplementary-material" rid="TS1">Supplementary Table 6</xref>). In particular, two bacteria taxa, of the genus <italic>Thalassomonas</italic> (OTU0016) and an unclassified Alteromonadales (OTU0021), are worthwhile mentioning because they were both found to be abundant (i.e., active) in coral microbiome transplanted Aiptasia (i.e., APO+ACRinoc, APO+PORinoc, SYM+ACRinoc, and SYM+PORinoc), but absent from Aiptasia transplanted with their own microbiomes (i.e., APO+APOinoc and SYM+SYMinoc) (<xref ref-type="supplementary-material" rid="TS1">Supplementary Table 6</xref>). Both OTUs are putative coral microbiome bacteria that were able to colonize apo- and symbiotic Aiptasia. On the contrary, a putative coral microbiome taxon from the genus <italic>Glaciecola</italic> (OTU0195) was only found associated with symbiotic anemones. Further, we found two Gammaproteobacteria (OTU0067 and OTU0099) to be specifically prevalent in anemones inoculated with <italic>Porites</italic> sp. microbiome preparations.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption><p>Bacterial taxa of control and microbiome transplanted Aiptasia. Venn diagrams representing the number of active OTUs ubiquitously present in all control anemones (APO/SYM), shared between APO/SYM anemones and transplanted anemones (APO+APOinoc, APO+ACRinoc, APO+PORinoc and SYM+SYMinoc, SYM+ACRinoc, SYM+PORinoc), and ubiquitously present in transplanted anemones 7 days after the microbiome transplantation. In the absence of sequenced inocula we chose to assess bacterial taxa that were consistently present in coral inoculated Aiptasia, but not present in control Aiptasia, as an indication for bacteria of coral origin. APO/SYM, apo- and symbiotic control anemones; APO_AB/SYM_AB, 7-day antibiotic-treated anemones with a subsequent 1-day recovery; APO+APOinoc, APO microbiome transplantation after antibiotic treatment; SYM+SYMinoc, SYM microbiome transplantation after antibiotic treatment; APO/SYM+ACRinoc, <italic>Acropora humilis</italic> microbiome transplantation after antibiotic treatment (7 days after inoculation); APO/SYM+PORinoc, <italic>Porites</italic> sp. microbiome transplantation after antibiotic treatment (7 days after inoculation).</p></caption>
<graphic xlink:href="fmicb-12-637834-g005.tif"/>
</fig>
</sec>
</sec>
<sec id="S4">
<title>Discussion</title>
<p>It is becoming increasingly clear that the specific composition and abundance of certain bacterial species affect host health and fitness (<xref ref-type="bibr" rid="B56">McFall-Ngai et al., 2013</xref>). At the same time, recent studies highlight that bacterial associations are not stable over time, but rather, assemble flexibly following fluctuations in the prevailing environment(s) (<xref ref-type="bibr" rid="B71">Roder et al., 2015</xref>; <xref ref-type="bibr" rid="B97">Ziegler et al., 2017</xref>; <xref ref-type="bibr" rid="B96">Ziegler et al., 2019</xref>; <xref ref-type="bibr" rid="B88">Voolstra and Ziegler, 2020</xref>). On the one hand, such observations support the notion that microbiome community changes can support host ecological adaption to environmental change (<xref ref-type="bibr" rid="B68">Reshef et al., 2006</xref>; <xref ref-type="bibr" rid="B88">Voolstra and Ziegler, 2020</xref>). On the other hand, the premise of flexibility gives rise to the idea of probiotics, i.e., inoculation with beneficial bacteria to support metaorganism stress resilience (<xref ref-type="bibr" rid="B63">Peixoto et al., 2017</xref>, <xref ref-type="bibr" rid="B64">2019</xref>, <xref ref-type="bibr" rid="B65">2021</xref>). The latter is gaining attention with regards to reef-building corals given the alarming loss of coral reef cover over recent decades (<xref ref-type="bibr" rid="B44">Hughes et al., 2017a</xref>, <xref ref-type="bibr" rid="B41">2020</xref>). However, besides the acknowledged importance of coral-associated bacteria (<xref ref-type="bibr" rid="B7">Bang et al., 2018</xref>; <xref ref-type="bibr" rid="B85">van Oppen and Blackall, 2019</xref>) and the promise of coral probiotics to work in principle (<xref ref-type="bibr" rid="B74">Rosado et al., 2019</xref>), we are still missing answers to many of the basic questions surrounding cnidarian microbiome building principles and the underlying mechanistic aspects. Aiptasia is an emerging model system to study cnidarian symbioses, and here we set out to build a foundation for bacterial functional studies using the Aiptasia model by characterizing surface topography, carrying capacity, and assessing the prospect of microbiome transplants.</p>
<p>Our results show pronounced differences in the ultrastructure of the surface ectoderm between <italic>Hydra</italic> and anthozoans with implications for microbial association. SEM analyses of <italic>Hydra</italic>, <italic>N. vectensis</italic>, Aiptasia, and three scleractinian coral species suggest that bacterial epibionts in anthozoans are (more) restricted to the surface mucus layer (SML) in comparison to hydrozoans. Notably, <italic>Hydra</italic> anemones feature a smooth surface ectoderm where the epithelial glycocalyx (i.e., the pericellular matrix made of glycoproteins and glycolipids that cover the plasma membrane of the epithelium) promotes bacterial attachment and lacks extensive ectodermal ciliation that may prevent bacterial adhesion (<xref ref-type="bibr" rid="B48">Kesimer et al., 2013</xref>; <xref ref-type="bibr" rid="B30">Fraune et al., 2014</xref>; <xref ref-type="bibr" rid="B91">Wein et al., 2018</xref>). Other hydrozoans such as <italic>Ectopleura crocea</italic> and <italic>Cladonema</italic> sp. have shown colonizing epibionts attached to the glycocalyx, which ranged from 200 nm to 1 &#x03BC;m in thickness from the hydroid ectoderm to the epibiont, and their surface topography was also shown to be smoother, resembling that of Hydra (<xref ref-type="bibr" rid="B22">di Camillo et al., 2012</xref>; <xref ref-type="bibr" rid="B1">Abouna et al., 2015</xref>). Although <italic>Hydra</italic> can be considered a derived hydrozoan due to its life history (e.g., lack of a medusoid stage and freshwater habitat), imaging results from the current and other studies (e.g., <xref ref-type="bibr" rid="B22">di Camillo et al., 2012</xref>; <xref ref-type="bibr" rid="B1">Abouna et al., 2015</xref>) support the general notion that hydrozoans and anthozoans differ in their surface topographies, with anthozoans featuring a ciliated, rough surface, and a more defined ectoderm-SML separation in contrast to hydrozoans that seem to exhibit a smooth(er) less ciliated surface. It has been shown that the SML of corals is highly dynamic, with SML being cyclically shed (<xref ref-type="bibr" rid="B15">Bythell and Wild, 2011</xref>). This is thought to prevent pathogen colonization from the surrounding environment (<xref ref-type="bibr" rid="B82">Shnit-Orland and Kushmaro, 2009</xref>; <xref ref-type="bibr" rid="B35">Glasl et al., 2016</xref>), but might also explain the flexible microbial association of corals commonly found across different environments (<xref ref-type="bibr" rid="B71">Roder et al., 2015</xref>; <xref ref-type="bibr" rid="B78">R&#x00F6;thig et al., 2016b</xref>, <xref ref-type="bibr" rid="B79">2017</xref>; <xref ref-type="bibr" rid="B97">Ziegler et al., 2017</xref>; <xref ref-type="bibr" rid="B88">Voolstra and Ziegler, 2020</xref>) and may contribute to the efficacy of coral probiotics (<xref ref-type="bibr" rid="B63">Peixoto et al., 2017</xref>, <xref ref-type="bibr" rid="B65">2021</xref>). At a more basal level, the difference in surface topography between hydrozoans and anthozoans argues for the need of having distinct cnidarian models to reflect the implied microbial association differences. For the two anthozoan models, <italic>N. vectensis</italic> and Aiptasia, there was little difference in terms of ectodermal topography and bacterial colonization between the two organisms, both at the column and tentacle level. However, microalgal symbionts in the family Symbiodiniaceae (<xref ref-type="bibr" rid="B50">LaJeunesse et al., 2018</xref>) were shown to putatively contribute to the composition of coral mucus through their exudates (<xref ref-type="bibr" rid="B13">Brown and Bythell, 2005</xref>; <xref ref-type="bibr" rid="B61">Nelson et al., 2013</xref>), which affect bacterial association (<xref ref-type="bibr" rid="B54">Matthews et al., 2020</xref>), and Symbiodiniaceae were also shown to harbor themselves specific bacteria (<xref ref-type="bibr" rid="B52">Maire et al., 2021</xref>). As such, Aiptasia is a model system not only for the study of coral-algal symbiosis, but also for the study of bacterial associations and for testing the capacity for microbiome manipulation as further discussed below.</p>
<p>We were surprised by the lack of observed bacterial colonization at the surface ectoderm of Aiptasia (anthozoans more generally) using SEM, which was readily apparent in <italic>Hydra</italic> using the same technique. As alluded to above, this might be a consequence of surface topography differences, which ultimately affect bacterial colonization, but also differences in how the preparation affects sample integrity. In the case of <italic>Hydra</italic>, the accessible glycocalyx was preserved during SEM preparation, whereas the mucus of the anthozoans species was lost by employing a classical SEM sample protocol. Indeed, a modified TEM protocol developed to preserve the mucus layer also confirmed the presence of bacteria in the surface mucus layer of Aiptasia polyps, but not in the ectodermal layer or glycocalyx (<xref ref-type="supplementary-material" rid="FS1">Supplementary Figure 1</xref>). This highlights the need for continuous development and improvements of protocols to visualize bacterial association (<xref ref-type="bibr" rid="B89">Wada et al., 2016</xref>). For instance, TEM analyses may be combined with CARD-FISH staining for improved specificity and visualization of Aiptasia- and coral-associated bacteria besides the exploration of other methods (<xref ref-type="bibr" rid="B48">Kesimer et al., 2013</xref>).</p>
<p>Complementary to the visual assessment of bacterial abundance, we determined a bacterial carrying capacity of &#x223C; 10<sup>4</sup> to 10<sup>5</sup> bacterial cells per Aiptasia polyp, pending on the symbiotic state. This number is similar to the bacterial density reported for <italic>Hydra</italic> (<xref ref-type="bibr" rid="B91">Wein et al., 2018</xref>) and may roughly equate to the &#x223C;10<sup>6</sup> bacterial cells/cm<sup>2</sup> coral tissue previously reported (<xref ref-type="bibr" rid="B49">Koren and Rosenberg, 2006</xref>; <xref ref-type="bibr" rid="B33">Garren and Azam, 2012</xref>). It is interesting to note that our bacterial capacity was an order of magnitude higher for symbiotic (10<sup>5</sup> bacterial cells/polyp) in comparison to aposymbiotic (10<sup>4</sup> bacterial cells/polyp) anemones. This difference may arise from the additional niche space provided by the symbiosome, which was previously shown to harbor bacteria (<xref ref-type="bibr" rid="B2">Ainsworth et al., 2015</xref>), and through association with Symbiodiniaceae, which harbor their own microbial community (<xref ref-type="bibr" rid="B21">Deines et al., 2020</xref>; <xref ref-type="bibr" rid="B52">Maire et al., 2021</xref>). Visualization and enumeration of cnidarian-associated bacteria is still relatively rare (<xref ref-type="bibr" rid="B60">Neave et al., 2017</xref>; <xref ref-type="bibr" rid="B18">Cooke et al., 2019</xref>), in part because of the difficulties associated with fluorescent staining techniques in corals (<xref ref-type="bibr" rid="B89">Wada et al., 2016</xref>). As such, we relied on CFU counts, which avoid many of these difficulties but at the cost of media selectivity, as highlighted by the discrepancy between absence of CFUs in marine media and amplicon sequencing-based detection of some bacterial taxa. Literature perusal suggests that the most prevalent bacterial taxa detected in gnotobiotic anemones using sequencing (OTU0002, OTU0003, and OTU0006) cannot grow on our employed media and therefore escape CFU counting (<xref ref-type="bibr" rid="B12">Brooijmans et al., 2009</xref>; <xref ref-type="bibr" rid="B95">Yetti et al., 2015</xref>; <xref ref-type="bibr" rid="B90">Wang et al., 2016</xref>). Nevertheless, the antibiotic-treated anemones were highly bacteria depleted as more than 95% of the sequencing reads represented only three OTUs, which correspond to less than 5% of the active taxa detected in control anemones. As such, we consider animals treated with our gnotobiotic protocol (<xref ref-type="bibr" rid="B19">Costa et al., 2019</xref>) highly bacteria depleted. Besides the availability of axenic or gnotobiotic animals, it is desirable to have bacterial isolates with fluorescent reporter plasmids for more accurate estimation, which also allows for tracking location and abundance of said bacteria, as shown in <italic>Hydra</italic> (<xref ref-type="bibr" rid="B91">Wein et al., 2018</xref>). On this note, viability-qPCR (<xref ref-type="bibr" rid="B26">Emerson et al., 2017</xref>) may comprise a molecular method for enumeration of the density of active bacteria, although we found that it requires significant optimization due to taxon-specific differences with regard to dye permeability. As alluded to above and recently (<xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>), 75% of the relative microbial abundance is comprised of only a handful of bacterial taxa, making Aiptasia a &#x201C;non-complex&#x201D; coral model for microbiome studies with the promise to obtain bacterial isolates for functional testing and manipulation (<xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>).</p>
<p>Our RNA-based sequencing analysis revealed that the community of active bacteria was less diverse in comparison to the DNA-based microbial community (<xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>): we identified an average of 38 and 64 active bacterial taxa associated with apo- and symbiotic anemones, while DNA-based analysis of the standing community retrieved 109 and 118 distinct bacteria, respectively. This may seem like a stark difference; however, it is not straight-forward to compare RNA- and DNA-based bacterial communities. Since abundance estimates are relative, &#x201C;absence&#x201D; in the RNA-based community analysis merely indicates that we could identify less bacteria (at the current sequencing depth) and that there is a putative difference between the bacterial community that is &#x201C;present&#x201D; (DNA) and the one that is &#x201C;active&#x201D; (RNA). Nevertheless, we compared the overlap in OTU-assigned taxonomies at the genus level for CC7 from <xref ref-type="bibr" rid="B77">R&#x00F6;thig et al. (2016a)</xref> and this study, which showed that 65% (APO) and 84% (SYM) of the identified bacterial genera in the RNA-based analysis were also found in the DNA-based analysis. Notably, such comparisons have inherent biases due to taxonomic redundancies and differences in the taxonomic classification between different OTU datasets.</p>
<p>To begin to explore the prospect of Aiptasia microbiome manipulation as a tool to interrogate bacterial function and test the effect of probiotics on holobiont biology, we conducted a series of inoculations/transplants on gnotobiotic Aiptasia with microbiomes from control anemones and from two coral species. <italic>Acropora humilis</italic> was chosen because its microbiome is highly uneven and dominated by bacteria of the genus <italic>Endozoicomonas</italic>, which could be used for tracking of the microbial transplant, since Aiptasia CC7 seems devoid of <italic>Endozoicomonas</italic> (<xref ref-type="bibr" rid="B77">R&#x00F6;thig et al., 2016a</xref>). However, we did not detect <italic>Endozoicomonas</italic> in the microbiome of inoculated anemones (i.e., SYM+ACRinoc, APO+ACRinoc). This suggests that <italic>Endozoicomonas</italic> exhibit high (coral) host specificity, despite their broad and prevalent distribution across marine invertebrates (<xref ref-type="bibr" rid="B59">Neave et al., 2016</xref>, <xref ref-type="bibr" rid="B60">2017</xref>; <xref ref-type="bibr" rid="B76">Rossbach et al., 2019</xref>). Moreover, <italic>Endozoicomonas</italic> reside within coral tissues (<xref ref-type="bibr" rid="B59">Neave et al., 2016</xref>, <xref ref-type="bibr" rid="B60">2017</xref>), which may explain their absence after microbiome transplantation, because mucus-associated bacteria may be easier to transfer than tissue-associated bacteria. Such differences putatively provide important insight regarding the choice of bacteria targeted for microbiome transplants. In contrast to <italic>A. humilis</italic>, <italic>Porites</italic> sp. was chosen as a donor because it is considered an environmentally resilient species with a more even and diverse microbiome (<xref ref-type="bibr" rid="B38">Hadaidi et al., 2017</xref>; <xref ref-type="bibr" rid="B69">Robbins et al., 2019</xref>). As such, successful microbiome transplantation would allow for subsequent testing of altered stress susceptibility. First off, our results show that all transplanted animals harbor a significantly different active bacterial community when compared to control anemones with the general notion that inoculated Aiptasia resemble each other more than control animals (<xref ref-type="fig" rid="F4">Figure 4</xref> and <xref ref-type="supplementary-material" rid="TS1">Supplementary Table 5</xref>). This is not highly surprising given that formation of an established microbial community may take time and likely goes through processes of inter-bacterial communication, host-bacterial communication, and winnowing, all of which presumably affect microbiome composition (<xref ref-type="bibr" rid="B28">Franzenburg et al., 2013a</xref>; <xref ref-type="bibr" rid="B10">Bernasconi et al., 2019</xref>; <xref ref-type="bibr" rid="B81">Shibl et al., 2020</xref>). As such, microbial consortia associated with Aiptasia after microbiome transplantation might represent a mix of specific bacteria administered with the inocula and opportunistic, environmentally present bacteria (e.g., resistant bacteria that survived the antibiotic treatment and were attached to the wells of the rearing plate), in particular copiotrophs. Copiotrophs are known to rapidly (re)populate carbon-rich environments such as the surface mucus layer (<xref ref-type="bibr" rid="B61">Nelson et al., 2013</xref>; <xref ref-type="bibr" rid="B55">McDevitt-Irwin et al., 2017</xref>; <xref ref-type="bibr" rid="B16">C&#x00E1;rdenas et al., 2018</xref>; <xref ref-type="bibr" rid="B37">Hadaidi et al., 2019</xref>) and as such may &#x201C;drive&#x201D; initial microbial repopulation dynamics. This makes the long(er)-term tracking of microbiome assemblage dynamics after transplantation important. It also suggests that antibiotic treated Aiptasia without any subsequent inoculation should be included in future experimental designs as controls for determining load and type of &#x201C;residual&#x201D; bacteria. In addition, future experiments should also include microbiome transplantations of untreated Aiptasia, resembling current coral probiotics procedures (<xref ref-type="bibr" rid="B65">Peixoto et al., 2021</xref>). This would provide further insight regarding repopulation dynamics and constraints.</p>
<p>Many of the taxa found in control Aiptasia established themselves again after microbiome inoculation, such as bacteria in the genus <italic>Thalassomonas</italic> (OTU0005, OTU0012), <italic>Glaciecola</italic> (OU0014), <italic>Thalassobius</italic> (OTU0018), or <italic>Alteromonas</italic> (OTU0007) (<xref ref-type="supplementary-material" rid="TS1">Supplementary Table 6</xref>). Microbiome transplantations with inocula from <italic>A. humilis</italic> and <italic>Porites</italic> sp. were successful to the extent that (at least) some foreign bacterial taxa (some of which were specific to the coral species from which the inoculum was obtained) were present (active) in Aiptasia polyps, as evidenced by their detection 7 days after microbiome transplantation. Notably, unavailability of sequenced inocula and coral native microbiomes within the current study limited the extent to which we could identify bacterial taxa with broad host compatibility, suitable for cross-species microbiome manipulation. Due to this, we considered bacterial taxa that were consistently present in coral-inoculated but not present in control Aiptasia as of putative coral origin. Besides treatment-specific differences, we commonly found bacterial taxa belonging to the Alteromonadaceae, Rhodobacteraceae, and Gammaproteobacteria to be transferred. This is encouraging given that bacteria from these taxonomic affiliations are commonly found in coral microbiomes (<xref ref-type="bibr" rid="B70">Roder et al., 2014</xref>; <xref ref-type="bibr" rid="B60">Neave et al., 2017</xref>; <xref ref-type="bibr" rid="B97">Ziegler et al., 2017</xref>, <xref ref-type="bibr" rid="B96">2019</xref>).</p>
<p>At large, our results suggest that cross-species microbiome manipulation via transplantation is possible (to a certain extent). That is to say, Aiptasia is a suitable system to test the function of (at least some) coral bacteria and their effect on holobiont biology. The obvious next step is to test for altered holobiont phenotypes, e.g., increased or decreased stress resilience, using a standardized framework (<xref ref-type="bibr" rid="B87">Voolstra et al., 2020</xref>) after microbial transplantation with subsequent elucidation of the underlying mechanism(s). In addition, to achieve consistent and stable changes of microbial host consortia, an improved understanding of inocula persistence, dispersion, location, bacterial load, and any putative long-term effects is wanted. Aiptasia seems like the model system of choice, given its taxonomic relatedness and physiological similarities with regard to Symbiodiniaceae association, microbiome composition, and surface and tissue complexity.</p>
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<sec id="S5">
<title>Conclusion</title>
<p>Bacteria affect the health and fitness of their hosts. Given the worldwide decline of corals and the reefs they build, a better understanding of the function of bacteria and their potential manipulation is important. To achieve this, the development of coral model systems is imperative. Here we set the foundation for Aiptasia as a model for the study of coral-bacterial interactions. We show that the surface ectoderm topography is highly similar between Aiptasia and corals, in line with overall similarities in the microbiome composition established previously. Building on these prospects, we have developed a protocol for the generation of gnotobiotic Aiptasia and determined the bacterial carrying capacity to perform microbiome manipulation experiments. Our results support the principal suitability of Aiptasia to microbiome manipulation and its putative ability to incorporate foreign bacterial species. Although more work is needed, our study is a first step and provides an avenue to study the function of self and foreign bacteria as well as to explore the mechanisms underlying microbial acquisition, association, and host specificity. Future work should incorporate standardized testing to elucidate the effect of altered microbiomes on holobiont phenotypes as well as the generation of fluorescently labeled bacterial isolates, which will allow for spatial/temporal tracking and enumeration of bacterial associates. The work presented here provides a foundation and we will continue to develop Aiptasia as a coral model for bacterial functional studies.</p>
</sec>
<sec id="S6">
<title>Data Availability Statement</title>
<p>Data determined in this study are available under NCBI BioProject <ext-link ext-link-type="DDBJ/EMBL/GenBank" xlink:href="PRJNA665377">PRJNA665377</ext-link> (<ext-link ext-link-type="uri" xlink:href="https://www.ncbi.nlm.nih.gov/bioproject/665377">https://www.ncbi.nlm.nih.gov/bioproject/665377</ext-link>). Scripts used for data analysis, curation, and plotting are available at <ext-link ext-link-type="uri" xlink:href="https://github.com/ajcardenasb/Aiptasia_microbiome_manipulation">https://github.com/ajcardenasb/Aiptasia_microbiome_manipulation</ext-link>. Abundant bacterial OTU reference sequences are available under GenBank Accession numbers <ext-link ext-link-type="DDBJ/EMBL/GenBank" xlink:href="MW577132">MW577132</ext-link> &#x2013; <ext-link ext-link-type="DDBJ/EMBL/GenBank" xlink:href="MW577168">MW577168</ext-link> (<ext-link ext-link-type="uri" xlink:href="https://www.ncbi.nlm.nih.gov/nuccore/?term=MW577132:MW577168[accn]">https://www.ncbi.nlm.nih.gov/nuccore/?term=MW577132:MW577168[accn]</ext-link>).</p>
</sec>
<sec id="S7">
<title>Author Contributions</title>
<p>CV, RC, and AC conceived and designed the experiments, analyzed the data, and wrote the manuscript. RC and AC collected and processed the samples. RC, AC, and CL-F generated the data. RC, AC, CL-F, GT, and CV generated the figures. RC, AC, CL-F, GT, AM, and CV interpreted the data. CL-F, AM, and CV provided tools, reagents, and methods. 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>
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<fn-group>
<fn fn-type="financial-disclosure">
<p><bold>Funding.</bold> Research reported in this publication was supported by KAUST baseline funds to CV.</p>
</fn>
</fn-group>
<ack>
<p>We acknowledge the KAUST Imaging and Characterization Core Lab for their support in TEM and SEM analysis and the KAUST Bioscience Core Lab (BCL) for their support with the NGS data generation. We would like to thank all collaborators who tested the bacteria depletion protocol and provided feedback. We would also like to thank Carol Buitrago-Lopez and Hagen Gegner for their help with the coral collection and maintenance. <italic>Hydra magnipapillata</italic> and <italic>Nematostella vectensis</italic> were kindly provided by Prof. Takashi Gojobori&#x2019;s group.</p>
</ack>
<sec id="S10" 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/fmicb.2021.637834/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmicb.2021.637834/full#supplementary-material</ext-link></p>
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