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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Immunol.</journal-id>
<journal-title>Frontiers in Immunology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Immunol.</abbrev-journal-title>
<issn pub-type="epub">1664-3224</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fimmu.2017.00736</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Immunology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Estrogens Promote the Production of Natural Neutralizing Antibodies in Fish through G Protein-Coupled Estrogen Receptor 1</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Rodenas</surname> <given-names>Mar&#x000ED;a C.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://frontiersin.org/people/u/442791"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Cabas</surname> <given-names>Isabel</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>G&#x000F3;mez-Gonz&#x000E1;lez</surname> <given-names>Nuria E.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Arizcun</surname> <given-names>Marta</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Meseguer</surname> <given-names>Jos&#x000E9;</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Mulero</surname> <given-names>Victoriano</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="cor1">&#x0002A;</xref>
<uri xlink:href="http://frontiersin.org/people/u/279447"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Garc&#x000ED;a-Ayala</surname> <given-names>Alfonsa</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="cor1">&#x0002A;</xref>
<uri xlink:href="http://frontiersin.org/people/u/434522"/>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Department of Cell Biology and Histology, Faculty of Biology, University of Murcia, IMIB-Arrixaca</institution>, <addr-line>Murcia</addr-line>, <country>Spain</country></aff>
<aff id="aff2"><sup>2</sup><institution>Centro Oceanogr&#x000E1;fico de Murcia, Instituto Espa&#x000F1;ol de Oceanograf&#x000ED;a (IEO)</institution>, <addr-line>Murcia</addr-line>, <country>Spain</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Lluis Tort, Universitat Aut&#x000F2;noma de Barcelona, Spain</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Carolina Tafalla, Instituto Nacional de Investigaci&#x000F3;n y Tecnolog&#x000ED;a Agraria y Alimentaria, Spain; Irene Salinas, University of New Mexico, United States</p></fn>
<corresp content-type="corresp" id="cor1">&#x0002A;Correspondence: Victoriano Mulero, <email>vmulero&#x00040;um.es</email>; Alfonsa Garc&#x000ED;a-Ayala, <email>agayala&#x00040;um.es</email></corresp>
<fn fn-type="other" id="fn002"><p>Specialty section: This article was submitted to Comparative Immunology, a section of the journal Frontiers in Immunology</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>29</day>
<month>06</month>
<year>2017</year>
</pub-date>
<pub-date pub-type="collection">
<year>2017</year>
</pub-date>
<volume>8</volume>
<elocation-id>736</elocation-id>
<history>
<date date-type="received">
<day>26</day>
<month>04</month>
<year>2017</year>
</date>
<date date-type="accepted">
<day>12</day>
<month>06</month>
<year>2017</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x000A9; 2017 Rodenas, Cabas, G&#x000F3;mez-Gonz&#x000E1;lez, Arizcun, Meseguer, Mulero and Garc&#x000ED;a-Ayala.</copyright-statement>
<copyright-year>2017</copyright-year>
<copyright-holder>Rodenas, Cabas, G&#x000F3;mez-Gonz&#x000E1;lez, Arizcun, Meseguer, Mulero and Garc&#x000ED;a-Ayala</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) or licensor 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>Natural antibodies play crucial roles in pathogen elimination, B-cell survival and homeostasis, and inflammatory and autoimmune diseases. Although estrogens are able to regulate both innate and adaptive immune responses, their role in the production of natural antibodies is unknown. Here, we show that the dietary intake of the synthetic estradiol analog, 17&#x003B1;-ethinylestradiol (EE<sub>2</sub>), one of the most potent pharmaceutical estrogens and intensively used in human therapeutics as a component of most oral contraceptives, regulates the abundance and proliferation of T and IgM<sup>&#x0002B;</sup> B lymphocytes in the teleost fish gilthead seabream (<italic>Sparus aurata</italic> L.). Furthermore, for the first time in vertebrates, it is shown that estrogen signaling through G protein-coupled estrogen receptor 1 (GPER1) induces the production of polyreactive natural antibodies, which are able to crossreact with unrelated antigens and commensal and pathogenic bacteria. In addition, the serum from fish treated with EE<sub>2</sub> or the GPER1 agonist G1 shows higher complement-dependent bactericidal activity than that from non-treated specimens. These results demonstrate that estrogens and GPER1 are the key regulators of natural antibody production and pathogen clearance in fish, paving the way for future studies in other vertebrate classes.</p>
</abstract>
<kwd-group>
<kwd>G protein-coupled estrogen receptor 1</kwd>
<kwd>estrogens</kwd>
<kwd>lymphocytes</kwd>
<kwd>natural antibodies</kwd>
<kwd>evolution</kwd>
<kwd>fish</kwd>
</kwd-group>
<contract-num rid="cn01">BIO2014-52655-R and AGL2014-53167-C3-1-R</contract-num>
<contract-num rid="cn02">19883/GERM/15</contract-num>
<contract-sponsor id="cn01">Ministerio de Econom&#x000ED;a y Competitividad<named-content content-type="fundref-id">10.13039/501100003329</named-content></contract-sponsor>
<contract-sponsor id="cn02">Fundaci&#x000F3;n S&#x000E9;neca<named-content content-type="fundref-id">10.13039/100007801</named-content></contract-sponsor>
<counts>
<fig-count count="6"/>
<table-count count="1"/>
<equation-count count="0"/>
<ref-count count="61"/>
<page-count count="12"/>
<word-count count="7073"/>
</counts>
</article-meta>
</front>
<body>
<sec id="S1" sec-type="introduction">
<title>Introduction</title>
<p>The impact of estrogens on immune responses is well documented (<xref ref-type="bibr" rid="B1">1</xref>&#x02013;<xref ref-type="bibr" rid="B4">4</xref>). For many years, the immune system has been considered as a natural target for estrogen action (<xref ref-type="bibr" rid="B5">5</xref>), as corroborated by the clear sex differences observed in autoimmune and inflammatory disorders (<xref ref-type="bibr" rid="B4">4</xref>).</p>
<p>Estrogens affect different stages of B-cell development and modify the humoral response (<xref ref-type="bibr" rid="B3">3</xref>), while a third generation of selective estrogen receptor (ER) modulators has been found to regulate B development and function (<xref ref-type="bibr" rid="B6">6</xref>). Moreover, it has recently been described that the activation of ERs directly influences antibody (Ab) expression by binding to switch sites and regulatory elements in the immunoglobulin heavy chain locus of activated B cells (<xref ref-type="bibr" rid="B7">7</xref>). All these effects are possible due to the presence of ER in immune cells (<xref ref-type="bibr" rid="B4">4</xref>), including lymphocytes (<xref ref-type="bibr" rid="B8">8</xref>).</p>
<p>Classically, the action of estrogens was thought to be mediated by nuclear ER&#x003B1; and ER&#x003B2;, which function as hormone-inducible transcription factors by binding to the estrogen-responsive element located within the promoter region of target genes (<xref ref-type="bibr" rid="B9">9</xref>), although it was later confirmed that they are also able to rapidly activate transduction pathways <italic>via</italic> non-genomic mechanisms. These additional effects are mediated by a membrane-anchored receptor called G protein-coupled estrogen receptor 1 (GPER1), which was identified by independent laboratories in the early 2000s (<xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B11">11</xref>) and later shown to be activated by 17&#x003B2;-estradiol (E<sub>2</sub>) (<xref ref-type="bibr" rid="B12">12</xref>&#x02013;<xref ref-type="bibr" rid="B14">14</xref>). GPER1 activation downstream mechanisms include several signaling pathways involving MAPKs, ERK, PI3K, cAMP, and intracellular calcium (<xref ref-type="bibr" rid="B15">15</xref>, <xref ref-type="bibr" rid="B16">16</xref>).</p>
<p>Xenoestrogens or environmental estrogens, known as endocrine disruptor chemicals (EDCs), are synthetic or natural substances of high stability that exert toxicity by mimicking the effects of estrogens (<xref ref-type="bibr" rid="B17">17</xref>). They have been described as being involved in autoimmunity (<xref ref-type="bibr" rid="B18">18</xref>, <xref ref-type="bibr" rid="B19">19</xref>) and as reducing B-cell precursors in mice (<xref ref-type="bibr" rid="B20">20</xref>) and have also been found to activate GPER1 (<xref ref-type="bibr" rid="B21">21</xref>). 17&#x003B1;-Ethinylestradiol (EE<sub>2</sub>) is a synthetic analog of E<sub>2</sub> and one of the most potent pharmaceutical estrogens and is intensively used in human therapeutics as a component of most oral contraceptives. The binding affinity of EE<sub>2</sub> to human ERs is one to two times higher than E<sub>2</sub> (<xref ref-type="bibr" rid="B22">22</xref>). However, it has been calculated that 16&#x02013;68% of the dose is excreted in the urine or feces (<xref ref-type="bibr" rid="B23">23</xref>), reaching the waste water treatment plants, where cannot be totally eliminated (<xref ref-type="bibr" rid="B24">24</xref>). Consequently, an unquantified load of xenoestrogens are released into the aquatic environment, where they can be absorbed by sediment and persist for long periods, or taken up by animals and concentrated in their tissues (<xref ref-type="bibr" rid="B22">22</xref>, <xref ref-type="bibr" rid="B25">25</xref>). It has been found in concentrations up to 21&#x02009;ng/l in a south-western European river (Mira, Portugal) (<xref ref-type="bibr" rid="B26">26</xref>).</p>
<p>The gilthead seabream (<italic>Sparus aurata</italic> L.) is a seasonal marine teleost of great commercial value in the Mediterranean area. Its hermaphrodite character makes it an interesting animal model to analyze the role of estrogens, natural or synthetic, in the immune response. We have previously demonstrated that nuclear ERs and GPER1 are expressed in gilthead seabream head kidney (bone marrow equivalent) leukocytes (<xref ref-type="bibr" rid="B27">27</xref>, <xref ref-type="bibr" rid="B28">28</xref>) and that GPER1 modulates granulocyte functions through a cAMP/protein kinase A/CREB signaling pathway (<xref ref-type="bibr" rid="B27">27</xref>). We also observed that EDCs altered the immune response of gilthead seabream by promoting some long-lasting effects even when their estrogenic disruptive effects were not present (<xref ref-type="bibr" rid="B29">29</xref>, <xref ref-type="bibr" rid="B30">30</xref>). Moreover, EE<sub>2</sub> bath-exposed specimens have an altered capacity to respond to an immune challenge, although the compound does not behave as an immunosuppressor (<xref ref-type="bibr" rid="B31">31</xref>), while the dietary intake of EE<sub>2</sub> stimulates the Ab response of vaccinated fish (<xref ref-type="bibr" rid="B29">29</xref>, <xref ref-type="bibr" rid="B30">30</xref>). However, no information exits on the impact of EE<sub>2</sub> on fish lymphocyte proliferation and differentiation or, particularly, on natural antibodies. Natural antibodies are present in the serum of vertebrates without any apparent antigenic stimulation and are an important field of research for their relevance in autoimmunity and for their role as a bridge between innate and adaptive immunities (<xref ref-type="bibr" rid="B32">32</xref>, <xref ref-type="bibr" rid="B33">33</xref>). Although the relevance of natural antibodies in fish is largely unknown, their existence in both cartilaginous and bony fish has been reported (<xref ref-type="bibr" rid="B32">32</xref>, <xref ref-type="bibr" rid="B34">34</xref>&#x02013;<xref ref-type="bibr" rid="B36">36</xref>). In addition, the opsonization and neutralizing ability of natural antibodies of rainbow trout against <italic>Aeromonas salmonicida</italic> has been demonstrated (<xref ref-type="bibr" rid="B37">37</xref>&#x02013;<xref ref-type="bibr" rid="B39">39</xref>). We, therefore, examined whether estrogens, and in particular, GPER1 signaling, are able to modulate T- and B-lymphocyte responses to an immunological challenge and natural Ab production.</p>
</sec>
<sec id="S2" sec-type="materials|methods">
<title>Materials and Methods</title>
<sec id="S2-1">
<title>Animals, <italic>In Vivo</italic> Treatments, and Sample Collection</title>
<p>Healthy specimens of gilthead seabream were from the Oceanographic Center of Murcia (Mazarr&#x000F3;n, Spain), where they were kept in running seawater aquaria (dissolved oxygen 6&#x02009;ppm, flow rate 20% aquarium vol/h) with a natural temperature and photoperiod. They were fed three times per day with a commercial pellet diet (44% protein and 22% lipids; Skretting) at a feeding rate of 1.5% of fish biomass. The environmental parameters, mortality, and food intake, as well as behavior, were recorded daily.</p>
<p>Two-month-old gilthead seabream specimens (<italic>n</italic>&#x02009;&#x0003D;&#x02009;100/treatment), with a body weight of 26.6&#x02013;63.2 (from the beginning to the end of the experiment), were exposed to EE2 (Figure <xref ref-type="fig" rid="F1">1</xref>A) in 170&#x02009;l aquaria. Briefly, EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food, 98% purity; Sigma) was incorporated in the commercial food using the ethanol evaporation method (0.3&#x02009;l ethanol/kg of food), as described elsewhere (<xref ref-type="bibr" rid="B40">40</xref>). The specimens were fed three times a day <italic>ad libitum</italic> with the pellet diet supplemented with EE<sub>2</sub> (treated fish) or non-supplemented (untreated fish) for 76&#x02009;days (days of treatment, dt). Following this time, all the specimens were fed with the commercial food for a further 23&#x02009;days (days posttreatment, dpt) (Figure <xref ref-type="fig" rid="F1">1</xref>A). In order to evaluate the effect of EE<sub>2</sub> on the immune response, specimens were intraperitoneally (i.p.) injected with keyhole limpet hemocyanin (KLH) (45&#x02009;&#x003BC;g/fish; Sigma-Aldrich) and Imject Alum adjuvant (4&#x02009;mg/fish; Thermo Scientific) (vaccinated/immunized fish) or phosphate-buffered saline (PBS) (control/unvaccinated fish) at the end of the treatment period, 76&#x02009;dt. Samples were taken 40 and 76&#x02009;dt and 1, 9, and 23&#x02009;days postimmunization (dpi) or dpt. Food intake was similar in all groups. Specimens (<italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/treatment/time of sampling) were fasted for 24&#x02009;h before sampling. They were tranquilized by 8&#x02009;&#x003BC;l/l of clove oil, immediately anesthetized using 40&#x02009;&#x003BC;l/l of clove oil, weighed and decapitated before the head kidneys and spleens were removed, and processed for gene expression and/or flow cytometry analysis, as described later. Serum samples from trunk blood were obtained by centrifugation and immediately frozen and stored at &#x02212;80&#x000B0;C until use. Cell suspensions from head kidney and spleen were obtained as described elsewhere (<xref ref-type="bibr" rid="B41">41</xref>, <xref ref-type="bibr" rid="B42">42</xref>).</p>
<fig id="F1" position="float">
<label>Figure 1</label>
<caption><p>Experimental design: 17&#x003B1;-ethinylestradiol (EE<sub>2</sub>) dietary exposure and immunization protocol of gilthead seabream juveniles. <bold>(A)</bold>. Fish were exposed to a non-supplemented diet (untreated fish) or to a supplemented diet with 5&#x02009;&#x003BC;g EE<sub>2</sub>/g food (treated fish) for 76&#x02009;days (days of treatment, dt). Then, the specimens were fed with commercial food for an additional period of 23&#x02009;days (days posttreatment, dpt). Fish were intraperitoneally (i.p.) injected with phosphate-buffered saline (PBS) (unvaccinated or control fish) or keyhole limpet hemocyanin (KLH) plus Imject Alum adjuvant (vaccinated fish) at 76&#x02009;dt. Sampling was carried out 40 and 76&#x02009;dt and 1, 9, and 23&#x02009;days postinjection (dpi) (1, 9, and 23&#x02009;dpt). <bold>(B)</bold> The levels of vitellogenin (Vtg) were determined in the serum of untreated and EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food)-treated fish 1, 9, and 23&#x02009;days after ceasing the treatment (dpt) by ELISA. Levels are shown as fold increase relative to the mean of untreated fish. Each bar represents mean&#x02009;&#x000B1;&#x02009;SEM of duplicates of six independent fish. The sample size was <italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/group/time of sampling. The asterisks denote statistically significant differences after a Student&#x02019;s <italic>t</italic>-test between the untreated and the EE<sub>2</sub>-treated group, at each time point and between the EE<sub>2</sub>-treated groups at the different time points. &#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05; &#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.01; and &#x0002A;&#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.001. <bold>(C)</bold> The <italic>il1b</italic> mRNA levels were determined in the head kidney of untreated and EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food)-treated fish (vaccinated or not) 1, 9, and 23&#x02009;days postimmunization (dpi) by RT-qPCR. Gene expression levels were normalized to <italic>rps18</italic> mRNA levels, and data represent as the mean&#x02009;&#x000B1;&#x02009;SEM of technical triplicates of six independent fish. Levels were shown as fold increase relative to the mean of non-vaccinated fish. The sample size was <italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/group/time of sampling. The asterisks denote statistically significant differences after a Student&#x02019;s <italic>t</italic>-test between unvaccinated and vaccinated fish at each time point. &#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05; &#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.01; and &#x0002A;&#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.001.</p></caption>
<graphic xlink:href="fimmu-08-00736-g001.tif"/>
</fig>
<p>Another set of experiments was performed for serum Ab titer determination by ELISA: (1) 2-month-old gilthead seabream specimens were dietary treated with EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food) or the GPER1 agonist G1 (5&#x02009;&#x003BC;g/g food; Sigma-Aldrich) for 110&#x02009;days (<xref ref-type="bibr" rid="B30">30</xref>), (2) adult specimens (650&#x02009;g mean weight) were treated with 0, 5, and 50&#x02009;ng/l EE<sub>2</sub> for 2&#x02009;months by bath immersion (<xref ref-type="bibr" rid="B31">31</xref>), and (3) adult specimens (225&#x02009;g mean weight) were exposed to dietary G1 (0, 2, and 20&#x02009;&#x003BC;g/fish/day treatment) for 50&#x02009;days (<xref ref-type="bibr" rid="B27">27</xref>).</p>
</sec>
<sec id="S2-2">
<title>Determination of Serum Vitellogenin (Vtg) Levels</title>
<p>The serum Vtg levels were determined by the enzyme-linked immunosorbent assay using a commercial kit (Cayman Chemical), following the manufacturer&#x02019;s instructions. In brief, an aliquot of 1:500 diluted serum from untreated and EE<sub>2</sub>-treated fish (<italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/treatment/time of sampling) was added to flat-bottomed 96-well plates, followed by a commercial polyclonal Ab against gilthead seabream Vtg (1:100) and an antirabbit IgG (whole molecule)-peroxidase Ab (1:1,000) (Sigma-Aldrich). Finally, the chromogen tetramethylbenzidine (TMB) was added and the absorbance was read at 450&#x02009;nm using an FLUOstart luminometer (BGM; LabTechnologies).</p>
</sec>
<sec id="S2-3">
<title>Analysis of Gene Expression</title>
<p>Total RNA was extracted from head kidney from untreated and EE<sub>2</sub>-treated (vaccinated or not) fish (<italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/treatment/time of sampling) at 1, 9, and 23&#x02009;dpi/dpt with TRIzol Reagent (Thermo Fisher Scientific), following the manufacturer&#x02019;s instructions, and quantified with a spectrophotometer (NanoDrop, ND-1000). The RNA was then treated with amplification grade DNase I (1&#x02009;U/&#x003BC;g RNA; Thermo Fisher Scientific) to remove genomic DNA traces that might interfere with the PCRs, and the SuperScript III RNase H Reverse Transcriptase (Thermo Fisher Scientific) was used to synthesize first-strand cDNA with oligo-dT18 primer from 1&#x02009;mg of total RNA for 50&#x02009;min at 50&#x000B0;C. The &#x003B2;-actin (<italic>actb</italic>) gene was analyzed by PCR performed with an Eppendorf Mastercycle Gradient Instrument (Eppendorf) to check cDNA quality. Reaction mixtures were incubated for 2&#x02009;min at 94&#x000B0;C, followed by 30 cycles of 45&#x02009;s at 94&#x000B0;C, 45&#x02009;s at the specific annealing temperature (55&#x000B0;C), 45&#x02009;s at 72&#x000B0;C, and finally, 10&#x02009;min at 72&#x000B0;C.</p>
<p>In the same samples, the expression levels of the gene coding for the proinflammatory cytokine interleukin-1&#x003B2; (<italic>il1b</italic>) were analyzed by real-time PCR performed with an ABI PRISM 7500 instrument (Applied Biosystems) using the SYBR Green PCR Core Reagents (Applied Biosystems). Reaction mixtures were incubated for 10&#x02009;min at 95&#x000B0;C, followed by 40 cycles of 15&#x02009;s at 95&#x000B0;C, 1&#x02009;min at 60&#x000B0;C, and finally, 15&#x02009;s at 95&#x000B0;C, 1&#x02009;min at 60&#x000B0;C, and 15&#x02009;s at 95&#x000B0;C. The gene expression was corrected by the ribosomal protein S18 gene (<italic>rps18</italic>) content in each sample using the comparative cycle threshold method, Ct method (2<sup>&#x02212;&#x00394;&#x00394;Ct</sup>). The gilthead seabream-specific primers used are listed in Table <xref ref-type="table" rid="T1">1</xref>. In all cases, samples were analyzed in triplicate.</p>
<table-wrap position="float" id="T1">
<label>Table 1</label>
<caption><p>Gene accession numbers and primer sequences used for expression analysis.</p></caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th valign="top" align="left">Gene</th>
<th valign="top" align="left">Accession no.</th>
<th valign="top" align="center">Name</th>
<th valign="top" align="left">Sequence (5&#x02032;/30)</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top"><italic>actb</italic></td>
<td align="left" valign="top">X89920</td>
<td align="center" valign="top">F3</td>
<td align="left" valign="top">ATCGTGGGGCGCCCCAGGCACC</td>
</tr>
<tr>
<td align="left" valign="top"/>
<td align="left" valign="top"/>
<td align="center" valign="top">R3</td>
<td align="left" valign="top">CTCCTTAATGTCACGCACGATTTC</td>
</tr>
<tr>
<td align="left" valign="top"><italic>il1b</italic></td>
<td align="left" valign="top">AJ277166</td>
<td align="center" valign="top">F2</td>
<td align="left" valign="top">GGGCTGAACAACAGCACTCTC</td>
</tr>
<tr>
<td align="left" valign="top"/>
<td align="left" valign="top"/>
<td align="center" valign="top">R3</td>
<td align="left" valign="top">TTAACACTCTCCACCCTCCA</td>
</tr>
<tr>
<td align="left" valign="top"><italic>rps18</italic></td>
<td align="left" valign="top">AM490061</td>
<td align="center" valign="top">F</td>
<td align="left" valign="top">AGGGTGTTGGCAGACGTTAC</td>
</tr>
<tr>
<td align="left" valign="top"/>
<td align="left" valign="top"/>
<td align="center" valign="top">R</td>
<td align="left" valign="top">CTTCTGCCTGTTGAGGAACC</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p><italic>The gene symbols followed the Zebrafish Nomenclature Guidelines (<uri xlink:href="http://zfin.org/zf_info/nomen.html">http://zfin.org/zf_info/nomen.html</uri>). All primers were used for real-time PCR, except <italic>actb</italic> primers that were used for conventional PCR</italic>.</p>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="S2-4">
<title>Immunofluorescence and Flow Cytometry</title>
<p>The percentage of Zap70-, IgM-, and Pax5-positive cells was determined by flow cytometry (Figure S1A in Supplementary Material). In brief, cytoplasmic Zap70 and Pax5, and surface and total IgM, were detected in aliquots of 0.5&#x02009;&#x000D7;&#x02009;10<sup>6</sup> head kidney leukocytes at 1, 9, and 23&#x02009;dpi/dpt and of spleen leukocytes at 23&#x02009;dpi/dpt (<italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/treatment/time of sampling) from untreated and EE<sub>2</sub>-treated fish (vaccinated or not). The leukocytes were washed with PBS containing 2% fetal calf serum (FCS; Thermo Fisher Scientific) and 0.05% sodium azide (FACS buffer). Cells were fixed with 4% paraformaldehyde for 15&#x02009;min at room temperature. After three rinses, cells were incubated in ice-cold PBS containing 1% BSA and saponin (Thermo Fisher Scientific) at 4&#x000B0;C to permeabilize the plasma membrane. Cells were then stained with 0 and 2&#x02009;&#x003BC;g/ml (0, 1:100) of the 99F2 rabbit monoclonal Ab to Zap70 (Cell Signaling) (<xref ref-type="bibr" rid="B43">43</xref>) or mouse monoclonal Ab specific to seabream IgM (Aquatic Diagnostics) (<xref ref-type="bibr" rid="B44">44</xref>), in PBS containing 2% FCS for 30&#x02009;min at 4&#x000B0;C. After washing, cells were incubated with a 1:1,000 dilution of a phycoerythrin-conjugated antirabbit or -mouse Ig Ab, respectively, for 30&#x02009;min at 4&#x000B0;C, and washed again twice. In other experiments, cells were also stained with 2&#x02009;&#x003BC;g/ml (1:100) of the D19F8 rabbit monoclonal Ab to Pax5 conjugated with Alexa 488 (Cell Signaling) (<xref ref-type="bibr" rid="B43">43</xref>) in PBS containing 2% FCS for 1&#x02009;h at room temperature. After washing, cells were analyzed in a flow cytometer (BD Biosciences).</p>
</sec>
<sec id="S2-5">
<title>Proliferation Assay</title>
<p>To assess the proliferative activity of head kidney and spleen Zap70<sup>&#x0002B;</sup> and IgM<sup>&#x0002B;</sup> cells at 1, 9, and 23&#x02009;dpi/dpt (<italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/treatment/time of sampling), 5-ethynyl-2&#x02032;-deoxyuridine (EdU) (Thermo Fisher Scientific) was i.p. injected 2&#x02009;h before sampling. Then, aliquots of 0.5&#x02009;&#x000D7;&#x02009;10<sup>6</sup> head kidney and spleen cells were used to determine the percentage of double positive cells, i.e., Zap70<sup>&#x0002B;</sup>/EdU<sup>&#x0002B;</sup> and IgM<sup>&#x0002B;</sup>/EdU<sup>&#x0002B;</sup>. EdU<sup>&#x0002B;</sup> cells were detected by fluorescent-azide coupling reaction with EdU according to the manufacturer&#x02019;s protocol (Click-iT; Thermo Fisher Scientific). Zap70<sup>&#x0002B;</sup> and IgM<sup>&#x0002B;</sup> were labeled as described earlier and analyzed by flow cytometry (Figure S1 in Supplementary Material). The percentage of positive cells is given on head kidney R2 region (FSC<sup>low</sup>/SSC<sup>low</sup>), which includes macrophages, lymphocytes, and hematopoietic precursor cells and excludes acidophilic granulocytes (R1: FSC<sup>high</sup>/SSC<sup>high</sup>) (<xref ref-type="bibr" rid="B44">44</xref>).</p>
</sec>
<sec id="S2-6">
<title>Determination of Serum IgM Titer</title>
<p>Total IgM titers and those specific to KLH, lysozyme (unrelated antigen), <italic>Shewanella putrefaciens</italic> strain Pdp11 (a skin microbiota bacterium from gilthead seabream) (<xref ref-type="bibr" rid="B45">45</xref>), or <italic>Vibrio anguillarum</italic> strain R82 (a fish pathogen) were determined in serum by ELISA (Aquatic Diagnostics), following the manufacturer&#x02019;s instructions. In brief, serial dilutions of pooled serum samples (<italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/treatment/time of sampling) were added to flat-bottomed 96-well plate precoated with KLH (1&#x02009;&#x003BC;g/well), chicken egg white lysozyme (1&#x02009;&#x003BC;g/well; Sigma-Aldrich), and <italic>S. putrefaciens</italic> or <italic>V. anguillarum</italic> (10<sup>6</sup> bacteria/well), followed by a monoclonal Ab specific to gilthead seabream IgM (1:100) and then an antimouse IgG peroxidase Ab (1:1,000) (Sigma-Aldrich). Finally, the chromogen TMB was added and the absorbance was read at 450&#x02009;nm using an FLUOstart luminometer (BGM; LabTechnologies). As negative controls, the serum or the primary Ab was omitted.</p>
</sec>
<sec id="S2-7">
<title>Bactericidal Activity</title>
<p><italic>Vibrio anguillarum</italic> strain R82 was grown in tryptic soy agar plates at 25&#x000B0;C. Fresh single colonies were diluted in 5&#x02009;ml of tryptic soy broth, cultured for 16&#x02009;h at 25&#x000B0;C on an orbital incubator at 300&#x02009;rpm, and adjusted to 10<sup>7</sup> bacteria/ml. Aliquots of 50&#x02009;&#x003BC;l containing 10<sup>6</sup> bacteria in HBSS with Ca<sup>2&#x0002B;</sup>/Mg<sup>2&#x0002B;</sup> were placed in flat-bottomed 96-well plates and incubated for 2&#x02009;h with 50&#x02009;&#x003BC;l of pool gilthead seabream serum samples diluted 1/10 in PBS. Moreover, several controls were introduced: blank, without bacteria; positive control, with 10&#x02009;&#x003BC;g/ml gentamicin (0% growth or 100% bactericidal activity); negative control, without serum (100% growth or 0% bactericidal activity); and decomplemented serum control (pretreated at 50&#x000B0;C, 20&#x02009;min) to asses complement-mediated killing. The bactericidal activity of serum samples was determined using a 2,3-bis(2-methoxy-4-nitro-5-sulfophenyl)-2<italic>H</italic>-tetrazolium-5-carboxanilide inner salt (XTT) assay where the yellow tetrazolium salt XTT is reduced to a colored formazan dye by dehydrogenase enzymes in metabolically active cells (<xref ref-type="bibr" rid="B46">46</xref>). The bactericidal activity was expressed as the percentage of bacterial growth inhibition.</p>
</sec>
<sec id="S2-8">
<title>Statistical Analysis</title>
<p>Data were analyzed by the analysis of variance. An unpaired Student&#x02019;s <italic>t</italic>-test was applied to determine differences between two groups. The critical value for statistical significance was taken as <italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05. The asterisks &#x0002A;, &#x0002A;&#x0002A;, and &#x0002A;&#x0002A;&#x0002A; refer to <italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05, <italic>p</italic>&#x02009;&#x0003C;&#x02009;0.01, and <italic>p</italic>&#x02009;&#x0003C;&#x02009;0.001, respectively. All statistical analyses were carried out using the GraphPad Prism 5 program.</p>
</sec>
</sec>
<sec id="S3">
<title>Results</title>
<sec id="S3-1">
<title>EE<sub>2</sub> Increases Vtg Serum Levels But Hardly Affects <italic>il1b</italic> Expression in Head Kidney</title>
<p>The survival of gilthead seabream specimens was 100% during the trial (data not shown). As a control for estrogenic endocrine disruption, serum Vtg levels were analyzed. The results showed that the dietary intake of EE<sub>2</sub> significantly increased serum Vtg levels, as we have previously described for hepatic <italic>Vtg</italic> transcript levels in adult and juvenile gilthead seabream fish treated with EE<sub>2</sub> (<xref ref-type="bibr" rid="B29">29</xref>&#x02013;<xref ref-type="bibr" rid="B31">31</xref>, <xref ref-type="bibr" rid="B47">47</xref>, <xref ref-type="bibr" rid="B48">48</xref>). Vtg levels peaked at the end of the treatment time and then gradually decreased, although they were still altered at 23&#x02009;dpt (Figure <xref ref-type="fig" rid="F1">1</xref>B). Furthermore, when the expression of the gene coding for <italic>il1b</italic> was analyzed in head kidney at 1, 9, and 23&#x02009;dpi to assess the activation of innate immunity in response to the immunization, increased <italic>il1b</italic> transcript levels were only evident 1 and 9&#x02009;dpi as expected (Figure <xref ref-type="fig" rid="F1">1</xref>C). However, dietary EE<sub>2</sub> failed to significantly affect <italic>il1b</italic> mRNA levels (Figure <xref ref-type="fig" rid="F1">1</xref>C).</p>
</sec>
<sec id="S3-2">
<title>EE<sub>2</sub> Affects the Abundance and Proliferation of T Lymphocytes</title>
<p>Both the dietary intake of EE<sub>2</sub> and immunization led to an increase in the percentage of T lymphocytes (i.e., Zap70<sup>&#x0002B;</sup> cells) in head kidney at 1&#x02009;dpi (Figure <xref ref-type="fig" rid="F2">2</xref>A), whereas no statistically significant differences were observed at 9 and 23&#x02009;dpi with any of the treatments (Figures <xref ref-type="fig" rid="F2">2</xref>B,D). Although the percentage of proliferating T lymphocytes (i.e., Zap70<sup>&#x0002B;</sup>/Edu<sup>&#x0002B;</sup> cells) in head kidney was unaffected by the treatments at 9&#x02009;dpi (Figure <xref ref-type="fig" rid="F2">2</xref>C), EE<sub>2</sub> slightly increased the percentage of proliferating T lymphocytes in the head kidney at 23&#x02009;dpi (Figure <xref ref-type="fig" rid="F2">2</xref>E).</p>
<fig id="F2" position="float">
<label>Figure 2</label>
<caption><p>17&#x003B1;-ethinylestradiol (EE<sub>2</sub>) exposure modulates the abundance and proliferation of T lymphocytes. The percentage of Zap70<sup>&#x0002B;</sup> cells <bold>(A,B,D)</bold> and that of proliferating Zap70<sup>&#x0002B;</sup> cells (i.e., EdU<sup>&#x0002B;</sup> cells) <bold>(C,E)</bold> were determined in head kidney leukocytes from untreated and EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food)-treated fish (vaccinated or not) 1 <bold>(A)</bold>, 9 <bold>(B,C)</bold>, and 23 <bold>(D,E)</bold> days after injection and posttreatment (dpi, dpt) by flow cytometry. The sample size was <italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/group/time of sampling. The mean for each group of specimens is shown as a horizontal line. The percentage is given on head kidney R2 region, which contains macrophages, lymphocytes, and precursor cells, excluding acidophilic granulocytes (<xref ref-type="bibr" rid="B49">49</xref>). The asterisks denote statistically significant differences after a Student&#x02019;s <italic>t</italic>-test between the indicated groups. &#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05.</p></caption>
<graphic xlink:href="fimmu-08-00736-g002.tif"/>
</fig>
</sec>
<sec id="S3-3">
<title>EE<sub>2</sub> Alters IgM<sup>&#x0002B;</sup> B-Lymphocyte Populations</title>
<p>Although the percentage of IgM<sup>&#x0002B;</sup> B lymphocytes in the head kidney was slightly higher in EE<sub>2</sub>/immunized fish than in the control at 9&#x02009;dpi/dpt, it was lower in all treated group than in the control at 23&#x02009;dpi/dpt (Figures <xref ref-type="fig" rid="F3">3</xref>A,C,F). Interestingly, although the percentage of IgM<sup>&#x0002B;</sup>/Pax5<sup>&#x02212;</sup> B lymphocytes, i.e., plasma cells, was unaltered at 1 and 23&#x02009;dpi/dpt, it was higher at 9&#x02009;dpi/dpt in EE<sub>2</sub>/non-immunized fish but not in immunized fish treated with EE<sub>2</sub> (Figures <xref ref-type="fig" rid="F3">3</xref>B,D,G). In addition, the dietary intake of EE<sub>2</sub> and immunization resulted in a decreased proliferation of IgM<sup>&#x0002B;</sup> B lymphocytes at 23&#x02009;dpi/dpt (Figures <xref ref-type="fig" rid="F3">3</xref>E,H). Neither immunization nor EE<sub>2</sub> exposure was seen to modulate IgM<sup>&#x0002B;</sup> B-lymphocyte abundance, proliferation, or differentiation in the spleen at 23&#x02009;dpi/dpt (data not shown).</p>
<fig id="F3" position="float">
<label>Figure 3</label>
<caption><p>17&#x003B1;-Ethinylestradiol (EE<sub>2</sub>) exposure promotes the differentiation of IgM<sup>&#x0002B;</sup> B lymphocytes. The percentage of total IgM<sup>&#x0002B;</sup> cells (surface and intracellular staining) in the head kidney <bold>(A,C,F)</bold> and the percentage of IgM<sup>&#x0002B;</sup>/Pax5<sup>&#x02212;</sup> cells <bold>(B,D,G)</bold>, and IgM<sup>&#x0002B;</sup>/EdU<sup>&#x0002B;</sup> cells <bold>(E,H)</bold> of total IgM<sup>&#x0002B;</sup> cells were determined in head kidney leukocytes from untreated and EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food)-treated fish (vaccinated or not) 1 <bold>(A,C,F)</bold>, 9 <bold>(B,D,G)</bold>, and 23 <bold>(E,H)</bold> dpi (1, 9, and 23&#x02009;dpt) by flow cytometry. The sample size was <italic>n</italic>&#x02009;&#x0003D;&#x02009;6 fish/group/time of sampling. The mean for each group of specimens is shown as a horizontal line. The percentage is given on head kidney R2 region, which contains macrophages, lymphocytes, and precursor cells, excluding acidophilic granulocytes (<xref ref-type="bibr" rid="B49">49</xref>). The asterisks denote statistically significant differences after a Student&#x02019;s <italic>t</italic>-test between the indicated groups. &#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05, &#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.01 and &#x0002A;&#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.001.</p></caption>
<graphic xlink:href="fimmu-08-00736-g003.tif"/>
</fig>
</sec>
<sec id="S3-4">
<title>EE<sub>2</sub> Induces the Production of Natural Neutralizing Antibodies</title>
<p>First, the KLH-specific IgM titer was analyzed by ELISA in serum from untreated and EE<sub>2</sub>-treated fish, both control and immunized, at 1, 9, and 23&#x02009;dpi/dpt. Unexpectedly, the dietary intake of EE<sub>2</sub> significantly increased the KLH-specific IgM titer at 1&#x02009;dpi/dpt (Figure <xref ref-type="fig" rid="F4">4</xref>A). However, immunization failed to elicit a specific IgM response at any of the times analyzed (Figures <xref ref-type="fig" rid="F4">4</xref>A&#x02013;C), presumably reflecting the poor primary Ab response to KLH.</p>
<fig id="F4" position="float">
<label>Figure 4</label>
<caption><p>17&#x003B1;-Ethinylestradiol (EE<sub>2</sub>) exposure induces the production of natural antibodies. Keyhole limpet hemocyanin (KLH)-specific <bold>(A&#x02013;C)</bold>, lysozyme-specific <bold>(D&#x02013;G)</bold>, and total <bold>(I&#x02013;L)</bold> IgM titers were determined in the serum by ELISA 1 <bold>(A,E,J)</bold>, 9 <bold>(B,F,K)</bold>, and 23 <bold>(C,G,L)</bold> dpi (1, 9, and 23&#x02009;dpt, respectively) and 40&#x02009;dt <bold>(D,I)</bold> in untreated and EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food)-treated fish (vaccinated or not). In addition, lysozyme-specific <bold>(H)</bold> and total <bold>(M)</bold> IgM titers were determined in the serum of specimens bath exposure for 58&#x02009;days to 0, 5, and 50&#x02009;ng/l EE<sup>2</sup>. The data represent the mean&#x02009;&#x000B1;&#x02009;SEM of absorbance value of the pooled sera of six individual fish. The sample size was&#x02009;&#x0003D;&#x02009;6 fish/group/time of sampling. The asterisks denote statistically significant differences after Student&#x02019;s <italic>t</italic>-test between the untreated and EE<sub>2</sub>-treated fish (vaccinated or not), at each time point. &#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05 and &#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.01.</p></caption>
<graphic xlink:href="fimmu-08-00736-g004.tif"/>
</fig>
<p>These results prompted us to analyze the IgM titer to an unrelated antigen, lysozyme, in the serum of non-immunized fish exposed to EE<sub>2</sub> by different routes (in this case dietary exposure and bath immersion). Strikingly, EE<sub>2</sub> significantly increased lysozyme-specific IgM titers during treatment (40&#x02009;dt) (Figure <xref ref-type="fig" rid="F4">4</xref>D) and posttreatment (1 and 9&#x02009;dpt) (Figures <xref ref-type="fig" rid="F4">4</xref>E,F), but the effect did not last until 23&#x02009;dpt (Figure <xref ref-type="fig" rid="F4">4</xref>G). Similar results were obtained in fish bath-exposed to EE<sub>2</sub> for approximately 2&#x02009;months (Figure <xref ref-type="fig" rid="F4">4</xref>H). The induction of natural antibodies by the administration of EE<sub>2</sub> was further confirmed by determining total serum IgM levels (Figures <xref ref-type="fig" rid="F4">4</xref>I&#x02013;M). Furthermore, EE<sub>2</sub>-induced natural IgM antibodies were not only polyreactive but also neutralizing, since they reacted against the commensal <italic>S. putrefaciens</italic> (Figures <xref ref-type="fig" rid="F5">5</xref>A&#x02013;C) and the pathogen <italic>V. anguillarum</italic> (Figures <xref ref-type="fig" rid="F5">5</xref>D&#x02013;F), inducing the death of the latter (Figures <xref ref-type="fig" rid="F5">5</xref>G,H). In all cases, the natural antibodies show low affinity, since high dilution of serum had to be used to detect them (Figures <xref ref-type="fig" rid="F4">4</xref>&#x02013;<xref ref-type="fig" rid="F6">6</xref>).</p>
<fig id="F5" position="float">
<label>Figure 5</label>
<caption><p>17&#x003B1;-Ethinylestradiol (EE<sub>2</sub>)-induced natural antibodies react against commensals and neutralize pathogens. <bold>(A&#x02013;F)</bold> The natural IgM titers against <italic>Shewanella putrefaciens</italic> or <italic>Vibrio anguillarum</italic> were determined in the serum by ELISA after 40&#x02009;days of treatment <bold>(A,D)</bold> and after 9 <bold>(B,E)</bold> and 23 <bold>(C,F)</bold> dpt in untreated and EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food)-treated fish. The data represent the mean&#x02009;&#x000B1;&#x02009;SEM of absorbance value of pool sera of six individual fish at 1:10 serum dilution. <bold>(G,H)</bold> The bactericidal activity against <italic>V. anguillarum</italic> of the serum of untreated and EE<sub>2</sub> (5&#x02009;&#x003BC;g/g food)-treated fish at 40&#x02009;dt <bold>(G)</bold> and EE<sub>2</sub> (0, 5, and 50&#x02009;ng/l) bath exposure adult fish for 58&#x02009;days <bold>(H)</bold> was determined by an XTT assay. The data represent the mean&#x02009;&#x000B1;&#x02009;SEM of percentage of bacterial activity by pool sera of six individual fish at 1:10 serum dilution. The simple size was&#x02009;&#x0003D;&#x02009;6 fish/group/time of sampling. The asterisks denote statistically significant differences after Student&#x02019;s <italic>t</italic>-test between the untreated and EE<sub>2</sub>-treated fish, at each time point. &#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05; &#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.01; and &#x0002A;&#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.001.</p></caption>
<graphic xlink:href="fimmu-08-00736-g005.tif"/>
</fig>
<fig id="F6" position="float">
<label>Figure 6</label>
<caption><p>G protein-coupled estrogen receptor 1 activation <italic>in vivo</italic> promotes the production of natural antibodies. <bold>(A&#x02013;D)</bold> Lysozyme-specific <bold>(A,C)</bold> and total <bold>(B,D)</bold> IgM titers were determined in the serum by ELISA after 30 and 110&#x02009;days of dietary intake of G1 (0, 2, and 20&#x02009;&#x003BC;g/fish/day) <bold>(A,B,E)</bold>, or 17&#x003B1;-Ethinylestradiol (EE<sub>2</sub>) (5&#x02009;&#x003BC;g/g food) and G1 (5&#x02009;&#x003BC;g/g food) <bold>(C,D)</bold>. The data represent the mean&#x02009;&#x000B1;&#x02009;SEM of absorbance value of the pooled sera from six individual fish at 1:10 serum dilution. The sample size was&#x02009;&#x0003D;&#x02009;6 fish/group/time of sampling. <bold>(E)</bold> The serum bactericidal activity against <italic>Vibrio anguillarum</italic> of fish exposure for 30&#x02009;days to G1 (0, 2, and 20&#x02009;&#x003BC;g/fish/day) was determined by an XTT assay. The data represent the mean&#x02009;&#x000B1;&#x02009;SEM of percentage of bacterial activity by pool sera of six individual fish at 1:10 serum dilution. The sample size was&#x02009;&#x0003D;&#x02009;6 fish/group/time of sampling. The asterisks denote statistically significant differences after Student&#x02019;s <italic>t</italic>-test between the untreated and EE<sub>2</sub>-treated fish, at each time point. &#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.05; &#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.01; and &#x0002A;&#x0002A;&#x0002A;<italic>p</italic>&#x02009;&#x0003C;&#x02009;0.001.</p></caption>
<graphic xlink:href="fimmu-08-00736-g006.tif"/>
</fig>
</sec>
<sec id="S3-5">
<title>GPER1 Signaling Promotes Natural Ab Production</title>
<p>As previous studies demonstrated the key role of estrogen signaling through GPER1 in the regulation of innate and adaptive immunities in gilthead seabream, we next evaluated the effect of GPER1 activation on natural Ab production using the specific agonist G1. The results showed that G1-treated fish had higher lysozyme-specific (Figure <xref ref-type="fig" rid="F6">6</xref>A) and total IgM (Figure <xref ref-type="fig" rid="F6">6</xref>B) serum titers and higher bactericidal activity against <italic>V. anguillarum</italic> at 30&#x02009;dt than the untreated controls (Figure <xref ref-type="fig" rid="F6">6</xref>E). Moreover, the effects of EE<sub>2</sub> and G1 on natural Ab production in fish treated for 110&#x02009;days were similar (Figures <xref ref-type="fig" rid="F6">6</xref>C,D).</p>
</sec>
</sec>
<sec id="S4" sec-type="discussion">
<title>Discussion</title>
<p>The fact that estrogens have a key as modulator role of mammals and fish immune systems is well known (<xref ref-type="bibr" rid="B4">4</xref>, <xref ref-type="bibr" rid="B29">29</xref>&#x02013;<xref ref-type="bibr" rid="B31">31</xref>, <xref ref-type="bibr" rid="B47">47</xref>). However, the effect of estrogens on fish lymphocytes, and in particular, on the production of natural antibodies, is unknown. In this study, we report for the first time the capacity of EE<sub>2</sub> to modulate lymphocyte populations and natural Ab production in teleost fish. We have seen that the dietary intake of EE<sub>2</sub> increased the abundance and proliferation of T lymphocytes in the head kidney of unvaccinated gilthead seabream specimens. In contrast, a reduction in the number of circulating lymphocytes was observed in fathead minnow exposed to potent estrogenic effluents (<xref ref-type="bibr" rid="B50">50</xref>), whereas E<sub>2</sub> bath exposure altered thymus development in European seabass (<xref ref-type="bibr" rid="B51">51</xref>). Unfortunately, the functional consequences of these observations were not investigated.</p>
<p>As regards, IgM<sup>&#x0002B;</sup> B lymphocytes, the dietary intake of EE<sub>2</sub>, did not affect their abundance in the two main lymphomyeloid organs, namely the head kidney and the spleen, confirming previous results (<xref ref-type="bibr" rid="B29">29</xref>, <xref ref-type="bibr" rid="B30">30</xref>). In contrast, another EDC, tamoxifen, was able to increase the number of IgM<sup>&#x0002B;</sup> B lymphocytes in vaccinated fish (<xref ref-type="bibr" rid="B29">29</xref>, <xref ref-type="bibr" rid="B30">30</xref>), suggesting that each EDC may have specific effects in fish adaptive immunity. Thus, it was observed in the present study that dietary EE<sub>2</sub> exposure transiently increased the abundance of plasma cells, i.e., IgM<sup>&#x0002B;</sup>/Pax5<sup>&#x02212;</sup> cells. This suggest that EE<sub>2</sub> is able to modulate B-cell lineage commitment, as Pax5 is (i) expressed from the pro-B cell through mature and activated B-cell stages, (ii) downregulated during terminal differentiation, and (iii) absent at the plasma cell stage in both mammals (<xref ref-type="bibr" rid="B52">52</xref>) and fish (<xref ref-type="bibr" rid="B53">53</xref>).</p>
<p>The most interesting observation in this study is that EE<sub>2</sub>, following dietary or bath exposure, induces the production of low affinity, polyreactive natural antibodies. Although we have previously described several long-lasting effects of dietary EE<sub>2</sub> in specific Ab production (<xref ref-type="bibr" rid="B29">29</xref>, <xref ref-type="bibr" rid="B30">30</xref>), the modulation of natural Ab production by dietary EE<sub>2</sub> disappears by 23&#x02009;dpt. Therefore, the stimulation of natural antibodies by EE<sub>2</sub> coincides with its effect on IgM<sup>&#x0002B;</sup> B-lymphocyte differentiation. Moreover, it was observed that the sera from EE<sub>2</sub>-treated fish manifested an enhanced bactericidal activity, suggesting that natural antibodies are able to effectively neutralize fish pathogens. In mammals, the primary roles of natural antibodies are to confine infection locally, to enhance the IgG response, to play a protective role in autoimmunity, and to take part in homeostasis and clearing of cell debris (<xref ref-type="bibr" rid="B54">54</xref>). Natural antibodies are mostly IgM type and are secreted by the long-lived, self-renewing B1 subset of B cells, which are generated during fetal or neonatal development (<xref ref-type="bibr" rid="B55">55</xref>, <xref ref-type="bibr" rid="B56">56</xref>). Teleost B cells resemble mammalian B1 cells since both of them show phagocytic and microbicidal activities (<xref ref-type="bibr" rid="B57">57</xref>). Although the relevance of natural antibodies in fish is largely unknown, their existence in both cartilaginous and bony fish has been reported (<xref ref-type="bibr" rid="B34">34</xref>&#x02013;<xref ref-type="bibr" rid="B36">36</xref>). More recently, the existence of natural Ab in cod has also been shown even though this species is a poor Ab responder (<xref ref-type="bibr" rid="B32">32</xref>) and lacks CD4 and MHCII (<xref ref-type="bibr" rid="B58">58</xref>). In addition, the opsonization and neutralizing ability of natural antibodies of rainbow trout against <italic>A. salmonicida</italic> has been demonstrated (<xref ref-type="bibr" rid="B37">37</xref>&#x02013;<xref ref-type="bibr" rid="B39">39</xref>).</p>
<p>Although estrogens regulate Ab production, including the production of autoantibodies (<xref ref-type="bibr" rid="B19">19</xref>, <xref ref-type="bibr" rid="B59">59</xref>, <xref ref-type="bibr" rid="B60">60</xref>), their impact on natural Ab production is largely unknown. It has been reported that chronic estrogen administration (31&#x02009;weeks) to mice resulted in increased IgM- and IgG-producing cells (<xref ref-type="bibr" rid="B61">61</xref>). However, the mechanisms involved and whether this effect results in increased natural antibodies titers are unknown. Therefore, to the best of our knowledge, this is the first study showing that estrogens regulate natural Ab production in vertebrates. In addition, this effect is mediated through GPER1 signaling, since the GPER1-specific agonist induces a similar natural Ab response to EE<sub>2</sub>. Our results pave the way for future studies aimed at shedding light on the relevance of estrogens in the protection of fish by natural antibodies, the signaling mechanism involved, including classical nuclear ERs, the impact of natural antibodies and estrogens in the crosstalk between natural antibodies, both IgM and IgT, and microbiota, and the therapeutic potential of estrogen administration to protect fish against infections in aquaculture.</p>
</sec>
<sec id="S5">
<title>Ethics Statement</title>
<p>The experiments described were approved by the Consejer&#x000ED;a de Agua, Agricultura y Medio Ambiente of the Regi&#x000F3;n de Murcia, Spain (approval number A13160507).</p>
</sec>
<sec id="S6" sec-type="author-contributor">
<title>Author Contributions</title>
<p>AG-A and VM conceived and designed the study; MR performed the research; MR, IC, NG-G, MA, JM, AG-A, and VM analyzed the data; and MR, IC, and VM wrote the manuscript with minor contribution from other authors.</p>
</sec>
<sec id="S7">
<title>Conflict of Interest Statement</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>
</body>
<back>
<ack>
<p>We thank I. Fuentes for her excellent technical assistance and Profs. A. E. Toranzo and M. A. Mori&#x000F1;igo for the <italic>V. anguillarum</italic> and <italic>S. putrefasciens</italic> strains, respectively.</p>
</ack>
<fn-group>
<fn fn-type="financial-disclosure">
<p><bold>Funding</bold>. This work was funded with support from the Spanish Ministerio de Econom&#x000ED;a y Competitividad (MINECO) (research grants BIO2014-52655-R to VM and AGL2014-53167-C3-1-R to AG-A and Ph.D. fellowship to MR), all cofunded with Fondos Europeos de Desarrollo Regional/European Regional Development Funds, and by the Fundaci&#x000F3;n S&#x000E9;neca, CARM (19883/GERM/15).</p>
</fn>
</fn-group>
<sec id="S8" sec-type="supplementary-material">
<title>Supplementary Material</title>
<p>The Supplementary Material for this article can be found online at <uri xlink:href="http://journal.frontiersin.org/article/10.3389/fimmu.2017.00736/full&#x00023;supplementary-material">http://journal.frontiersin.org/article/10.3389/fimmu.2017.00736/full&#x00023;supplementary-material</uri>.</p>
<supplementary-material xlink:href="Image_1.JPEG" id="SM1" mimetype="applicationn/JPEG" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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