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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Ecol. Evol.</journal-id>
<journal-title>Frontiers in Ecology and Evolution</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Ecol. Evol.</abbrev-journal-title>
<issn pub-type="epub">2296-701X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fevo.2018.00211</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Ecology and Evolution</subject>
<subj-group>
<subject>Brief Research Report</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Occurrence of Alkaloids in Grass Seeds Symbiotic With Vertically-Transmitted <italic>Epichlo&#x000EB;</italic> Fungal Endophytes and Its Relationship With Antioxidants</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Gundel</surname> <given-names>Pedro E.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x0002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/110850/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Seal</surname> <given-names>Charlotte E.</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/320652/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Biganzoli</surname> <given-names>Fernando</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/569668/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Molina-Montenegro</surname> <given-names>Marco A.</given-names></name>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
<xref ref-type="aff" rid="aff5"><sup>5</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>V&#x000E1;zquez-de-Aldana</surname> <given-names>Beatriz R.</given-names></name>
<xref ref-type="aff" rid="aff6"><sup>6</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/352565/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Zabalgogeazcoa</surname> <given-names>I&#x000F1;igo</given-names></name>
<xref ref-type="aff" rid="aff6"><sup>6</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/452443/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Bush</surname> <given-names>Lowell P.</given-names></name>
<xref ref-type="aff" rid="aff7"><sup>7</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Mart&#x000ED;nez-Ghersa</surname> <given-names>Mar&#x000ED;a A.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Ghersa</surname> <given-names>Claudio M.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>IFEVA, Facultad de Agronom&#x000ED;a, Universidad de Buenos Aires, CONICET</institution>, <addr-line>Buenos Aires</addr-line>, <country>Argentina</country></aff>
<aff id="aff2"><sup>2</sup><institution>Department of Comparative Plant and Fungal Biology, Royal Botanic Gardens</institution>, <addr-line>Kew</addr-line>, <country>United Kingdom</country></aff>
<aff id="aff3"><sup>3</sup><institution>Departamento de M&#x000E9;todos Cuantitativos y Sistemas de Informaci&#x000F3;n, Facultad de Agronom&#x000ED;a, Universidad de Buenos Aires</institution>, <addr-line>Buenos Aires</addr-line>, <country>Argentina</country></aff>
<aff id="aff4"><sup>4</sup><institution>CEMF, Instituto de Ciencias Biol&#x000F3;gicas, Universidad de Talca</institution>, <addr-line>Talca</addr-line>, <country>Chile</country></aff>
<aff id="aff5"><sup>5</sup><institution>CEAZA, Universidad Cat&#x000F3;lica del Norte</institution>, <addr-line>Coquimbo</addr-line>, <country>Chile</country></aff>
<aff id="aff6"><sup>6</sup><institution>Instituto de Recursos Naturales y Agrobiolog&#x000ED;a de Salamanca (IRNASA-CSIC)</institution>, <addr-line>Salamanca</addr-line>, <country>Spain</country></aff>
<aff id="aff7"><sup>7</sup><institution>Department of Plant &#x00026; Soil Sciences, University of Kentucky</institution>, <addr-line>Lexington, KY</addr-line>, <country>United States</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Margot Schulz, Universit&#x000E4;t Bonn, Germany</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Benjamin Fuchs, Freie Universit&#x000E4;t Berlin, Germany; Chunjie Li, Lanzhou University, China</p></fn>
<corresp id="c001">&#x0002A;Correspondence: Pedro E. Gundel <email>gundel&#x00040;agro.uba.ar</email></corresp>
<fn fn-type="other" id="fn001"><p>This article was submitted to Chemical Ecology, a section of the journal Frontiers in Ecology and Evolution</p></fn></author-notes>
<pub-date pub-type="epub">
<day>11</day>
<month>12</month>
<year>2018</year>
</pub-date>
<pub-date pub-type="collection">
<year>2018</year>
</pub-date>
<volume>6</volume>
<elocation-id>211</elocation-id>
<history>
<date date-type="received">
<day>08</day>
<month>10</month>
<year>2018</year>
</date>
<date date-type="accepted">
<day>27</day>
<month>11</month>
<year>2018</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x000A9; 2018 Gundel, Seal, Biganzoli, Molina-Montenegro, V&#x000E1;zquez-de-Aldana, Zabalgogeazcoa, Bush, Mart&#x000ED;nez-Ghersa and Ghersa.</copyright-statement>
<copyright-year>2018</copyright-year>
<copyright-holder>Gundel, Seal, Biganzoli, Molina-Montenegro, V&#x000E1;zquez-de-Aldana, Zabalgogeazcoa, Bush, Mart&#x000ED;nez-Ghersa and Ghersa</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>Host organisms can acquire new functional traits through symbiosis. Seed-transmitted <italic>Epichlo&#x000EB;</italic> fungal endophytes are known to protect host plants against herbivores and increase tolerance to abiotic stresses by alkaloids and antioxidants, respectively (currencies of mutualism). Whereas, alkaloids are fungal products with demonstrated effects at plant vegetative stage, few studies have focused on alkaloids in seeds. We assessed the occurrence of fungal alkaloids and determined their concentrations in seeds of two host grasses, <italic>Festuca rubra</italic> and <italic>Lolium multiflorum</italic>. Then, we sought for a relationship with the antioxidants tocochromanols and glutathione, which are involved in the control of oxidative stress. Different alkaloids were detected depending on the species and plant genotype. Most notably, loline alkaloids were not detected in <italic>F. rubra</italic> seeds, whereas ergovaline and peramine were absent in <italic>L. multiflorum</italic>. In <italic>F. rubra</italic>, ergovaline concentration was dependent on the maternal line in interaction with the production year, diminishing in seeds after 1 year of storage. The exposure of <italic>L. multiflorum</italic> plants to ozone had no effect on the seed concentration of lolines. There was a significant positive relationship between the concentrations of ergovaline and tocochromanols in both species, and between ergovaline concentration and E<sub>GSSG/2GSH</sub> (glutathione half-cell reduction potential) in RAB maternal line of <italic>F. rubra</italic>. These results suggest that alkaloid and antioxidants have a close association in seeds of host grasses, and that the alkaloid bioactivity could be related with the antioxidant capacity to control stress. This has important implications for the ecology of partner species, thus supporting its consideration for further research.</p></abstract>
<kwd-group>
<kwd>grass-endophyte symbiosis</kwd>
<kwd>secondary compounds</kwd>
<kwd>defensive mutualism</kwd>
<kwd>currency of mutualism</kwd>
<kwd>seed quality</kwd>
</kwd-group>
<counts>
<fig-count count="1"/>
<table-count count="1"/>
<equation-count count="0"/>
<ref-count count="55"/>
<page-count count="7"/>
<word-count count="5787"/>
</counts>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="s1">
<title>Introduction</title>
<p>Host organisms can acquire new functional traits through symbiosis (Kiers and West, <xref ref-type="bibr" rid="B30">2015</xref>). In the symbiosis between cool-season grasses (Subfamily Po&#x000F6;ideae) and <italic>Epichlo&#x000EB;</italic> fungal endophytes (Clavicipitaceae) (reviewed by Clay and Schardl, <xref ref-type="bibr" rid="B5">2002</xref>), the high prevalence of symbiotic individuals in populations has been ascribed to both an endophyte-mediated resistance to herbivory by alkaloids and tolerance to abiotic stress by antioxidants, known as the &#x0201C;currencies of the mutualism&#x0201D; (Schardl et al., <xref ref-type="bibr" rid="B41">2007</xref>; Hamilton and Bauerle, <xref ref-type="bibr" rid="B22">2012</xref>). Nonetheless, the effects of fungal endophytes on host plant fitness can vary depending to partners&#x00027; species and genotypes, and as a result of the ecological context (Clay and Schardl, <xref ref-type="bibr" rid="B5">2002</xref>; Saikkonen et al., <xref ref-type="bibr" rid="B40">2013</xref>).</p>
<p>Seeds are critical to the grass-endophyte symbiosis as fungus carriers from one generation to the next (Gundel et al., <xref ref-type="bibr" rid="B18">2011a</xref>, <xref ref-type="bibr" rid="B19">2017</xref>). The seed is the plant structure with the greatest fungus/plant biomass ratio which stores fungal alkaloids (TePaske et al., <xref ref-type="bibr" rid="B46">1993</xref>; Justus et al., <xref ref-type="bibr" rid="B29">1997</xref>; V&#x000E1;zquez-de-Aldana et al., <xref ref-type="bibr" rid="B49">2003</xref>). The profile and concentration of alkaloids varies greatly responding to factors such as species identities, plant tissue/stage, and growth conditions (Bush et al., <xref ref-type="bibr" rid="B4">1997</xref>; Faeth et al., <xref ref-type="bibr" rid="B9">2002</xref>; Rasmussen et al., <xref ref-type="bibr" rid="B38">2007</xref>; Mace et al., <xref ref-type="bibr" rid="B34">2014</xref>). Production of alkaloids can be triggered by herbivory (Sullivan et al., <xref ref-type="bibr" rid="B45">2007</xref>; Fuchs et al., <xref ref-type="bibr" rid="B12">2017a</xref>), although it remains unknown whether alkaloids accumulate in seeds as a consequence (Gundel et al., <xref ref-type="bibr" rid="B19">2017</xref>). Endophyte presence in seeds is deemed to deter granivorous animals (Uchitel et al., <xref ref-type="bibr" rid="B47">2011</xref>), an effect that may be extended to protect seedlings from herbivores (Stewart, <xref ref-type="bibr" rid="B44">1985</xref>; Czarnoleski et al., <xref ref-type="bibr" rid="B6">2010</xref>). However, the endophyte-conferred resistance in seedlings may be ineffective (Lewis and Clements, <xref ref-type="bibr" rid="B33">1986</xref>) because of a very low alkaloid level (Dymock et al., <xref ref-type="bibr" rid="B8">1989</xref>) and/or because of fungus viability loss. Since the alkaloids are present in the seed, their loss rate could be independent of the endophyte viability (Stewart, <xref ref-type="bibr" rid="B44">1985</xref>), but dependent on seed quality parameters.</p>
<p>A potentiated antioxidant system is proposed as a mechanism by which symbiotic plants usually exhibit higher tolerance to abiotic stress (White and Torres, <xref ref-type="bibr" rid="B53">2010</xref>; Hamilton et al., <xref ref-type="bibr" rid="B23">2012</xref>). The presence of endophytes in seeds may be related to a higher antioxidant capacity. For example, endophytic seeds of <italic>F. rubra</italic> (RAB maternal line) had a higher concentration of the lipid-soluble antioxidants &#x003B1;-tocopherol and &#x003B1;-tocotrienol than non-endophytic seeds (Gundel et al., <xref ref-type="bibr" rid="B15">2012</xref>), that may contribute to stabilize membrane functionality (Falk and Munn&#x000E9;-Bosch, <xref ref-type="bibr" rid="B10">2010</xref>). In contrast, the glutathione half-cell reduction potential (E<sub>GSSG/2GSH</sub>), a marker of the cellular redox state that shifts toward positive values with a loss of seed viability (Kranner et al., <xref ref-type="bibr" rid="B31">2010</xref>; Seal et al., <xref ref-type="bibr" rid="B43">2010</xref>), was more positive in endophytic compared to non-endophytic seeds of <italic>L. multiflorum</italic> (Gundel et al., <xref ref-type="bibr" rid="B20">2015</xref>). However, the presence of an endophyte does not always contribute toward viability. Whereas endophytes enhance the survival of germinating seeds in <italic>L. multiflorum</italic> and <italic>F. rubra</italic> (Gundel et al., <xref ref-type="bibr" rid="B16">2006</xref>, <xref ref-type="bibr" rid="B21">2011b</xref>), they had a negative effect on seed viability under both cool-dry and wet-warm storage conditions (Gundel et al., <xref ref-type="bibr" rid="B15">2012</xref>, <xref ref-type="bibr" rid="B20">2015</xref>). Therefore, endophyte effects on seeds may differ depending on the plant species, seed quality, seed storage conditions and antioxidant.</p>
<p>With growing evidence beginning to elucidate the ecological functions of alkaloids and antioxidants in the grass-endophyte symbiosis independently, it is striking that any relationship between these two compounds is yet to be explored. Here, we first present data on the concentration of different fungal alkaloids in seeds of two grass species, <italic>F. rubra</italic> and <italic>L. multiflorum</italic>. With the aim to have within-species variation in the profile and level of alkaloids, we analyzed seeds produced by different plants and years in the case of <italic>F. rubra</italic>, and produced in atmospheres with high and low concentration of ozone in the case of <italic>L. multiflorum</italic>. Ozone is a stress factor associated to tropospheric contamination that depending on the intensity, can cause growth loses or induced resistance in plants by activating the antioxidant system (Men&#x000E9;ndez et al., <xref ref-type="bibr" rid="B35">2009</xref>). Then, we explored the existence of relationships between alkaloids and antioxidants. A relationship between these currencies of mutualism could have significant ecological consequences: a negative relationship elicited by different factors (i.e., antioxidants to abiotic stress and alkaloids to herbivory) would mean that the occurrence of a given factor (e.g., stress factor) would render the plant susceptible to another factor (e.g., herbivory) and <italic>vice-versa</italic>. Alternatively, a positive relationship would indicate that a lower concentration of antioxidants would imply a lower concentration of alkaloids and consequently seeds may be more prone to herbivory.</p>
</sec>
<sec sec-type="materials and methods" id="s2">
<title>Materials and Methods</title>
<sec>
<title>Seed Material</title>
<sec>
<title>Festuca rubra</title>
<p>We used half-sib seeds produced by clones of three individual plants (RAB, SAN, and PEN) infected by <italic>Epichlo&#x000EB; festucae</italic>, the common fungal endophyte of fine fescues (Zabalgogeazcoa et al., <xref ref-type="bibr" rid="B55">2006</xref>; Dirihan et al., <xref ref-type="bibr" rid="B7">2016</xref>). The original plants were collected from three sites separated by at least 40 km, in dehesa grasslands of Salamanca, Spain. <italic>Epichlo&#x000EB;</italic> fungal endophytes have shown to affect different growth attributes and biochemical variables of those maternal lines (Zabalgogeazcoa et al., <xref ref-type="bibr" rid="B55">2006</xref>; V&#x000E1;zquez-de-Aldana et al., <xref ref-type="bibr" rid="B48">2013</xref>). Each plant was split into three ramets, randomly transplanted in a field plot on a research farm (IRNASA-CSIC, Salamanca, Spain; Gundel et al., <xref ref-type="bibr" rid="B21">2011b</xref>). The seeds were produced in 3 years: 2009, 2010, and 2011, and stored for 24, 12, and 1 month, respectively, under dry and cold (10&#x000B0;C) conditions. In 2012, seed lots produced by each maternal line and ramet (<italic>n</italic> &#x0003D; 2; since a ramet was lost in two of the maternal lines, we decided to used just 2 ramets each) in each year, were processed for alkaloid determination.</p>
</sec>
<sec>
<title>Lolium multiflorum</title>
<p>The original population was collected in a semi-natural grassland (Pampa Region, Argentina) where populations usually present high frequency of endophyte-infected plants (Gundel et al., <xref ref-type="bibr" rid="B14">2009</xref>). In 2011, <italic>L. multiflorum</italic> plants with and without <italic>Epichlo&#x000EB; occultans</italic> were exposed to a high concentration of tropospheric ozone (Gundel et al., <xref ref-type="bibr" rid="B20">2015</xref>). At pre-anthesis, 64 plants growing independently in 2 L pots were placed in any of the 8 open-top chambers with either high (&#x02248;120 ppb) or low (&#x0003C; 10 ppb) levels of ozone for 5 days (2 h at noon). Seeds produced by all the plants within an open-top chamber were pooled and stored in dry and cold conditions for 3 months. In 2012, seed lots produced by all the plants within a chamber were pooled (<italic>n</italic> &#x0003D; 4 for each ozone treatment) and were processed for alkaloid determination.</p>
</sec>
</sec>
<sec>
<title>Alkaloid Analysis</title>
<p>Concentration of the ergopetine alkaloid, ergovaline (Chemical name: 12&#x02032;-Hydroxy-2&#x02032;-methyl-5&#x02032;alpha-(1-methylethyl)-ergotaman-3&#x02032;,6&#x02032;,18-trione) was quantified by HPLC following a modification of the methods described by Hill et al. (<xref ref-type="bibr" rid="B25">1993</xref>) and Yue et al. (<xref ref-type="bibr" rid="B54">2000</xref>). A 1.0 g ground seed sample was extracted in 20 ml of CHCl<sub>3</sub> and 1 ml of 0.5 mM NaOH for 2 h. A solution (10 &#x003BC;g mL<sup>&#x02212;1</sup>) of ergotamine ditartrate (Sigma-Aldrich) was added as internal standard. The mixture was vacuum-filtered through Whatman n&#x000B0; 2 filter paper and a 10 ml aliquot of filtrate was passed through a 500 mg Ergosil (Analtech; Newark, USA) solid-phase column preconditioned with CHCl<sub>3</sub>. Plant pigments were removed with 5 ml of chloroform:acetone (1:3). The sample was eluted with 2 ml of methanol and vacuum concentrated, redissolved in 1 ml of methanol, and filtered through a 0.22 &#x003BC;m nylon filter. Ergovaline quantification in extracts was performed in a HPLC system (Waters 2690) with an Xterra MS C18 Waters column (4.6 &#x000D7; 100 mm) and a fluorescence detector (Waters 2475) &#x003BB;<sub>exc</sub> &#x0003D; 250 nm and &#x003BB;<sub>em</sub> &#x0003D; 420 nm. The mobile phase was acetonitrile and 0.01M ammonium acetate with a gradient flow of 0.8 ml min<sup>&#x02212;1</sup>.</p>
<p>Peramine (Chemical name: 2-[3-(2-methyl-1-oxopyrrolo[1,2-a]pyrazin-3-yl)propyl]guanidine) was determined using the HPLC method described by Barker et al. (<xref ref-type="bibr" rid="B1">1993</xref>) and Yue et al. (<xref ref-type="bibr" rid="B54">2000</xref>). A freeze-dried and ground sample (100 mg) was extracted in 3 ml of 30% isopropanol for 30 min at 90&#x000B0;C. The mixture was centrifuged and the extract was passed through a preconditioned Varian Bond Elut carboxylic acid (CBA) column packed with 100 mg of adsorbent. After a wash of the column with 1&#x02013;2 ml of methanol, peramine was eluted with 1 ml of 5% formic acid in 80% aqueous methanol. The extract was filtered through a 0.22 &#x003BC;m nylon filter and chromatographed in a Waters 2690 system with a Nova Pak C18 Waters column (3.9 &#x000D7; 150 mm). The isocratic mobile phase consisted of 18% (v/v) acetonitrile in a guanidine carbonate (10 mM)-formic acid buffer. Detection was performed with a Photodiode Array Detector (Waters 2996) at 280 nm. For more details see V&#x000E1;zquez-de-Aldana et al. (<xref ref-type="bibr" rid="B51">2010</xref>).</p>
<p>Pyrrolizidine alkaloids (NANL: N-acetilnorloline, NFL: N-formylloline, and NAL: N-acetylloline) [Chemical name: (6r,7r,7as)-n-methylhexahydro-1h-1,6-epoxypyrrolizin-7-amine] were extracted from powdered plant material with ethanol:methylene chloride (4:1, v/v) containing internal standard quinoline and sodium bicarbonate following protocol in Helander et al. (<xref ref-type="bibr" rid="B24">2016</xref>). Individual alkaloids were resolved and quantified by GC equipped with FID detector. Chromatographic conditions were 15 m &#x000D7; 0.53 mm DB5 column with initial oven temperature of 70&#x000B0;C increased to 160&#x000B0;C at 45&#x000B0;C min<sup>&#x02212;1</sup>, held for 5 min and increased to 290 at 45 min<sup>&#x02212;1</sup> and held for 7 min.</p>
</sec>
<sec>
<title>Antioxidant Analysis</title>
<p>In searching for relationships with the alkaloids, we focussed on total tocochromanols (that comprises several independent compounds of tocopherols and tocotrienols) and the glutathione half-cell reduction potential (E<sub>GSSG/2GSH</sub>) that were found to be higher in concentration (tocochromanols) or more negative (E<sub>GSSG/2GSH</sub>) in the presence of seed endophytes (Gundel et al., <xref ref-type="bibr" rid="B15">2012</xref>, <xref ref-type="bibr" rid="B20">2015</xref>). Published values were taken from our earlier works which analyzed the same seed lots (Gundel et al., <xref ref-type="bibr" rid="B15">2012</xref>, <xref ref-type="bibr" rid="B20">2015</xref>).</p>
</sec>
<sec>
<title>Data Analysis</title>
<p>We built generalized least squares models (gls function, nlme package, Pinheiro et al., <xref ref-type="bibr" rid="B36">2017</xref>) in R (R. Core Team, <xref ref-type="bibr" rid="B39">2017</xref>) to test the effects of the different variation factors on the concentration of alkaloids in seeds. In the case of <italic>F. rubra</italic>, the alkaloid was ergovaline while the factors were maternal line (PEN and RAB; SAN was not included in the analysis since we did not detect ergovaline) and production year (2009, 2010, and 2011). In the case of <italic>L. multiflorum</italic>, the alkaloids were &#x0201C;total lolines&#x0201D; and derivatives (NANL, NFL, and NAL) as affected by the maternal exposure to ozone. When necessary, we also modeled variance heterogeneity of errors with the option weights. Significance was tested with Type II Likelihood Ratio Test (car package; Fox and Weisberg, <xref ref-type="bibr" rid="B11">2011</xref>). Finally, we tested the relationship between the alkaloids (ergovaline and total lolines) with the total tocochromanols and the E<sub>GSSG/2GSH</sub> in the seeds.</p>
</sec>
</sec>
<sec sec-type="results" id="s3">
<title>Results</title>
<sec>
<title>Festuca rubra</title>
<p>Loline alkaloids were not detected in any of the assessed <italic>F. rubra</italic> seed. The alkaloid peramine was only present in seeds of the maternal line PEN produced in 2010 (3.12 &#x000B1; 0.01 &#x003BC;g.g<sup>&#x02212;1</sup>) and 2011 (5.68 &#x000B1; 0.01 &#x003BC;g.g<sup>&#x02212;1</sup>; Table <xref ref-type="table" rid="T1">1</xref>).</p>
<table-wrap position="float" id="T1">
<label>Table 1</label>
<caption><p>Concentration of fungal alkaloids in endophyte-symbiotic seeds of <italic>Festuca rubra</italic> and <italic>Lolium multiflorum</italic> as affected by &#x0201C;maternal line and production year&#x0201D;, and &#x0201C;maternal exposure to ozone,&#x0201D; respectively.</p></caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th valign="top" align="left"><bold>Species</bold></th>
<th valign="top" align="center" colspan="2" style="border-bottom: thin solid #000000;"><bold>Variation factor</bold></th>
<th valign="top" align="center" colspan="3" style="border-bottom: thin solid #000000;"><bold>Alkaloid</bold></th>
</tr>
<tr style="border-bottom: thin solid #000000;">
<th/>
<th valign="top" align="left"><bold>Maternal line</bold></th>
<th valign="top" align="center"><bold>Production year</bold></th>
<th valign="top" align="center"><bold>Ergovaline</bold></th>
<th valign="top" align="center"><bold>Lolines</bold></th>
<th valign="top" align="center"><bold>Peramine</bold></th>
</tr>
<tr>
<th/>
<th/>
<th/>
<th valign="top" align="center"><bold>(&#x003BC;g.g<sup><bold>&#x02212;1</bold></sup> DM)</bold></th>
<th valign="top" align="center"><bold>(&#x003BC;g.g<sup><bold>&#x02212;1</bold></sup> DM)</bold></th>
<th valign="top" align="center"><bold>(&#x003BC;g.g<sup><bold>&#x02212;1</bold></sup> DM)</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left"><italic>Festuca rubra</italic></td>
<td valign="top" align="left">SAN</td>
<td valign="top" align="center">2009</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
</tr>
<tr>
<td/>
<td/>
<td valign="top" align="center">2010</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
</tr>
<tr>
<td/>
<td/>
<td valign="top" align="center">2011</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
</tr>
<tr>
<td/>
<td valign="top" align="left">PEN</td>
<td valign="top" align="center">2009</td>
<td valign="top" align="center">0.08 (0.00)</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
</tr>
<tr>
<td/>
<td/>
<td valign="top" align="center">2010</td>
<td valign="top" align="center">0.01 (0.00)</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">3.12 (0.01)</td>
</tr>
<tr>
<td/>
<td/>
<td valign="top" align="center">2011</td>
<td valign="top" align="center">0.04 (0.00)</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">5.68 (0.01)</td>
</tr>
<tr>
<td/>
<td valign="top" align="left">RAB</td>
<td valign="top" align="center">2009</td>
<td valign="top" align="center">0.43 (0.01)</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
</tr>
<tr>
<td/>
<td/>
<td valign="top" align="center">2010</td>
<td valign="top" align="center">0.80 (0.02)</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
</tr>
<tr>
<td/>
<td/>
<td valign="top" align="center">2011</td>
<td valign="top" align="center">0.72 (0.02)</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">n.d.</td>
</tr>
<tr>
<td/>
<td valign="top" align="left" colspan="2"><bold>Maternal ozone exposure</bold></td>
</tr>
<tr>
<td valign="top" align="left"><italic>Lolium multiflorum</italic></td>
<td valign="top" align="left" colspan="2">high (&#x02248;120 ppb)</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">1440.75 (226.00)</td>
<td valign="top" align="center">n.d.</td>
</tr>
<tr>
<td/>
<td valign="top" align="left" colspan="2">low (&#x0003C; 10 ppb)</td>
<td valign="top" align="center">n.d.</td>
<td valign="top" align="center">1426.50 (171.74)</td>
<td valign="top" align="center">n.d.</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p><italic>Values are mean (SE); n &#x0003D; 2, and n &#x0003D; 4, for F. rubra and L. multiflorum, respectively</italic>.</p>
</table-wrap-foot>
</table-wrap>
<p>Ergovaline was not detected in seeds from the maternal line SAN in any of the production years (Table <xref ref-type="table" rid="T1">1</xref>). The concentration of ergovaline in seeds of the other two maternal lines was found dependent on production year (<italic>X</italic><inline-formula><mml:math id="M1"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 302.870, <italic>P</italic> &#x0003C; 0.001). The concentration in seeds of RAB was 15-fold higher in comparison to that of PEN with a mean difference across production years of 0.61 &#x003BC;g.g<sup>&#x02212;1</sup> (Table <xref ref-type="table" rid="T1">1</xref>).</p>
<p>Ergovaline concentration was related to tocochromanol concentrations but varied between maternal lines (<italic>X</italic><inline-formula><mml:math id="M2"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 20.492, <italic>P</italic> &#x0003C; 0.001). For the RAB lineage, a significant positive relationship between the alkaloid and tocochromanol concentrations was apparent, although this relationship was not related with the production year (<italic>X</italic><inline-formula><mml:math id="M3"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 0.003, <italic>P</italic> &#x0003D; 0.956; Figure <xref ref-type="fig" rid="F1">1A</xref>). The relationship between alkaloid and tocochromanol concentration was not significant in PEN.</p>
<fig id="F1" position="float">
<label>Figure 1</label>
<caption><p>(Upper) Relationship between the concentration of the alkaloid ergovaline and antioxidant (total) tocochromanols <bold>(A)</bold> and the glutathione half-cell reduction potential (E<sub>GSSG/2GSH</sub>) <bold>(B)</bold> in seeds of two maternal lines (PEN and RAB, white and gray symbols, respectively) of <italic>Festuca rubra</italic> symbiotic with the fungal endophyte <italic>Epichlo&#x000EB; festucae</italic>, produced in three different years: 2009 (squares), 2010 (circles), and 2011 (triangles). Regression lines and coefficient of determinations are only shown when significant (<italic>P</italic> &#x0003C; 0.05) and are calculated for a given data set (e.g., RAB). (Lower) Relationship between the concentration of loline alkaloids and antioxidant (total) tocochromanols <bold>(C)</bold> and the glutathione half-cell reduction potential (E<sub>GSSG/2GSH</sub>) <bold>(D)</bold> in seeds produced by <italic>Lolium multiflorum</italic> plants symbiotic with the fungal endophyte <italic>Epichlo&#x000EB; occultans</italic> exposed to high (&#x02248;120 ppb, gray diamonds) or low (&#x0003C; 10 ppb, white diamonds) ground-level ozone. Since there was no effect of ozone, the regression line and coefficient of determination correspond to the whole data set and is significant at <italic>P</italic> &#x0003C; 0.05.</p></caption>
<graphic xlink:href="fevo-06-00211-g0001.tif"/>
</fig>
<p>Independently of the year (<italic>X</italic><inline-formula><mml:math id="M4"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 2.065, <italic>P</italic> &#x0003D; 0.151) but influenced by the maternal line (<italic>X</italic><inline-formula><mml:math id="M5"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 37.944, <italic>P</italic> &#x0003C; 0.001), the concentration of ergovaline was negatively related to E<sub>GSSG/2GSH</sub> for RAB but positively related for PEN (Figure <xref ref-type="fig" rid="F1">1B</xref>).</p>
</sec>
<sec>
<title>Lolium multiflorum</title>
<p>Neither ergovaline nor peramine were detected in any of the <italic>L. multiflorum</italic> seed lots (Table <xref ref-type="table" rid="T1">1</xref>).</p>
<p>The exposure of mother plants to ozone did not affect either the concentration of total lolines in the seed (<italic>X</italic><inline-formula><mml:math id="M6"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 0.003, <italic>P</italic> &#x0003D; 0.961; Table <xref ref-type="table" rid="T1">1</xref>) nor that of the lolines individually (NANL: <italic>X</italic><inline-formula><mml:math id="M7"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 0.820, <italic>P</italic> &#x0003D; 0.365, NFL: <italic>X</italic><inline-formula><mml:math id="M8"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 0.046, <italic>P</italic> &#x0003D; 0.831, and NAL: <italic>X</italic><inline-formula><mml:math id="M9"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 0.001, <italic>P</italic> &#x0003D; 0.974). The average concentration of each individual loline alkaloid in seeds produced by mother plants treated and non-treated with ozone was 254.87 &#x000B1; 20.84, 1147.12 &#x000B1; 113.43, and 31.625 &#x000B1; 3.49 (mean &#x000B1; SE; &#x003BC;g.g<sup>&#x02212;1</sup> DM) for NANL, NFL, and NAL, respectively.</p>
<p>A significant positive relationship between the concentration of lolines and tocochromanols (<italic>X</italic><inline-formula><mml:math id="M10"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 11.693, <italic>P</italic> &#x0003D; 0.001) was independent of mother plants exposure to ozone (<italic>X</italic><inline-formula><mml:math id="M11"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 2.773, <italic>P</italic> &#x0003D; 0.096; Figure <xref ref-type="fig" rid="F1">1C</xref>). There was no relationship between loline concentration and E<sub>GSSG/2GSH</sub> (<italic>X</italic><inline-formula><mml:math id="M12"><mml:msubsup><mml:mrow></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mn>2</mml:mn></mml:mrow></mml:msubsup></mml:math></inline-formula> &#x0003D; 0.133, <italic>P</italic> &#x0003D; 0.715; Figure <xref ref-type="fig" rid="F1">1D</xref>).</p>
</sec>
</sec>
<sec sec-type="discussion" id="s4">
<title>Discussion</title>
<p>Here we showed that, despite variability accounted for by genotype and species identity and the environmental conditions of seed production, seeds are carriers of fungal alkaloids, and the concentration may be related with the antioxidants system of the seeds. Because antioxidants are related to seed quality and functionality (Kranner et al., <xref ref-type="bibr" rid="B31">2010</xref>; Seal et al., <xref ref-type="bibr" rid="B43">2010</xref>), they may also be involved in the control of endophyte longevity (Gundel et al., <xref ref-type="bibr" rid="B15">2012</xref>, <xref ref-type="bibr" rid="B20">2015</xref>) and alkaloids bioactivity. Although more studies are certainly required, the two currencies of mutualism (Schardl et al., <xref ref-type="bibr" rid="B41">2007</xref>; Hamilton and Bauerle, <xref ref-type="bibr" rid="B22">2012</xref>) appear as fundamental but interactive players for the ecological fate of the symbiotic unit (i.e., the seed). By joining host grass life cycle, fungal endophytes multiply and disperse through the seed (Gundel et al., <xref ref-type="bibr" rid="B18">2011a</xref>). Thus, seeds are a crucial structure to protect (Gundel et al., <xref ref-type="bibr" rid="B19">2017</xref>).</p>
<p>The alkaloid ergovaline is mainly known due to its toxicity on mammals (Bush et al., <xref ref-type="bibr" rid="B4">1997</xref>; Saikkonen et al., <xref ref-type="bibr" rid="B40">2013</xref>), although it can also be effective in deterring herbivorous insects (Potter et al., <xref ref-type="bibr" rid="B37">2008</xref>). The concentration of the alkaloid ergovaline varies greatly among plant species, genotypes and tissues (Schardl et al., <xref ref-type="bibr" rid="B42">2013</xref>; Mace et al., <xref ref-type="bibr" rid="B34">2014</xref>). A great variation was previously shown between plants (0&#x02013;0.47 &#x003BC;g.g<sup>&#x02212;1</sup>) in stems and leaves of <italic>F. rubra</italic> (V&#x000E1;zquez-de-Aldana et al., <xref ref-type="bibr" rid="B50">2007</xref>, <xref ref-type="bibr" rid="B51">2010</xref>). In our study, the concentrations of ergovaline in seeds were similar to those found in plant vegetative tissues in Italian ecotypes (Jensen et al., <xref ref-type="bibr" rid="B28">2007</xref>) but lower than those from Switzerland (Leuchtmann et al., <xref ref-type="bibr" rid="B32">2000</xref>). An ergovaline concentration of 0.40 &#x003BC;g.g<sup>&#x02212;1</sup> is considered a critical threshold in cattle diets above which symptoms of toxicosis can be observed (Bony and Delatour, <xref ref-type="bibr" rid="B3">2001</xref>). Although much lower than the concentration found in seeds of <italic>Schedonorus arundinaceus</italic> (1.1&#x02013;4.4 &#x003BC;g.g<sup>&#x02212;1</sup>; TePaske et al., <xref ref-type="bibr" rid="B46">1993</xref>), the seeds produced by the RAB plants exhibited seed alkaloid concentrations higher than the toxicosis threshold (from 0.41 to 0.83 &#x003BC;g.g<sup>&#x02212;1</sup>), being probably effective in deterring small rodents and herbivorous insects. Additionally, the observed variation among plants in alkaloid profile and concentration would indicate potential for populations to respond to selection pressures exerted by herbivory.</p>
<p>A similar variation has been observed in plant species associated with loline-producing endophytes. Concentration of lolines in <italic>L. multiflorum</italic> seeds showed high variability (880&#x02013;1,922 &#x003BC;g.g<sup>&#x02212;1</sup>) but it was on average significantly higher (&#x02248;1430.63 &#x003BC;g.g<sup>&#x02212;1</sup>) compared to the concentration found in dry seed of the same species previously (TePaske et al., <xref ref-type="bibr" rid="B46">1993</xref>) (&#x02248;52 &#x003BC;g.g<sup>&#x02212;1</sup>). However, the concentrations of lolines we found are slightly lower to that reported for <italic>F. pratensis</italic> dry seeds (&#x02248;1,801 &#x003BC;g.g<sup>&#x02212;1</sup>) by Justus et al. (<xref ref-type="bibr" rid="B29">1997</xref>). The fungal endophytes of these two last grass species, <italic>E. occultans</italic> and <italic>E. uncinatum</italic>, are well-known as loline-producing endophytes and the latter one is known for its high production level (Schardl et al., <xref ref-type="bibr" rid="B41">2007</xref>). Since lolines are insect deterrents and non-toxic for vertebrates, forage species infected with those endophytes such as <italic>L. multiflorum, L. rigidum</italic>, and <italic>F. pratensis</italic>, are naturally protected against agricultural plagues. Lolines are also found in seeds of <italic>S. arundinaceus</italic> infected by <italic>E. coenophiala</italic> (Jackson et al., <xref ref-type="bibr" rid="B27">1984</xref>). The existence of strains producing lolines and/or peramine but not ergovaline or lolitrem-B (that are toxic for livestock) is the foundation of the use of the &#x0201C;safe-endophyte technology&#x0201D; in forage breeding (Gundel et al., <xref ref-type="bibr" rid="B17">2013</xref>). This technology relies on the quality of the seeds since not only the fungus but also its alkaloids determine its successful application in agriculture.</p>
<p>Interestingly, even though the gene required for the peramine (perA) is found in <italic>E. occultans</italic>, the alkaloid remains undetected in tissue and now in seeds, of <italic>Lolium multiflorum</italic> (Bast&#x000ED;as et al., <xref ref-type="bibr" rid="B2">2017</xref>). Peramine is a unique and potent insecticide fungal alkaloid (Bush et al., <xref ref-type="bibr" rid="B4">1997</xref>; Schardl et al., <xref ref-type="bibr" rid="B42">2013</xref>). Here, it was only detected in seeds produced by the <italic>F. rubra</italic> PEN but with variation among years. There was a clear relationship between the level of peramine and the year (2009: 0 &#x003BC;g.g<sup>&#x02212;1</sup>, 2010: 3.12 &#x003BC;g.g<sup>&#x02212;1</sup>, and 2011: 5.68 &#x003BC;g.g<sup>&#x02212;1</sup>, corresponding to 24, 12, and 1 month of storage) suggesting a susceptibility to denaturalize with time. It was found in <italic>L. perenne</italic> that the level of peramine follows the growing cycle of the host grass, showing a minimum (&#x0003C; 1.0 &#x003BC;g.g<sup>&#x02212;1</sup>) in winter and a maximum (4&#x02013;8 &#x003BC;g.g<sup>&#x02212;1</sup>) in summer (Fuchs et al., <xref ref-type="bibr" rid="B13">2017b</xref>). With a suggested threshold of 2 &#x003BC;g.g<sup>&#x02212;1</sup> for peramine to be effective against herbivores (see references in Fuchs et al., <xref ref-type="bibr" rid="B13">2017b</xref>), the concentration observed in seeds of PEN <italic>F. rubra</italic> line has the potential to be preserved for up to 1 year of storage.</p>
<p>Unlike the alkaloids, for which the genetic information for their synthesis is encoded in the endophyte genome (Schardl et al., <xref ref-type="bibr" rid="B42">2013</xref>), both the plant and the fungus can, in principle, produce molecules with antioxidant capacity (Huang et al., <xref ref-type="bibr" rid="B26">2007</xref>). However, no precise information exists regarding the direct contribution of the fungus toward the antioxidant activity of plants (Hamilton et al., <xref ref-type="bibr" rid="B23">2012</xref>) and their seeds (Gundel et al., <xref ref-type="bibr" rid="B15">2012</xref>, <xref ref-type="bibr" rid="B20">2015</xref>). Our results support the hypothesis that there is a positive relationship between both these two groups of secondary compounds. It was particularly evident for ergovaline in <italic>F. rubra</italic> RAB maternal line, as the concentration of alkaloid was related to a higher antioxidant capacity with regard to both tocochromanols and E<sub>GSSG/2GSH</sub>, whereas in <italic>L. multiflorum</italic> seeds, a positive relationship was only found between loline alkaloids and tocochromanols.</p>
<p>The functionality of both tocochromanols and glutathione in the seed has implications for the ecology of the species. Previous studies that show a protective role of endophytes on seeds and seedlings, highlight alkaloids as the compounds responsible for this fact. For example, endophyte-infected seedlings of <italic>L. perenne</italic> were resistant to the weevil <italic>Listronotus bonariensis</italic> even though the fungus was dead, proving that alkaloids remain bioactive long after the demise of the fungus (Stewart, <xref ref-type="bibr" rid="B44">1985</xref>). Nonetheless, this bioactivity could be broken if alkaloids are target of oxidative processes associated with aging and deteriorating conditions (Walters, <xref ref-type="bibr" rid="B52">1998</xref>). We suggest that a lower antioxidant capacity is associated with a lower concentration of alkaloids. As seed quality parameters decline, the potential for the endophytes to protect the seeds is likely to diminish.</p>
</sec>
<sec id="s5">
<title>Author Contributions</title>
<p>PG, MAM-G, and CMG designed the research. PG, FB and MAM-M analyzed the data and made the figures. BRVdA, IZ, LPB, and CS performed the analyses for alkaloid and antioxidant quantification. PG, CS, BRVdA, and MAM-M wrote the manuscript. PG edited and submitted the manuscript. All authors have approved the final version of the manuscript.</p>
<sec>
<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>
</sec>
</body>
<back>
<ack><p>Authors thank Andrea C. Ueno for his technical assistance of preparing seeds for their analyses.</p>
</ack>
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<fn-group>
<fn fn-type="financial-disclosure"><p><bold>Funding.</bold> This article was supported by the projects PII20150126 (Fondecyt-Chile) and AGL2016-76035-C21R (Spanish, MICINN).</p>
</fn>
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