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<journal-id journal-id-type="publisher-id">Front. Microbiomes</journal-id>
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<journal-title>Frontiers in Microbiomes</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Microbiomes</abbrev-journal-title>
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<issn pub-type="epub">2813-4338</issn>
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<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-id pub-id-type="doi">10.3389/frmbi.2026.1735358</article-id>
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<subj-group subj-group-type="heading">
<subject>Original Research</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>Maize leaf endosphere microbiome was affected by domestication and shows patterns consistent with microbial dysbiosis</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Topcu</surname><given-names>Ilksen</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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<name><surname>Bernal</surname><given-names>Julio S.</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>*</sup></xref>
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<contrib contrib-type="author" corresp="yes">
<name><surname>Antony-Babu</surname><given-names>Sanjay</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>*</sup></xref>
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<aff id="aff1"><label>1</label><institution>Department of Plant Pathology and Microbiology, Texas A&amp;M University</institution>, <city>College Station</city>, <state>TX</state>,&#xa0;<country country="us">United States</country></aff>
<aff id="aff2"><label>2</label><institution>Department of Entomology, Texas A&amp;M University</institution>, <city>College Station</city>, <state>TX</state>,&#xa0;<country country="us">United States</country></aff>
<author-notes>
<corresp id="c001"><label>*</label>Correspondence: Julio S. Bernal, <email xlink:href="mailto:juliobernal@tamu.edu">juliobernal@tamu.edu</email>; Sanjay Antony-Babu, <email xlink:href="mailto:sanjay@tamu.edu">sanjay@tamu.edu</email></corresp>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-02-23">
<day>23</day>
<month>02</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2026</year>
</pub-date>
<volume>5</volume>
<elocation-id>1735358</elocation-id>
<history>
<date date-type="received">
<day>29</day>
<month>10</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>03</day>
<month>02</month>
<year>2026</year>
</date>
<date date-type="rev-recd">
<day>21</day>
<month>01</month>
<year>2026</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2026 Topcu, Bernal and Antony-Babu.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Topcu, Bernal and Antony-Babu</copyright-holder>
<license>
<ali:license_ref start_date="2026-02-23">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. 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.</license-p>
</license>
</permissions>
<abstract>
<sec>
<title>Background</title>
<p>Whether domestication, post-domestication spread, and breeding affected the maize leaf endosphere microbiota is poorly understood despite the well-known effects of those processes on the crop&#x2019;s genetics and responses to the environment. We examined the leaf endosphere microbial communities associated with three plant groups (Zea mays): teosintes, maize landraces, and maize elite inbreds. The teosintes group included Balsas (Z. mays parviglumis) and perennial (Zea diploperennis) teosinte, and each maize (Z. mays mays) group included genotypes from Mexico and USA. We used 16S-V4 region amplicon sequencing of the leaf endophytic microbiota to infer how the microbial communities of inbred maize may have been shaped by the crop&#x2019;s evolution, and whether they were affected by: (i) the transition from a perennial life history to an annual life history in the teosintes; (ii) domestication of maize from Balsas teosinte; (iii) northward spread of landrace maize from Mexico to the US; and (iii) breeding of landrace maizes to produce elite inbreds.</p>
</sec>
<sec>
<title>Results</title>
<p>The leaf endophytic microbial community differed among the plant groups and genotypes, and was affected by domestication, as indicated by a decline in bacterial diversity and changes in microbial community structure between wild (teosinte) and domesticated (maize) Zea. While the microbial community structure was stringent and regulated in the teosintes, it was variable in the maize landraces and inbreds, as evidenced by greater distances to centroid based on Euclidean dissimilarity metric. This pattern was suggestive of microbial dysbiosis in the leaf endosphere associated with domestication and is consistent with predictions of the Anna Karenina principle. This finding marks the first evidence of dysbiosis associated with domestication. FAPROTAX predictions suggested that the teosintes may harbor microbial communities enriched in taxa associated with cellulolytic, chitinolytic, and nitrate respiration functions, while the maizes showed higher fermentation and nitrate reduction functions.</p>
</sec>
<sec>
<title>Conclusions</title>
<p>Our results showed that the leaf endosphere microbial community structures in maize are consistent with alterations associated with dysbiosis. Our findings enhanced our understanding of the effects of anthropogenic processes including crop domestication, spread, and breeding on the leaf endosphere of elite maize cultivars, and may guide the development of evolutionarily-and ecologically sustainable biofertilizers and biocontrol agents.</p>
</sec>
</abstract>
<kwd-group>
<kwd>leaf endosphere</kwd>
<kwd>maize</kwd>
<kwd>microbiome</kwd>
<kwd>plant domestication</kwd>
<kwd>teosinte</kwd>
<kwd><italic>Zea diploperennis</italic></kwd>
<kwd><italic>Zea mays mays</italic></kwd>
<kwd><italic>Zea mays parviglumis</italic></kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was received for this work and/or its publication. This work was financially funded through USDA-Research, Education, and Economics Information System &#x201c;Deciphering Microbial Functions to Improve Plant Productivity and Sustainable Agriculture&#x201d;. The authors would like to thank USDA NIFA award numbers 2021-70006&#x2013;35321 and 2023-67013-39155, TAMU-CONACyT grant (246391-97140), and USDA HATCH project 1021870 #TEX09714. I.T. was supported in part by the Ministry of National Education of T&#xfc;rkiye. This research was carried out using the advanced computational resources provided by Texas A&amp;M High Performance Research Computing.</funding-statement>
</funding-group>
<counts>
<fig-count count="8"/>
<table-count count="1"/>
<equation-count count="0"/>
<ref-count count="143"/>
<page-count count="17"/>
<word-count count="9525"/>
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<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Environmental Microbiomes</meta-value>
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</front>
<body>
<sec id="s1">
<title>Background</title>
<p>The plant microbiome consists of numerous taxa of microorganisms, including bacteria, fungi, archaea, protists, and viruses, which play essential roles in many plant functions, such as growth, nutrient uptake, plant resistance against pathogens and insects, and plant tolerance of abiotic stresses (<xref ref-type="bibr" rid="B116">Vandenkoornhuyse et&#xa0;al., 2002</xref>; <xref ref-type="bibr" rid="B51">Hassani et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B114">Trivedi et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B101">Sahu et&#xa0;al., 2022</xref>). The microbial components of plant holobiomes coevolved with their host plants and occurs in specialized niches, such as the rhizosphere (space nearest plant roots that is inhabited by microorganisms), phyllosphere (surface of aboveground plant tissues that is inhabited by microorganisms), and endosphere (internal above- and belowground plant tissues) (<xref ref-type="bibr" rid="B51">Hassani et&#xa0;al., 2018</xref>). The structure and composition of microbiome communities colonizing plant niches can be influenced by numerous variables (e.g., plant genotype, soil type, biotic and abiotic environmental variables, plant development stage, and geographical location), and plant survival and reproduction are mediated by microbiome communities (<xref ref-type="bibr" rid="B41">Finkel et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B57">Jackson and Denney, 2011</xref>; <xref ref-type="bibr" rid="B60">Johnston-Monje et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B21">Brisson et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B135">Xiong et&#xa0;al., 2021a</xref>). Moreover, host plants selectively recruit particular beneficial microorganisms in their niche compartments and, in return, the recruited microbial assemblages enhance the survival and reproduction of their hosts (<xref ref-type="bibr" rid="B42">Fitzpatrick et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B136">Xiong et&#xa0;al., 2021b</xref>). For example, rhizosphere microbiota is known to play essential roles in soil nutrient acquisition and enhance plant defense against biotic stressors (<xref ref-type="bibr" rid="B23">Bulgarelli et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B15">Begum et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B42">Fitzpatrick et&#xa0;al., 2019</xref>). Similarly, phyllosphere and leaf endosphere microbiota play crucial roles in defense against plant pathogens and other important plant processes (<xref ref-type="bibr" rid="B100">Ryan et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B13">Balint-Kurti et&#xa0;al., 2010</xref>; <xref ref-type="bibr" rid="B61">Johnston-Monje and Raizada, 2011</xref>; <xref ref-type="bibr" rid="B104">Shehata et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B101">Sahu et&#xa0;al., 2022</xref>).</p>
<p>The processes of plant domestication, geographic spread, and improvement resulted in significant reductions in the genetic diversity of crop species and shaped their microbial assemblages (<xref ref-type="bibr" rid="B111">Szoboszlay et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B92">P&#xe9;rez-Jaramillo et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B52">Hassani et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B49">Gutierrez and Grillo, 2022</xref>; <xref ref-type="bibr" rid="B55">Huang et&#xa0;al., 2022</xref>). Maize (<italic>Zea mays mays</italic>) is one of the most widely cultivated cereal crops globally and the Americas is the crop&#x2019;s top-producing region (<xref ref-type="bibr" rid="B37">FAO, 2022</xref>). Maize is the product of Balsas teosinte (<italic>Zea mays parviglumis</italic>) domestication, which began ca. 9,200 years ago in the Pacific lowlands of southern Mexico (<xref ref-type="bibr" rid="B82">Matsuoka et&#xa0;al., 2002</xref>). Several post-domestication processes, including farmer (artificial) and natural selection, geographic spread, and modern breeding led to dramatic morphological- and physiological trait changes in maize (<xref ref-type="bibr" rid="B138">Yamasaki et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B142">Zhang et&#xa0;al., 2023</xref>). Artificial selection by farmers after domestication produced a wide variety of landrace cultivars (<xref ref-type="bibr" rid="B131">Wellhausen, 1952</xref>; <xref ref-type="bibr" rid="B120">Vielle-Calzada and Padilla, 2009</xref>). Dispersal to North America and the present-day USA began as early as 2,100 years ago and was followed by <italic>in situ</italic> development of landrace cultivars, followed by synthetic cultivars derived from simple crossed of landraces in the 1800s, and modern elite inbred and hybrid cultivars beginning ca. 100 years ago (<xref ref-type="bibr" rid="B121">Vigouroux et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B85">Merrill et&#xa0;al., 2009</xref>; <xref ref-type="bibr" rid="B118">Van Heerwaarden et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B56">Hufford et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B119">van Heerwaarden et&#xa0;al., 2012</xref>). Genetic (allelic) diversity in maize has been reduced due to a population bottleneck and directional selection targeting genomic regions associated with agronomically significant traits (<xref ref-type="bibr" rid="B142">Zhang et&#xa0;al., 2023</xref>). Two prominent examples are tgal1 and ZmSRO1d-R. The tga1 largely controls the loss of the seed fruitcase. The fruitcase a critical and early step in maize domestication (<xref ref-type="bibr" rid="B128">Wang et&#xa0;al., 2005</xref>), where in Balsas teosinte, each seed is enclosed in a hardened fruitcase largely precluding human consumption of the seed. Domestication of Balsas teosinte required selection, and fixation, upon a single nonsynonymous G to C mutation in tga1 leading to the evolution of the fully exposed seeds of maize (<xref ref-type="bibr" rid="B129">Wang et&#xa0;al., 2015</xref>). The ZmSRO1d-R, which modulates the balance between crop yield and drought resistance by increasing ROS levels in guard cells, was selected during domestication and breeding (<xref ref-type="bibr" rid="B46">Gao et&#xa0;al., 2022</xref>). Previous study has employed genome-wide association studies (GWAS) to systematically examine how genetic variation in maize correlates with the composition of root-associated microbial communities. By analyzing large populations of maize together with their corresponding microbial profiles, researchers identified single-nucleotide polymorphisms (SNPs) associated with shifts in rhizosphere community structures (<xref ref-type="bibr" rid="B84">Meier et&#xa0;al., 2022</xref>). Although no study has yet explored how genetic loci in teosinte influence its microbiome composition, maize domestication has led to a significant reduction in genetic diversity relative to teosinte. This observation raises the question of whether this reduction in genetic diversity may, in turn, have impacted microbial diversity in the leaf endosphere.</p>
<p>Microbial taxa relevant to plant survival and reproduction may be absent or underrepresented in the microbial assemblages of modern crop cultivars, plausibly because such cultivars have been bred to thrive under conditions in which crop nutrition and defense against insects and pathogens depend on use of synthetic fertilizers and pesticides (<xref ref-type="bibr" rid="B25">Chaudhary, 2013</xref>; <xref ref-type="bibr" rid="B47">Gopal and Gupta, 2016</xref>; <xref ref-type="bibr" rid="B92">P&#xe9;rez-Jaramillo et&#xa0;al., 2016</xref>). Hence it is important to evaluate whether and to which extent the microbial community structure in modern crops differs from the structures in their domesticated and wild ancestors, which typically thrive in the absence of synthetic fertilizers and pesticides. Particularly, it is relevant to evaluate whether crop microbial community structure was affected by domestication and post-domestication processes, e.g., farmer selection, geographic spread, and modern breeding, or whether signs of diminished microbial recruitment are evident. Additionally, it is important to evaluate whether microbial dysfunction, i.e., dysbiosis, is associated with domestication and post-domestication processes. Dysbiosis is defined as encompassing any microbial compositional or functional alteration, including changes in abundance, diversity, or critical functions&#x200b; (<xref ref-type="bibr" rid="B12">B&#xe4;ckhed et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B53">Henao-Mejia et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B89">Olesen and Alm, 2016</xref>; <xref ref-type="bibr" rid="B10">Arnault et&#xa0;al., 2023</xref>). Healthy microbiomes are typically characterized by a balanced composition with controlled variability, where deterministic processes driven by host regulation maintain functional stability and resilience (<xref ref-type="bibr" rid="B12">B&#xe4;ckhed et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B77">Lozupone et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B54">Henry et&#xa0;al., 2021</xref>). A reduction in heterogeneity may indicate dominance by a few microbial taxa, potentially resulting from environmental stressors or pathogen invasion, leading to functional impairments such as disease resistance (<xref ref-type="bibr" rid="B12">B&#xe4;ckhed et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B27">Chen et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B50">Han et&#xa0;al., 2022</xref>). In addition, a rise in heterogeneity often represents increased stochasticity in microbial community assembly, associated with dysbiosis and reduced host capacity to regulate its microbiota&#x200b; (<xref ref-type="bibr" rid="B12">B&#xe4;ckhed et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B10">Arnault et&#xa0;al., 2023</xref>). These shifts highlight the intricate relationship between microbiome structure and host health, where deviations from balanced heterogeneity can significantly impact fitness and productivity. Subjected to abiotic or biotic stresses, plant (and animal) microbiomes may fall under dysbiosis (<xref ref-type="bibr" rid="B70">Lavrinienko et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B50">Han et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B10">Arnault et&#xa0;al., 2023</xref>). The Anna Karenina Principle (AKP), viz. &#x201c;all healthy microbiota are alike; each disease-associated microbiota is sick in its own way&#x201d; (<xref ref-type="bibr" rid="B140">Zaneveld et&#xa0;al., 2017</xref>), is used in microbiome studies to describe whether plants harbor a dysfunctional microbiota (<xref ref-type="bibr" rid="B140">Zaneveld et&#xa0;al., 2017</xref>) (<xref ref-type="bibr" rid="B79">Ma, 2020</xref>),. While dysbiosis has been demonstrated well in human and animal microbiomes (<xref ref-type="bibr" rid="B140">Zaneveld et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B79">Ma, 2020</xref>), little is known in plant-associated microbiomes. Dysbiosis is linked to poor health in hosts (<xref ref-type="bibr" rid="B106">Sohrabi et&#xa0;al., 2023</xref>) and the current knowledge of plant microbiome dysbiosis, although limited, comes from the study of plant diseases (<xref ref-type="bibr" rid="B66">Koskella et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B31">Choi et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B71">Lee et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B50">Han et&#xa0;al., 2022</xref>). For instance, a study conducted on the rhizosphere of dead, but standing, Korean fir trees revealed a state of dysbiosis characterized by a noticeable decrease in the richness and diversity of the microbiota within the rhizosphere when compared to the microbiota of healthy trees (<xref ref-type="bibr" rid="B50">Han et&#xa0;al., 2022</xref>). Additionally, a defect in pattern-triggered immunity and the absence of a specific metabolite, previously linked to phyllosphere, are associated with dysbiosis in plants (<xref ref-type="bibr" rid="B27">Chen et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B108">Su et&#xa0;al., 2024</xref>). Understanding the underlying conditions that lead to microbial dysfunction, and fitness costs in plant hosts, is important because it may inform the study of beneficial microbiomes and the development of microbial inoculants for sustainable crop production.</p>
<p>The study presented here is the first, to the best of our knowledge, to assess whether and how domestication, geographic spread, and modern breeding affected the bacterial community of the maize leaf endosphere. Some effects of domestication and breeding on the microbial assembly of the maize rhizosphere were reported in prior studies (<xref ref-type="bibr" rid="B39">Favela et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B55">Huang et&#xa0;al., 2022</xref>). Here, we report on the assemblages of endophytic bacterial microbiota of leaves in a suite of teosintes (<italic>Zea</italic> spp. other than maize) and maize genotypes spanning the evolution of maize: perennial teosinte (<italic>Zea diploperennis</italic>), Balsas teosinte, landrace maize cultivars, and elite inbred maize cultivars. Using this suite, we inferred on effects of the perennial to annual life history transition in teosintes (perennial vs Balsas teosinte), domestication (Balsas teosinte vs. Mexican landrace maize), geographic spread (Mexican vs USA landrace maize), and modern breeding (Mexican and US landrace vs elite inbred maize). We addressed whether the structural and compositional aspects of the leaf endophytic bacterial community were mediated by life history evolution, domestication, geographic spread, and modern breeding, and whether dysbiosis is associated with domestication or other processes. Furthermore, we examine how stringency in teosinte and maize, defined as the level of selectivity or ecological filtering exerted by the plant host, has changed during the process of maize domestication. Numerous studies have documented marked losses of genetic and trait diversity associated with maize domestication (<xref ref-type="bibr" rid="B22">Buckler and Stevens, 2006</xref>; <xref ref-type="bibr" rid="B99">Ross-Ibarra et&#xa0;al., 2007</xref>; <xref ref-type="bibr" rid="B56">Hufford et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B44">Fontes-Puebla et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B28">Chen et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B16">Bernal et&#xa0;al., 2023</xref>) and we suggest that it is plausible that such losses parallel changes in the leaf endophytic bacterial community. We hypothesized that transition from perennial to annual life history in teosintes, and maize domestication, geographic spread, and breeding would each be associated with: i) reduction in the diversity and richness of the microbial community recruited within the leaf endosphere; and ii) reductions in stringency and increases in variability in processes mediating recruitment. We also investigated whether these changes were associated with signatures of dysbiosis in terms of alpha- and beta-diversities. This includes a reduction in alpha-diversity, such as decreased richness or diversity, and increased beta-diversity, reflecting greater stochasticity in community composition, consistent with the Anna Karenina Principle.</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<title>Materials and methods</title>
<sec id="s2_1">
<title>Plant materials and growth</title>
<p>A suite of 17 teosinte and maize accessions corresponding to six genotypes contained within three plant groups were selected to represent the evolution of maize from perennial teosinte to elite inbred maize. Specifically, this suite included the following three plant groups, each with two genotypes: (i) teosinte, including perennial teosinte (1 accession) and Balsas teosinte (6 accessions); (ii) Mexican maize, including Mexican landrace maize (1 accession) and Mexican elite inbred maize (2 accessions); and (iii) US maize, including US landrace maize (3 accessions) and US elite inbred maize (4 accessions) (<xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Table S1</bold></xref>). Using these plant groups and genotypes we addressed whether the leaf endosphere bacterial community was affected by: (i) the transition from a perennial to an annual life history (comparison: perennial vs Balsas teosinte); (ii) domestication (Balsas teosinte vs Mexican landrace); (iii) northward spread (Mexican landrace vs US landrace); (iv) breeding in Mexico (Mexican landrace vs Mexican elite inbred); and (v) breeding in USA (US landrace vs US elite inbred). Domestication effects were inferred using the maize landrace Tuxpen&#xf1;o because its distribution overlaps that of Balsas teosinte and with the area where maize was domesticated (<xref ref-type="bibr" rid="B82">Matsuoka et&#xa0;al., 2002</xref>; <xref ref-type="bibr" rid="B139">Yang et&#xa0;al., 2019</xref>).</p>
<p>Seeds were surface sterilized by soaking in 1% Tween20 followed by 5% bleach solution, both steps for one minute each. This was followed by alcohol wash with 70% ethanol twice in less than one minute and a final rinse with sterile reverse osmosis water (RO water) for one minute. The surface-sterilized seeds were transferred to sterile paper prewet with water in sterile Petri dishes for three days in a dark space for pre-germination. One germinated seed was transplanted per cone-tainer pot (4 &#xd7; 25 cm, diam &#xd7; length) that contained equal mixture (v/v) of play sand (Quikrete, Atlanta, Georgia, USA) and SunGro Sunshine LC1 soil mix (SunGro, Agawam, Massachusetts, USA). Before use, the soil-sand mixture was autoclaved thrice at 121 &#xb0;C for 1 hour at 24hrs intervals to reduce the initial microbial load and recolonizing microbial community in the soil (<xref ref-type="bibr" rid="B64">King et&#xa0;al., 2024</xref>). Five replicates per accession (except CML277 with three replicates because of poor germination) were grown for 4 weeks in a growth room under artificial LED lights and 1-week greenhouse condition with natural light. The plants were watered with tap water every other day.</p>
</sec>
<sec id="s2_2">
<title>Collection of leaf endosphere samples</title>
<p>Above-ground biomass was harvested from the 5-week-old seedlings. The entire above-ground mass was mostly made of leaf matter or curled up leaf with little or no real stem. The leaf samples were surface sterilized by soaking in a 5% bleach solution for one minute, a single rinse of 70% ethanol, and rinsed with sterile RO water. Surface-sterilized leaf samples were dabbed on sterile paper to remove excess moisture and sliced into small pieces. The sample tissues were flash-frozen and stored at -80 &#xb0;C until further processing.</p>
</sec>
<sec id="s2_3">
<title>DNA extraction</title>
<p>DNA was extracted from the leaf tissues using the ZymoBIOMICS&#x2122; DNA Miniprep Kit (Zymo Research, Irvine, CA, USA) and the protocol was modified (See detailed Method S1). DNA concentration was quantified using SpectraMax QuickDrop Micro-Volume Spectrophotometer, and the extracted DNA was verified by 1% agarose gel electrophoresis. According to the results of QuickDrop, the samples, which have less than 0.800 A260/A230 ratios, were tested whether they can be amplified by PCR (and hence can be used to produce metabarcoding libraries) with universal primers 27F (5&#x2032;-AGAGTTTGATCATGGCTCAG-3&#x2032;) as forward and 1492R (5&#x2032;-GGTTACCTTGTTACGACTT-3&#x2032;) as reverse primer (<xref ref-type="bibr" rid="B69">Lane, 1991</xref>). 10 &#x3bc;l PCR reaction was containing 5 &#x3bc;l of mix KAPA2G Fast HotStart ReadyMix PCR Kit (KAPA Biosystems, Wodurn, MA), 3 &#x3bc;l Molecular Biology Grade Water, CorningTM, 0.5 &#x3bc;l of each primer, and 1 &#x3bc;l of a 1e-2 DNA dilution from the leaf sample. PCR reaction mixture was amplified as follows: 95&#x2009;&#xb0;C for 3&#x2009;mins, then 95&#x2009;&#xb0;C for 15 sec, 48&#x2009;&#xb0;C for 15 sec, and followed by 72&#x2009;&#xb0;C for 30&#x2009;sec for 39 cycles. Subsequently, a final extension step was performed at 72&#x2009;&#xb0;C for 1 min, and the reaction was held at 10&#x2009;&#xb0;C continually. PCR products were run on 1% agarose gel and confirmed for the presence of bacterial 16S rRNA genes. DNA concentration was quantified using Qubit dsDNA HS Assay kit by Qubit 2.0 fluorometer (Life Technologies, Carlsbad, USA).</p>
</sec>
<sec id="s2_4">
<title>Metabarcoding and Illumina Mi Seq sequencing</title>
<p>Metabarcoding library preparation and sequencing was carried out by TxGen - Genomics and Bioinformatics Services, Texas A&amp;M University, College Station (<ext-link ext-link-type="uri" xlink:href="https://www.txgen.tamu.edu">https://www.txgen.tamu.edu</ext-link>). Briefly, the V4 region of the 16S rRNA gene was amplified using NEXTflex-16S V4 Amplicon-Seq Library Prep Kit 2.0 and primers 16S V4 forward (5&#x2019;-GACGC TCTTC CGATC TTATG GTAAT TGTGT GCCAG CMGCC GCGGT AA-3&#x2019;) and 16S V4 reverse (5&#x2019;-TGTGC TCTTC CGATC TAGTC AGTCA GCCGG ACTAC HVGGG TWTCT AAT-3&#x2019;) (BIOO Scientific, Austin, TX, USA). The libraries were sequenced using the Illumina MiSeq MCS 2.5.0.5 and RTA 1.18.54 software with default parameter settings. Sequencer.bcl basecall files were formatted into fastq files using bcl2fastq 2.20 script configureBclToFastq.pl. The quality of Illumina Mi Seq sequencing reads was assessed with FastQC (<xref ref-type="bibr" rid="B9">Andrews, 2010</xref>). Although no-template controls were not sequenced, negative controls were included during DNA extraction and PCR library preparation to ensure that the amplicons originated from the samples and not from the reagents. Additionally, microbial cultivation tests (data not shown) demonstrated that the surface-sterilized leaf samples contained sufficient microbial biomass for downstream analysis.</p>
<p>Raw amplicon data were processed using MOTHUR software (v.1.48.0, <ext-link ext-link-type="uri" xlink:href="https://mothur.org/wiki/miseq_sop/">https://mothur.org/wiki/miseq_sop/</ext-link>, accessed online December 2022) following the default settings (<xref ref-type="bibr" rid="B67">Kozich et&#xa0;al., 2013</xref>). The recommended SOP was followed except for the maximum length adjusted to 320 to accommodate our assembled read lengths. Because this study was designed to investigate the bacterial community composition of the leaf endosphere, we performed &#x201c;remove.lineage&#x201d; command in mothur to filter out sequences associated with chloroplast, mitochondria, archaea, eukaryota, and unknown lineages. Sequences were clustered into operational taxonomic units (OTUs) at a 97% similarity threshold. Because this study focused on broad patterns of microbial community structure, diversity, and ecological variation across teosinte and maize, 97% OTU clustering was appropriate for these objectives. The consensus taxonomy of the OTUs was generated using the &#x201c;classify.otu&#x201d; command in mothur with reference data using the SILVA database (release 138.1, <ext-link ext-link-type="uri" xlink:href="https://mothur.org/wiki/silva_reference_files/">https://mothur.org/wiki/silva_reference_files/</ext-link>) (<xref ref-type="bibr" rid="B94">Pruesse et&#xa0;al., 2007</xref>).</p>
</sec>
<sec id="s2_5">
<title>Statistical analyses</title>
<p>OTU data and taxonomic information on OTUs were analyzed for all statistical calculations and data visualization in R (<xref ref-type="bibr" rid="B95">R Core Team, 2022</xref>) and JMP Pro 17 statistical software (<xref ref-type="bibr" rid="B59">JMP&#xae;, 2025</xref>). The data were normalized using cumulative sum scaling (CSS) for all analyses, except for Venn diagram analysis and richness metrics, which were calculated based on absolute species counts. Richness metrics were calculated from OTU tables filtered to retain taxa with &#x2265;10 total counts across all samples, thereby reducing noise while maintaining biologically meaningful richness estimates. Bacterial alpha diversity, including the Chao1, Shannon, Simpson, Observed and Fisher indices, was estimated using JMP software. The results of alpha diversity were visualized and statistical analysis were conducted using JMP software (<xref ref-type="bibr" rid="B59">JMP&#xae;, 2025</xref>). We performed alpha diversity analysis of bacterial communities in the leaf endosphere of maize using a nested analysis of variance (ANOVA) model that included plant group (teosinte, Mexican maize, US maize) and genotype (perennial teosinte, Balsas teosinte, Mexican landrace, Mexican elite inbred, US landrace, US elite inbred) nested within plant group. As warranted, after ANOVA plant group means were separated using Tukey&#x2019;s tests; genotype means were compared using five <italic>a priori</italic> contrasts: perennial vs Balsas teosinte; Balsas teosinte vs Mexican landrace; Mexican landrace vs US landrace; Mexican landrace vs Mexican elite inbred; and US landrace vs US elite inbred. The critical <italic>P</italic> value for each <italic>a priori</italic> contrast was set to 0.010 to maintain the experiment-wise error rate at 0.05 (<xref ref-type="bibr" rid="B2">Abdi and Williams, 2010</xref>). To measure bacterial beta diversity, we used Principal Coordinate Analysis (PCoA) based on Bray-Curtis and weighted UniFrac metrics (<xref ref-type="bibr" rid="B20">Bray and Curtis, 1957</xref>; <xref ref-type="bibr" rid="B76">Lozupone et&#xa0;al., 2007</xref>). A nested permutational analysis of variance (PERMANOVA) was performed to assess the differences in community composition among plant group (teosinte, Mexican maize, US maize) and genotype (perennial teosinte, Balsas teosinte, Mexican landrace, Mexican elite inbred, US landrace, US elite inbred) nested within plant group. Pairwise comparisons of genotype were calculated using pairwise PERMANOVA function based on adjusted false discovery rate (FDR) P-values. Further, distance to centroid based on Bray-Curtis dissimilarity metric and Nonmetric Multidimensional Scaling (NMDS) analysis was conducted to test for differences in beta diversity between plant samples (<xref ref-type="bibr" rid="B8">Anderson, 2001</xref>). PCoA, centroid plot, and NMDS analyses were performed using &#x201c;phyloseq&#x201d;, &#x201c;microbial &#x201c;, &#x201c;microeco&#x201d;, &#x201c;file2meco&#x201d;, and &#x201c;magrittr&#x201d; R packages (<xref ref-type="bibr" rid="B86">microbial R package</xref>; <xref ref-type="bibr" rid="B8">Anderson, 2001</xref>; <xref ref-type="bibr" rid="B83">McMurdie and Holmes, 2013</xref>; <xref ref-type="bibr" rid="B73">Liu et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B11">Bache and Wickham, 2022</xref>; <xref ref-type="bibr" rid="B74">Liu et&#xa0;al., 2022</xref>). NMDS plots were visualized in R, while the PCoA and distance to centroid plots were visualized in JMP Pro 17 statistical software (<xref ref-type="bibr" rid="B59">JMP&#xae;, 2025</xref>) using output file form microeco package. Weighted UniFrac metric was calculated in Mothur using &#x201c;unifrac.weighted&#x201d; and visualized as PCoA plot in R. The output files from &#x201c;pcoa&#x201d; command line in Mothur were utilized in R generating the plot. R packages including &#x201c;rgl&#x201d;, &#x201c;vegan&#x201d;, &#x201c;tidyverse&#x201d;, &#x201c;ggtext&#x201d;, &#x201c;ggplot2&#x201d;, and &#x201c;stats&#x201d; were employed for visualization of Weighted UniFrac plot (<xref ref-type="bibr" rid="B87">Murdoch, 2001</xref>; <xref ref-type="bibr" rid="B132">Wickham, 2016</xref>; <xref ref-type="bibr" rid="B133">Wickham et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B134">Wilke, 2020</xref>; <xref ref-type="bibr" rid="B88">Oksanen et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B95">R Core Team, 2022</xref>). Cluster dendrogram based on Bray-Curtis similarity was calculated from OTUs with the &#x201c;vegdist&#x201d; function in R (<xref ref-type="bibr" rid="B88">Oksanen et&#xa0;al., 2022</xref>). Reductions in stringency and increases in variability of processes involved in microbial recruitment in leaf and AKP were assessed using the beta-nearest taxon index (&#x3b2;NTI). Phylogenetic distances between microbial communities were also evaluated using &#x3b2;NTI (<xref ref-type="bibr" rid="B103">Shade and Handelsman, 2012</xref>). The beta mean nearest-taxon distance (betaMNTD) was calculated using a &#x2018;sample pool&#x2019; null model analysis with 999 randomizations within the picante package in R, and the results were visualized using the ggplot2 package to provide a comprehensive understanding of microbial community composition (<xref ref-type="bibr" rid="B62">Kembel et&#xa0;al., 2010</xref>; <xref ref-type="bibr" rid="B132">Wickham, 2016</xref>).</p>
<p>Linear discriminant analysis effect sizes (LEfSe) were used to determine differentially abundant features between plant types (<xref ref-type="bibr" rid="B102">Segata et&#xa0;al., 2011</xref>). LefSe was calculated by setting a <italic>p-value</italic> of less than 0.05 and the logarithmic LDA (linear discriminant analysis) effect size score threshold was set to 4.0. The LEfSe analysis was conducted using &#x201c;phyloseq&#x201d;, &#x201c;microeco&#x201d;, &#x201c;file2meco&#x201d;, and &#x201c;ggplot2&#x201d; R packages (<xref ref-type="bibr" rid="B83">McMurdie and Holmes, 2013</xref>; <xref ref-type="bibr" rid="B132">Wickham, 2016</xref>; <xref ref-type="bibr" rid="B73">Liu et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B74">Liu et&#xa0;al., 2022</xref>). The relative abundances of leaf endosphere microbiota at the phylum and genus levels were generated in R. UpSet plot and a Venn diagram, which shows unique or shared OTUs between genotypes, and were calculated in R using the &#x201c;microeco&#x201d; package (<xref ref-type="bibr" rid="B73">Liu et&#xa0;al., 2021</xref>). Shared OTUs were defined as core microbiome (<xref ref-type="bibr" rid="B103">Shade and Handelsman, 2012</xref>). Finally, the bacterial functional profiles of the six genotypes were determined through Functional Annotation of Prokaryotic Taxa (FAPROTAX) (<xref ref-type="bibr" rid="B75">Louca et&#xa0;al., 2016</xref>).</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<title>Results</title>
<p>We sequenced the bacterial 16S rRNA V4 region from 83 leaf samples from 17 plant accessions corresponding to six genotypes spanning the evolution of maize from perennial teosinte to elite inbred maize. From these samples we obtained 3,921,857 bacterial sequences, which yielded 2,714,777 total sequences and 189,434 unique sequences after running &#x201c;screen.seqs&#x201d;, &#x201c;unique.seqs&#x201d; and &#x201c;align.seqs&#x201d; command lines. We reran the &#x201c;screen.seqs&#x201d; command, per the Mothur pipeline, to ensure that all the sequences aligned with the same region and obtained 2,545,257 total sequences and 156,886 unique sequences. We reran the &#x201c;unique.seqs&#x201d; step once more after quality filtering to eliminate duplicates, which yielded the same total number of sequences as the previous step but 151,799 unique sequences. After these steps, we ran chimera clustering and removal steps which yielded 2,490,998 total sequences and 73,348 unique sequences. Finally, we removed non-target taxonomic lineages using the &#x201c;remove.lineage&#x201d; command and obtained 99,623 total and 24,666 unique bacterial sequences. After rarefaction, we obtained 423 bacterial OTUs for further analysis.</p>
<p>The OTUs fell into a total of 229 genera from 19 phyla, according to taxa similarities with sequences in the SILVA database. The most dominant taxa among the 40 most abundant (per relative abundance) bacterial genera were either lower in abundance or completely missing in the maize landraces and elite inbreds compared to the teosintes (<xref ref-type="fig" rid="f1"><bold>Figure&#xa0;1</bold></xref>). Marked decreases in the relative abundances of the genera <italic>Devosia, Caulobacter, Chitinophaga</italic>, and <italic>Dyadobacter</italic>, among others, are evident from the teosintes to the maizes. A few genera seemed more abundant in maize compared to teosinte, such as <italic>Pantoea, Staphylococcus, Acinetobacter, Corynebacterium</italic>, and <italic>Ralstonia</italic> (<xref ref-type="fig" rid="f1"><bold>Figure&#xa0;1</bold></xref>). At the phylum level, Proteobacteria (65.5%), Bacteroidetes (14.1%), Actinobacteria (9.26%), Firmicutes (3.40%), and TM7 (1.92%) were the most dominant phyla in maize leaf endosphere bacterial communities. Notably, the relative abundance of Actinobacteria was consistently high in the teosintes and varied between low and high in maize, suggesting a marked effect of domestication (<xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Figure S1</bold></xref>).</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>Heatmap illustrating the relative abundance of the top 40 taxa OTUs at genus-level in maize genotypes. The genotypes are ordered to span the evolution of maize: perennial teosinte, Balsas teosinte, Mexican landrace maize, Mexican inbred maize, US landrace maize, and US inbred maize, as shown at the top.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="frmbi-05-1735358-g001.tif">
<alt-text content-type="machine-generated">Heatmap comparing the relative abundance of bacterial genera across perennial teosinte, Balsas teosinte, Mexican landrace, Mexican inbred, US landrace, and US inbred groups, with color intensity indicating higher abundance.</alt-text>
</graphic></fig>
<p>The shared and unique OTUs among maize genotypes were assessed and visualized using UpSet plot (<xref ref-type="fig" rid="f2"><bold>Figure&#xa0;2</bold></xref>). There were 37 OTUs shared by all plant genotypes, making them the central core microbial community shared by all the <italic>Zea</italic> genotypes studied here. Overall, the core microbial community of the six genotypes included 37 OTUs in 17 unique genera. Balsas teosinte and US inbred genotypes harbored the highest numbers of unique bacterial taxa, with 901 and 251, respectively, followed by US landrace with 149, Mexican inbred with 171, perennial teosinte with 122 and Mexican landrace with 31 unique taxa (<xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Figure S2</bold></xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>UpSet plot showing shared and unique bacterial OTUs between maize genotypes in the leaf endosphere microbiota. Perennial teosinte harbored 122 unique bacterial taxa, Balsas teosinte 901, US inbred 251, US landrace 149, Mexican inbred 171, and Mexican landrace 31, respectively.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="frmbi-05-1735358-g002.tif">
<alt-text content-type="machine-generated">Bar chart and matrix visualization comparing intersection sizes for six genetic groups: Mexican inbred, perennial teosinte, Balsas teosinte, US landrace, US inbred, and Mexican landrace. Blue bars show intersection sizes, red bars show set sizes, and red dots indicate intersection combinations.</alt-text>
</graphic></fig>
<p>The loss of diversity associated with domestication was particularly evident in the diversity indices associated with the plant groups and genotypes (<xref ref-type="fig" rid="f3"><bold>Figure&#xa0;3</bold></xref>). Comparisons among Shannon and Chao1 indices of leaf endosphere microbiota among the plant groups revealed a trend of declining diversity and richness from teosinte to Mexican maize (landrace and elite inbred) and US maize (landrace and elite inbred), as well as a consistent decline between the Balsas teosinte and Mexican landrace genotypes, indicating an effect of domestication (P&lt;0.0001, <xref ref-type="fig" rid="f3"><bold>Figure&#xa0;3</bold></xref>). These findings were further supported by the richness OTUs, and Simpson and Fisher indices (<xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Figure S3</bold></xref>). Breeding (i.e., landrace vs elite inbred maize comparison) did not have a consistent effect on OTU diversity as its effect was significant only per Shannon index and for Mexican maize (P = 0.005).</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Box plots and histograms showing leaf endosphere alpha diversity indices observed in maize genotypes. In the left plot, Teosinte, Mexican maize, and US maize were compared using Tukey&#x2019;s test. In the right plot, nested groups within Teosinte (perennial and Balsas), Mexican maize (landrace and inbred), and US maize (landrace and inbred) were compared using a-priori contrasts. The Shannon and Chao1 indices exhibit a pattern of decreasing diversity and richness from Teosinte to Mexican maize (landrace and elite inbred) and to US maize (landrace and elite inbred). Teosintes generally showed greater diversity and richness in the leaf endosphere microbiota (P&lt;0.05).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="frmbi-05-1735358-g003.tif">
<alt-text content-type="machine-generated">Violin plot with box plots showing Chao1 and Shannon diversity indices for bacterial communities across teosinte, Mexican maize, and US maize groups. The left section groups by plant type, and the right section further differentiates by genotype within each group: perennial teosinte, Balsas teosinte, Mexican landrace, Mexican inbred, US landrace, and US inbred. Statistical test results within the figure indicate significant effects of domestication and plant group for both indices. Green indicates teosinte, yellow Mexican maize, and red US maize. Individual sample data points are shown as gray dots.</alt-text>
</graphic></fig>
<p>We used Principal Coordinates Analysis (PCoA) based on Bray-Curtis dissimilarity matrices of bacterial communities to analyze and visualize beta diversity dissimilarities among the six genotypes (<xref ref-type="fig" rid="f4"><bold>Figure&#xa0;4</bold></xref>); corresponding weighted Unifrac metric and NMDS plots are shown in <xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Figure S4</bold></xref>. PCoA revealed marked divergence in the composition of leaf endosphere microbiota between the teosinte and maize genotypes along the first axis (PCo 1, 25.5%), while little to no divergence was evident among genotypes along the second axis (PCo 2, 9.4%). The divergent pattern separating teosinte and maize along the first axis suggested a potential effect of domestication on beta diversity of leaf endosphere bacterial communities. Nested permutational analysis of variance (PERMANOVA) revealed significant effects of plant group (R<sup>2</sup> = 0.2469, P &lt; 0.001), whereas genotype nested within plant group was not significant (R<sup>2</sup> = 0.04834, P = 0.008) (<xref ref-type="table" rid="T1"><bold>Table&#xa0;1A</bold></xref>). Comparisons among plant groups of leaf endosphere microbiota indicated significant effects of domestication in beta diversity (Teosinte vs Mexican maize, P = 0.001) while comparisons among genotypes revealed significant effects of domestication (Balsas teosinte vs. Mexican landrace, P = 0.002) (<xref ref-type="table" rid="T1"><bold>Table&#xa0;1B</bold></xref>). In addition, hierarchical clustering analysis based on the Bray-Curtis distance of bacterial OTUs from leaf samples showed clear separation between teosinte and maize samples (<xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Figure S5</bold></xref>). Importantly, the within-cluster spread (= average distance to centroid) was significantly greater in maize, both Mexican and US, compared to teosinte (P &lt; 0.001) (<xref ref-type="fig" rid="f5"><bold>Figure&#xa0;5</bold></xref>). The increases in variation (within-cluster spread) with domestication are consistent with predictions of the Anna Karenina Principle, which predicts that under stress, microbial communities are increasingly shaped by stochastic processes and suffer overall increases in the differences between communities (<xref ref-type="bibr" rid="B10">Arnault et&#xa0;al., 2023</xref>).</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Leaf endosphere beta diversity is represented as a principal coordinates analysis (PCoA) plot based on Bray-Curtis dissimilarity values among maize genotypes. Each point represents a single sample, and the shape and colors indicate individual maize genotype. PCoA plot demonstrate significant differences in leaf endosphere microbiota composition between teosintes and maize plant group along the first axis (PCo 1, 25.5%), while differences along the second axis (PCo 2, 9.4%) were comparatively minor. The distinct pattern observed between teosintes and maize along the first axis indicated that domestication has influenced beta diversity of leaf endosphere bacterial communities. Centroids are represented by empty black symbols.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="frmbi-05-1735358-g004.tif">
<alt-text content-type="machine-generated">Two-panel graphic showing principal coordinates analysis (PCoA) plots of plant groups. Left panel: Green, yellow, and red dots represent teosinte, Mexican maize, and U.S. maize, clustered with distinct colored ellipses. Right panel: Colored symbols and dashed ellipses denote groups including Balsas teosinte, perennial teosinte, Mexican landrace, U.S. landrace, and U.S. inbred maize, each annotated. Insets provide statistical significance for domestication and genotype effects.</alt-text>
</graphic></fig>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>(A) Results of PERMANOVA analysis on leaf endosphere microbiota showed significant effects of plant group and nested genotype (plant group). (B) Pairwise comparisons of PERMANOVA based on adjusted false discovery rate (FDR) P-values identified significant differences among maize plant group and genotypes (FDR adjusted P&lt;0.05).</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" colspan="4" align="left">(A)</th>
</tr>
</thead>
<tbody>
<tr>
<th valign="middle" align="left">PERMANOVA results for plant group</th>
<th valign="middle" align="left">R<sup>2</sup></th>
<th valign="middle" align="left">F</th>
<th valign="middle" align="left">Pr (&gt;F)</th>
</tr>
<tr>
<td valign="middle" align="left">Plant group</td>
<td valign="middle" align="left">0.2469</td>
<td valign="middle" align="left">13.48</td>
<td valign="middle" align="left"><bold>0.001</bold></td>
</tr>
<tr>
<td valign="middle" align="left">Genotype (Plant group)</td>
<td valign="middle" align="left">0.04834</td>
<td valign="middle" align="left">1.76</td>
<td valign="middle" align="left"><bold>0.008</bold></td>
</tr>
<tr>
<td valign="middle" align="left">Residual</td>
<td valign="middle" align="left">0.70475</td>
<td valign="middle" align="left"/>
<td valign="middle" align="left"/>
</tr>
<tr>
<td valign="middle" align="left">Total</td>
<td valign="middle" align="left">1</td>
<td valign="middle" align="left"/>
<td valign="middle" align="left"/>
</tr>
</tbody>
</table>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" colspan="4" align="left">(B)</th>
</tr>
</thead>
<tbody>
<tr>
<th valign="middle" align="left">Plant group comparison</th>
<th valign="middle" align="left">R<sup>2</sup></th>
<th valign="middle" align="left">F</th>
<th valign="middle" align="left">Pr (&gt;F)</th>
</tr>
<tr>
<td valign="middle" align="left">Teosinte vs. Mexican maize</td>
<td valign="middle" align="left">0.81582</td>
<td valign="middle" align="left">203.75</td>
<td valign="middle" align="left"><bold>0.001</bold></td>
</tr>
<tr>
<td valign="middle" align="left">Mexican maize vs. US maize</td>
<td valign="middle" align="left">0.008871</td>
<td valign="middle" align="left">0.41</td>
<td valign="middle" align="left">0.765</td>
</tr>
<tr>
<th valign="middle" align="left">Genotype comparison</th>
<th valign="middle" align="left">R<sup>2</sup></th>
<th valign="middle" align="left">F</th>
<th valign="middle" align="left">P<sub>adj</sub></th>
</tr>
<tr>
<td valign="middle" align="left">Perennial teosinte vs. Balsas teosinte</td>
<td valign="middle" align="left">0.02135</td>
<td valign="middle" align="left">0.72</td>
<td valign="middle" align="left">0.625</td>
</tr>
<tr>
<td valign="middle" align="left">Balsas teosinte vs. Mexican landrace</td>
<td valign="middle" align="left">0.81006</td>
<td valign="middle" align="left">140.7</td>
<td valign="middle" align="left"><bold>0.002</bold></td>
</tr>
<tr>
<td valign="middle" align="left">Mexican landrace vs. Mexican inbred</td>
<td valign="middle" align="left">0. 18914</td>
<td valign="middle" align="left">2.56</td>
<td valign="middle" align="left">0.137</td>
</tr>
<tr>
<td valign="middle" align="left">Mexican landrace vs. US landrace</td>
<td valign="middle" align="left">0.11642</td>
<td valign="middle" align="left">2.37</td>
<td valign="middle" align="left">0.123</td>
</tr>
<tr>
<td valign="middle" align="left">Us landrace vs. US inbred</td>
<td valign="middle" align="left">0.06586</td>
<td valign="middle" align="left">2.32</td>
<td valign="middle" align="left">0.126</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Significant values are indicated in bold.</p></fn>
</table-wrap-foot>
</table-wrap>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Violin plot illustrates distance to centroid based on Euclidean dissimilarity metric, demonstrating variability in maize genotypes across the effect of life history, domestication, northward spread, and breeding. The x-axis represents plant group and genotypes: Teosinte (perennial and Balsas teosinte), Mexican maize (Mexican landrace and inbred), and US maize (US landrace and inbred).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="frmbi-05-1735358-g005.tif">
<alt-text content-type="machine-generated">Violin plots compare Euclidean distance to centroid among teosinte, Mexican maize, and U.S. maize groups. Statistical significance is shown, with largest variation and distances observed in U.S. maize groups. Colors distinguish categories.</alt-text>
</graphic></fig>
<p>The beta-nearest taxon index (&#x3b2;NTI) is a critical metric for elucidating the processes governing microbial community assembly, distinguishing between deterministic and stochastic influences. A &#x3b2;NTI value &gt; 2 signifies that heterogeneous selection drives community composition, where varying environmental pressures across sites lead to greater phylogenetic divergence and reduced taxonomic overlap compared to random expectations. Conversely, a &#x3b2;NTI &lt; -2 indicates homogeneous selection, wherein consistent environmental conditions promote phylogenetic convergence and tighter community clustering. Values of &#x3b2;NTI between -2 and 2 align with the null model, suggesting that stochastic processes, such as random dispersal, ecological drift, or historical contingencies, predominantly shape community composition. In this study, teosintes were found to have &#x3b2;NTI values &lt; -2, indicating a dominance of deterministic processes, whereas Mexican and US maize genotypes exhibited &#x3b2;NTI values between -2 and 2, suggesting stochastic processes as the primary drivers of community assembly (<xref ref-type="fig" rid="f6"><bold>Figure&#xa0;6A</bold></xref>). Furthermore, the proportions of deterministic and stochastic influences were quantified, revealing that deterministic processes had a stronger effect on teosintes, while Mexican and US maize genotypes were predominantly shaped by stochastic processes with a smaller contribution from deterministic factors (<xref ref-type="fig" rid="f6"><bold>Figure&#xa0;6B</bold></xref>).</p>
<fig id="f6" position="float">
<label>Figure&#xa0;6</label>
<caption>
<p>The boxplot illustrates the &#x3b2;NTI values across maize genotypes <bold>(A)</bold>, while the stacked bar plot shows the proportions of stochastic (orange) and deterministic (blue) processes contributing to community assembly within each genotype group <bold>(B)</bold>. Teosintes exhibited &#x3b2;NTI values &lt; -2, indicating a stronger influence of deterministic processes. In contrast, Mexican and US maize genotypes displayed &#x3b2;NTI values between -2 and 2, suggesting that community assembly in these groups was primarily governed by stochastic processes, with a comparatively smaller contribution from deterministic factors.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="frmbi-05-1735358-g006.tif">
<alt-text content-type="machine-generated">Panel A shows a boxplot of betaNTI values for six genotypes, with perennial teosinte and Balsas teosinte displaying lower median betaNTI than landrace and inbred groups. Panel B is a stacked bar chart illustrating deterministic and stochastic process proportions by genotype, revealing an increasing proportion of stochastic processes from perennial teosinte through to US inbred.</alt-text>
</graphic></fig>
<p>The LDA effect sizes (LEfSe) analysis, with LDA score cutoff at 4 and alpha value of 0.05, was conducted to identify biomarker taxa at the order level. Single order exceeded the cutoff in the Mexican inbred line and US inbred line genotypes two orders in the Mexican landrace genotype, eight in the Balsas teosinte genotype, four in the perennial teosinte genotype, and none in the US landrace genotype (<xref ref-type="fig" rid="f7"><bold>Figure&#xa0;7</bold></xref>). Comparisons of each genotype as a paired group were further analyzed to identify significantly enriched taxa based on the Kruskal-Wallis rank-sum test (&#x3b1; = 0.05) (<xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Figure S6</bold></xref>). LEfSe analysis showed most of the differentially abundant taxa were enriched in the teosinte genotypes, both perennial and Balsas. In genotype-wise comparisons, most of the differentially abundant taxa were similarly enriched in the teosinte genotypes(<xref ref-type="supplementary-material" rid="SM1"><bold>Supplementary Figure S6</bold></xref>).</p>
<fig id="f7" position="float">
<label>Figure&#xa0;7</label>
<caption>
<p>Linear discriminant analysis (LDA) effect size (LEfSe) analysis of biomarker taxa at order level among maize genotypes. Horizontal bars represent enriched taxa and the effect size of each taxon, and the colors indicate the genotype. LDA score cutoff 4 with an alpha value of 0.05 was used to distinguish bacterial taxon. LEfSe analysis indicates that the majority of differentially abundant taxa were more prevalent in the teosinte genotypes, including both perennial and Balsas varieties. Mexican inbred and US inbred line genotypes had one taxon at the order level. There were two orders in Mexican landrace. Balsas teosinte exhibited eight orders, while the perennial teosinte showed four.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="frmbi-05-1735358-g007.tif">
<alt-text content-type="machine-generated">Horizontal bar chart displaying LDA scores for various bacterial orders grouped by plant types. Blue bars represent perennial teosinte, green is Balsas teosinte, red is Mexican landrace, yellow is Mexican inbred, and orange is US inbred.</alt-text>
</graphic></fig>
<p>Lastly, FAPROTAX functional prediction analysis showed that the perennial and Balsas teosinte genotypes had higher nitrate and nitrogen respiration interactions than the maize genotypes (<xref ref-type="fig" rid="f8"><bold>Figure&#xa0;8</bold></xref>). In contrast, the US inbred- and US landrace maize genotypes, followed by Mexican inbred and Mexican landrace genotypes had higher fermentation and nitrate reduction interactions compared to the teosinte genotypes (<xref ref-type="fig" rid="f8"><bold>Figure&#xa0;8</bold></xref>).</p>
<fig id="f8" position="float">
<label>Figure&#xa0;8</label>
<caption>
<p>Functional Annotation of Prokaryotic Taxa (FAPROTAX) analysis of leaf endosphere of maize genotypes. FAPROTAX predictions indicated that the teosintes exhibited higher cellulolytic, chitinolytic, nitrogen respiration, and nitrate respiration functions, while maize landraces and elite inbreds displayed higher fermentation and nitrate reduction functions.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="frmbi-05-1735358-g008.tif">
<alt-text content-type="machine-generated">Heatmap visualizing functional microbial profiles across six genotypes: perennial teosinte, Balsas teosinte, Mexican landrace, Mexican inbred, US landrace, and US inbred. Functions are grouped into C-cycle, energy source, N-cycle, and other categories. Aerobic chemoheterotrophy and nitrate reduction show the highest proportions, indicated by darker red, particularly in US inbred and Mexican inbred genotypes. Color gradient bar on the right reflects proportions ranging from zero to 0.5 percent. Function and genotype labels are clearly shown on axes.</alt-text>
</graphic></fig>
</sec>
<sec id="s4" sec-type="discussion">
<title>Discussion</title>
<p>In this study, we examined the leaf endosphere microbiota of a suite of six teosinte and maize (<italic>Zea</italic> spp.) genotypes spanning the evolution of maize from teosintes (perennial and Balsas teosinte) to maize landraces (Fr. Mexico and United States) and maize elite inbreds (Fr. Mexico and United States). Through comparisons among those six genotypes, we inferred on effects of transitioning from perennial to annual life history in the teosintes (perennial vs Balsas teosinte), domestication (Balsas teosinte vs Mexican landrace maize), northward spread (Mexican vs US landrace maize), and breeding (Mexican and US landrace vs Mexican and US inbred maize). In line with Anna Karenina principle predictions (<xref ref-type="bibr" rid="B140">Zaneveld et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B27">Chen et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B10">Arnault et&#xa0;al., 2023</xref>), we expected that teosinte&#x2019;s transition from perennial to annual life history, and maize domestication, northward spread, and breeding would be associated with increasing variability in bacterial communities driven by stochastic processes. Importantly, we found that domestication in particular, evident both in comparisons between the Balsas teosinte and Mexican landrace genotypes, as well as between teosintes and maizes broadly, was associated with decreasing leaf endosphere bacterial diversity and increasing variability in bacterial communities. This suggested that dysbiosis is associated with maize domestication. Below, we discuss our results showing that maize domestication significantly affected &#x3b1;-diversity and &#x3b2;-diversity of the leaf endosphere microbial community, and other differences in the structure and assemblage of the leaf endosphere microbial community associated with maize domestication, northward spread, and breeding.</p>
<sec id="s4_1">
<title>Maize domestication significantly affected &#x3b1;-diversity and &#x3b2;-diversity of leaf endosphere microbial community</title>
<p>We found that the Shannon and Chao1 diversity values in the Balsas teosinte genotype were higher than in the Mexican landrace genotype, and that generally they were higher in the teosintes compared to the maizes. We propose that the reductions are due to an increasing dominance of stochastic over deterministic processes mediating the leaf microbiome&#x2019;s assemblage. The diversity decreases both in Mexican landrace maize and maizes combined relative to their predecessors indicate that the decreases are associated with domestication, and in parallel with a transition from plant survival and reproduction in a highly variable natural environment to a typically richer and more predictable agricultural environment (<xref ref-type="bibr" rid="B17">Bernal and Medina, 2018</xref>; <xref ref-type="bibr" rid="B43">Fontes-Puebla and Bernal, 2020</xref>). In contrast, there were no significant changes in diversity associated with the transition from perennial to annual life history, northward maize spread, and breeding. To our knowledge, ours is the first study reporting a significant decay in leaf endosphere bacterial diversity and richness associated with maize domestication. Importantly, our study reveals significantly higher bacterial diversity and richness in the leaf endosphere of Balsas teosintes compared to the maize inbreds that serve as parents of commercial hybrid varieties, while highlighting a decline in bacterial diversity with likely implications for maize productivity in environments under stress from climate change.</p>
<p>Our PCoA analysis revealed a clear divergence between teosinte and maize in variation, in addition to diversity, associated with their leaf bacterial communities. In addition, our study highlighted distinct patterns in the clustering of teosintes, including perennial and Balsas teosinte, compared to the more variable distributions observed in maize landraces and elite inbreds. Notably, the beta diversity in leaf bacterial communities exhibited variations among plant groups, with teosinte displaying higher diversity in the leaf endosphere than the maize groups. Consistently, a previous study on the microbiome of wild and domesticated wheat species showed that the bacterial communities in the leaves of wild wheat species were more phylogenetically clustered compared to the bacterial communities in domesticated wheat (<xref ref-type="bibr" rid="B52">Hassani et&#xa0;al., 2020</xref>). In terms of the maize leaf endosphere microbiota study, previous studies have demonstrated no significant differences in the beta diversity of leaf-associated bacterial assemblages among modern maize cultivars (<xref ref-type="bibr" rid="B65">Kong et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B124">Wagner et&#xa0;al., 2020b</xref>). This is consistent with studies showing that host plants play important roles in shaping their endophytic bacteria communities (<xref ref-type="bibr" rid="B4">Agler et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B124">Wagner et&#xa0;al., 2020b</xref>; <xref ref-type="bibr" rid="B136">Xiong et&#xa0;al., 2021b</xref>; <xref ref-type="bibr" rid="B105">Singh et&#xa0;al., 2023</xref>). Thus, variation in the diversity between teosinte and maize plant groups in this study can be attributed to the selectiveness of the host plant. In addition, such selection may be correlated with host plant functional traits and ecological strategies (<xref ref-type="bibr" rid="B63">Kembel et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B68">Laforest-Lapointe et&#xa0;al., 2017</xref>). Any underlying mechanisms and consequences of diminished selection effect remain to be explored.</p>
<p>Collectively, we observed increased beta-diversity and decreased alpha-diversity in leaf-associated bacterial communities coincident with maize domestication. This pattern is observed both in comparisons between Balsas teosinte and Mexican landrace genotypes, as well as more broadly between teosintes and maizes. This is potentially due to decreased selection and increased relevance of stochastic processes. Patterns similar to these are also noted in association with stress in plants and other hosts, including humans and animals (<xref ref-type="bibr" rid="B115">Turnbaugh et&#xa0;al., 2009</xref>; <xref ref-type="bibr" rid="B3">Abrahamsson et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B140">Zaneveld et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B96">Rocca et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B70">Lavrinienko et&#xa0;al., 2020</xref>). For instance, mutations of immunity-related genes in <italic>Arabidopsis</italic>, and disease in Korean fir and chili pepper were associated with reductions in the diversity of their microbial communities (<xref ref-type="bibr" rid="B27">Chen et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B45">Gao et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B50">Han et&#xa0;al., 2022</xref>). Seemingly, hosts lose beneficial microbiota due to stochastic processes associated with stress. Additionally, the negative effects of stresses are compounded by dysbiosis, following Anna Karenina Principle predictions (AKP) (<xref ref-type="bibr" rid="B93">Petersen and Round, 2014</xref>; <xref ref-type="bibr" rid="B117">Vangay et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B72">Levy et&#xa0;al., 2017</xref>). AKP suggests a rise of stochastic over deterministic processes mediating microbial community composition within the holobiont (<xref ref-type="bibr" rid="B140">Zaneveld et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B5">Ahmed et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B10">Arnault et&#xa0;al., 2023</xref>). We found that teosintes exhibited &#x3b2;NTI values &lt; -2, indicating a stronger influence of deterministic processes, whereas Mexican and US maize genotypes showed &#x3b2;NTI values between -2 and 2, highlighting the predominance of stochastic processes with a smaller contribution from deterministic factors. The proportions of deterministic and stochastic influences further supported these observations. The decline in diversity and increase in variability in the bacterial community of the maize leaf endosphere observed in this study reveal patterns suggestive of dysbiosis. The increased variability within the bacterial community is consistent with AKP. We suggest that the maize leaf endosphere exhibits patterns akin to dysbiosis. The decline in the diversity of microbial species in leaf endosphere of the maizes compared with the teosintes may impact the crop&#x2019;s ability to cope with biotic and abiotic stresses (<xref ref-type="bibr" rid="B49">Gutierrez and Grillo, 2022</xref>; <xref ref-type="bibr" rid="B6">Alam and Purugganan, 2024</xref>), particularly as environments change rapidly under climate change. Although we identified microbial signatures of dysbiosis through AKP, we did not evaluate the functions of the leaf endosphere microbiota in host fitness in this study. These results provide a basis for future investigations into the effects of leaf endosphere microbial functions in teosintes and maize on host fitness.</p>
<p>Current knowledge of plant microbiome dysbiosis, although limited, is largely derived from studies of pathogenic plant states. However, evidence also indicates that dysbiosis can result from host genetic disruptions that impair microbiota homeostasis, such as loss of TIP1 function, environmental stressors, and agricultural practices. <xref ref-type="bibr" rid="B30">Cheng et&#xa0;al. (2024)</xref> identified TIP GROWTH DEFECTIVE 1 (TIP1) as a key regulator of leaf microbiota homeostasis in <italic>Arabidopsis</italic>. Loss of TIP1 function under high-humidity conditions led to dysbiosis, marked by a &gt;1,000-fold increase in endophytic bacterial load, reduced microbial diversity, and dominance of <italic>Pseudomonas</italic> and <italic>Stenotrophomonas</italic>, while beneficial taxa such as <italic>Bacillus</italic> and <italic>Paenibacillus</italic> were nearly eliminated. This microbial imbalance was associated with chlorosis, tissue lesions, and constitutive activation of immune genes, consistent with an autoimmune-like phenotype. These symptoms were absent under axenic conditions, indicating that the immune responses were microbiota dependent. Transfer of the dysbiotic microbiota from tip1 plants to healthy plants induced disease-like symptoms, demonstrating that the altered microbial community alone was sufficient to cause tissue damage. Together, these findings show that disruption of host control over the leaf microbiota results in dysbiosis-associated autoimmunity, linking microbial imbalance to immune dysfunction in plants. Moreover, <xref ref-type="bibr" rid="B130">Wasimuddin et&#xa0;al. (2025)</xref> reported that chemical stressors, including arsenic and the herbicide terbuthylazine, induced dysbiosis in soil microbiomes. Exposure to these compounds significantly reduced bacterial richness and diversity, indicating a loss of microbial balance. Community composition shifted toward stress-tolerant taxa such as <italic>Flavobacteriaceae</italic>, <italic>Burkholderiaceae</italic>, and <italic>Xanthomonadaceae</italic>, suggesting functional reorganization under chemical stress. Soil microbial interaction networks were also altered, reflecting changes in community structure and stability. Collectively, these findings demonstrate that chemical stressors drive dysbiosis in soil microbiomes. In another study, <xref ref-type="bibr" rid="B33">Darriaut et&#xa0;al. (2024)</xref> demonstrated that grapevine decline was associated with microbial dysbiosis, characterized by shifts in the composition, diversity, and functional potential of belowground microbiomes across bulk soil, rhizosphere, and root endosphere compartments. Symptomatic vines exhibited reduced microbial richness, enrichment of stress-tolerant and potentially pathogenic taxa, and decreased mycorrhizal colonization, indicating a loss of microbial balance. The authors suggested that long-term soil management practices and the resulting decline in soil microbial resilience likely contributed to this dysbiosis, promoting the dominance of stress-adapted and pathogenic microorganisms over beneficial symbionts.</p>
<p>Teosintes defend against herbivorous insects and pathogens by a variety of means (<xref ref-type="bibr" rid="B98">Rosenthal and Welter, 1995</xref>; <xref ref-type="bibr" rid="B97">Rosenthal and Dirzo, 1997</xref>; <xref ref-type="bibr" rid="B112">Takahashi et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B110">Szczepaniec et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B26">Chavan, 2014</xref>; <xref ref-type="bibr" rid="B34">de Lange et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B18">Bernal et&#xa0;al., 2015</xref>), and differences in defense strengths and strategies between teosinte and maize seem to be associated with their divergent environments, i.e. typically poorer, wild environments for the former and richer, agricultural environments for the latter (<xref ref-type="bibr" rid="B43">Fontes-Puebla and Bernal, 2020</xref>; <xref ref-type="bibr" rid="B44">Fontes-Puebla et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B16">Bernal et&#xa0;al., 2023</xref>). Examining the diversity of leaf endosphere microbiota in wild crop relatives may provide insights to how traits that allow plants to survive in the wild can, alongside other enhancements, be utilized to improve the breeding process. Previous studies revealed effects of maize host genetics and environmental conditions on how domestication and breeding shaped rhizosphere-associated microbiomes. <xref ref-type="bibr" rid="B21">Brisson et&#xa0;al. (2019)</xref> demonstrated that hybrid breeding significantly altered rhizosphere microbial communities, with inbred maize lines harboring communities more similar to teosintes than to modern hybrids under nutrient-depleted soils. <xref ref-type="bibr" rid="B14">Barnes et&#xa0;al. (2024)</xref> further reported that root microbiomes differed between teosintes and modern maize, and that teosinte accessions from distinct native environments harbored unique microbial groups associated with temperature and elevation. <xref ref-type="bibr" rid="B55">Huang et&#xa0;al. (2022)</xref> showed that domestication and genetic improvement increased rhizobacterial diversity and modified network structure, with inbreds exhibiting greater modularity than teosintes and landraces. In contrast to these belowground findings, our analysis of leaf endophytic communities indicated that domestication was associated with reduced bacterial diversity and greater variability in community composition in the endosphere of maize landraces and inbreds relative to teosintes. Collectively, these results suggest that while domestication and&#xa0;breeding often enhanced microbial diversity and functional&#xa0;adaptability in the rhizosphere, they simultaneously imposed&#xa0;losses in stability in the leaf endosphere, providing the&#xa0;first&#xa0;evidence of endophytic dysbiosis associated with crop domestication.</p>
</sec>
<sec id="s4_2">
<title>Differences in the structure and assemblage of leaf endosphere microbial community associated with maize domestication, northward spread, and breeding</title>
<p>We found that Bacteroidetes and Actinobacteria (both Proteobacteria) were the most dominant taxa in the leaf endosphere bacterial communities. Similar compositions have been found in studies of different plant varieties such as the phyllosphere microbiome of sorghum (<xref ref-type="bibr" rid="B109">Sun et&#xa0;al., 2021</xref>), leaf endosphere of prairie plants (<xref ref-type="bibr" rid="B35">Ding and Melcher, 2016</xref>), and leaf microbiota of <italic>Arabidopsis</italic> (<xref ref-type="bibr" rid="B19">Bodenhausen et&#xa0;al., 2013</xref>). Furthermore, we observed a decline in the relative abundance of several taxa from the teosinte group, including perennial and Balsas teosinte, to the maize inbred lines, including <italic>Devosia</italic> and <italic>Caulobacter</italic> (Proteobacteria), and <italic>Stenotrophomonas and Pseudomonas</italic> (Pseudomonadota). Moreover, five genera showed higher abundance in maize plant group, <italic>Pantoea, Staphylococcus, Acinetobacter, Corynebacterium, Ralstonia</italic>. These results are consistent with those of previous research (<xref ref-type="bibr" rid="B122">Wagner et&#xa0;al., 2020a</xref>) which identified <italic>Pantoea</italic> spp. as the dominant taxa in hybrid maize cultivars at an early growth stage. Similarly, our study highlighted <italic>Pantoea and Ralstonia</italic> as dominant taxa in leaf samples from elite inbred lines, including lines from Mexico and US. Additionally, <italic>Staphylococcus</italic> and <italic>Corynebacterium</italic> were also among the top 20 genera in the relative abundance analysis of that research (<xref ref-type="bibr" rid="B122">Wagner et&#xa0;al., 2020a</xref>). Interestingly, the depleted genera observed in elite inbred maize in our study were also not detected in the previous research. Previous studies have demonstrated that taxa within these genera can exhibit either plant growth-promoting or biocontrol functions, or act as plant pathogens. For instance, <italic>Pantoea agglomerans</italic> has been shown to promote plant growth (<xref ref-type="bibr" rid="B78">Luziatelli et&#xa0;al., 2020</xref>), whereas <italic>Pantoea stewartii</italic> subsp. <italic>stewartii</italic> is the causal agent of Stewart&#x2019;s wilt disease in maize (<xref ref-type="bibr" rid="B38">Farthing et&#xa0;al., 2025</xref>). The functional roles of these taxa enriched in maize may therefore differentially influence host plant performance. Future studies should aim to classify maize-enriched endophytic leaf taxa at the species level to distinguish beneficial from pathogenic bacteria and to experimentally assess their functional effects on the host plant.</p>
<p>We identified a few OTUs as known beneficial bacteria, though we did not test their functional properties. For example, we identified <italic>Methylobacterium</italic> spp., which are well known phyllosphere colonizers with documented beneficial effects, e.g., production of phytohormones, and enhancement of seed germination and plant growth (<xref ref-type="bibr" rid="B90">Omer et&#xa0;al., 2004</xref>; <xref ref-type="bibr" rid="B80">Madhaiyan et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B1">Abanda-Nkpwatt et&#xa0;al., 2006</xref>; <xref ref-type="bibr" rid="B91">Palberg et&#xa0;al., 2022</xref>). Previous studies consistently reported Methylobacteriaceae as the most abundant or as a biomarker taxon for leaf microbiota studies in maize (<xref ref-type="bibr" rid="B126">Wallace et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B137">Xueliang et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B136">Xiong et&#xa0;al., 2021b</xref>). In our study, we did not observe Methylobacteriaceae as an indicator taxon among genotypes in LEfSe analysis, though they were found to be more abundant in the teosinte plant group than in Mexican and US elite inbred genotypes. Moreover, we identified that classes Xanthomonadales, Actinomycetales, Burkholderiales, Rhizobiales were enriched in the teosinte group and Mexican landrace genotype as potential biomarkers with different abundances. This is in line with <xref ref-type="bibr" rid="B135">Xiong et&#xa0;al. (2021a)</xref> who found Actinobacteria, Burkholderiaceae, and Rhizobiaceae to be abundant in the phylloplane and rhizosphere of maize during the seedling stage, even if they were not identified as biomarker taxa. Many strains within those taxa establish beneficial partnerships with their host plants, including biological nitrogen fixation, plant growth stimulation, and protection against plant pathogens (<xref ref-type="bibr" rid="B32">Conn et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B36">Erlacher et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B7">Alvarez et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B125">Wahyudi et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B58">Jaiswal et&#xa0;al., 2021</xref>). Our findings demonstrated that biomarker taxa of teosinte were significantly more enriched in that plant group when compared to elite inbred lines, suggesting that wild ancestors may harbor greater diversity of beneficial taxa than crops. Such enriched bacterial taxa may confer functional advantages to their host plants, including increased tolerance of biotic and abiotic stress and greater adaptability to new environments. Further study is needed to better understand the correlations and functions of these taxa in crop wild ancestors, as well as for harnessing them to improve plant growth and health in crops.</p>
<p>We found that the core microbiome consists of 36 taxa shared across six genotypes. The predominant classes within this central core microbiome were Alphaproteobacteria, Gammaproteobacteria, Actinobacteria, and Betaproteobacteria. The taxonomic affiliations observed in our findings are similar to those in other crop studies on the core microbiome of phyllosphere bacterial communities, e.g., tree leaves (<xref ref-type="bibr" rid="B63">Kembel et&#xa0;al., 2014</xref>), grasses (<xref ref-type="bibr" rid="B48">Grady et&#xa0;al., 2019</xref>), and <italic>Arabidopsis thaliana</italic> (<xref ref-type="bibr" rid="B19">Bodenhausen et&#xa0;al., 2013</xref>). Moreover, <xref ref-type="bibr" rid="B61">Johnston-Monje and Raizada (2011)</xref> detected a core microbiota of endophytes that remained conserved in <italic>Zea</italic> seeds. Core microbial communities establish enduring relationships with plant hosts and crucially influence biological processes of their host plants (<xref ref-type="bibr" rid="B113">Tian et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B107">Stopnisek and Shade, 2021</xref>; <xref ref-type="bibr" rid="B141">Zhang et&#xa0;al., 2022</xref>). Our finding provides insight into core bacteriome taxa in the leaf endosphere as shaped by maize domestication and breeding. We suggest that a core bacterial community potentially coexists in mutual syntrophy, which provided a reproducible and conserved suite of taxa during maize domestication and breeding. Further studies are needed to understand the functions of the core bacterial community in relation to the biological functions of the maize host plant.</p>
<p>We used FAPROTAX analyses to evaluate potential functions of the microbiota of the different plant genotypes. While not conclusive, results from these analyses are useful for indicating future research directions concerning the functional ecology of endophytic bacteria and their host plants. Ecological functions and functional abundance of microbial communities can vary with plant type, plant development, and environment, among other variables (<xref ref-type="bibr" rid="B143">Zhou et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B136">Xiong et&#xa0;al., 2021b</xref>; <xref ref-type="bibr" rid="B29">Cheng et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B74">Liu et&#xa0;al., 2022</xref>). Regulation of functional groups and shifts in functional groups indicate that plant-recruited microbes reflect the current needs of the host plant (<xref ref-type="bibr" rid="B143">Zhou et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B29">Cheng et&#xa0;al., 2022</xref>). The results of FAPROTAX suggested that nitrate reduction, nitrate respiration, fermentation, and cellulolytic activities were most prominent in the two teosinte genotypes, while nitrate reduction and fermentation were prominent among the four maize genotypes. The latter results align with findings from a previous study on maize hybrids (<xref ref-type="bibr" rid="B136">Xiong et&#xa0;al., 2021b</xref>). Our findings provide predicted potential functions of the active microbial community in leaf endosphere. However, experimental research is essential to validate and confirm the predicted functional roles of these bacteria in enhancing plant fitness.</p>
<p>In addition to genotype, plant developmental stage and age affect phyllosphere microorganisms through the release of specific hormones and biologically active compounds. Previous research has shown that plant phenology is a major factor influencing the assembly of both phyllosphere and rhizosphere microbiomes (<xref ref-type="bibr" rid="B123">Wagner et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B81">Manching et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B127">Walters et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B135">Xiong et&#xa0;al., 2021a</xref>). <xref ref-type="bibr" rid="B24">Chaparro et&#xa0;al. (2014)</xref> reported that plants are able to select particular groups of microbes at different stages of development and suggested that this process is mediated by the secretion of distinct mixtures of compounds and phytochemicals in root exudates that vary across developmental stages, thereby contributing to the recruitment of the rhizosphere microbiome. Further, <xref ref-type="bibr" rid="B123">Wagner et&#xa0;al. (2016)</xref> showed that both leaf and root microbiome composition changes with plant age, especially during early to mid-vegetative growth. Thus, a limitation of the present study is that the impact of leaf ontogeny on leaf endophytic bacterial communities in teosinte and maize was not evaluated. Leaves from each genotype were collected at a single developmental stage, namely the five-week vegetative stage, when plants were approximately at the V4-V5 growth stage with four to six fully collared leaves. Leaf ontogeny was not considered, as accurately determining the ontogenetic stage of individual leaves is challenging. Consequently, this study could not assess changes in leaf endophytic bacterial community composition across different stages of leaf ontogeny in teosinte and maize. Future studies using time-series sampling across multiple developmental stages and evaluating the effects of plant ontogeny on microbial recruitment would provide insight into the temporal dynamics of endophytic microbiome assembly.</p>
<p>The environment in which experiments are conducted is an important determinant of microbiome assembly. Greenhouse and field experiments can yield different outcomes in microbiome studies because multiple environmental factors influence microbial community composition, and microbial assemblages are known to shift under conventional agricultural conditions (<xref ref-type="bibr" rid="B123">Wagner et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B40">Favela et&#xa0;al., 2024</xref>). Because this study focused on host genotype effects on the leaf endosphere microbiota while minimizing environmental variation, experiments were conducted under controlled greenhouse conditions. Consequently, the findings cannot be extrapolated to absolute microbiome status under natural field conditions. Future studies should examine leaf endosphere microbiota of teosintes and maize in natural habitats, including the effects of environmental factors on these communities.</p>
</sec>
</sec>
<sec id="s5" sec-type="conclusions">
<title>Conclusion</title>
<p>The findings presented here suggest that maize domestication played a pivotal role in shaping the assembly of maize leaf endophytes, with the plant genotype being a primary driver of this assembly. This was particularly evident in our comparisons between Balsas teosinte and Mexican landrace maize. Indeed, those comparisons showed significant declines of microbial diversity in the leaf endosphere associated with maize domestication. Strikingly, we found a signature of microbial dysbiosis is also associated with maize domestication. Particularly, a shift in microbial community structure from highly stringent and regulated in Balsas teosinte to loose and unregulated in maize, especially in Mexican landrace maize, the immediate descendant of Balsas teosinte. Taken together, these results are in line with and add support to the Anna Karenina principle in microbial dysbiosis and represent the first evidence of microbial signatures of dysbiosis caused by plant domestication. Also, our study demonstrated that teosintes harbor a greater number of biomarker taxa than maize landraces and elite inbred cultivars. Collectively, our results suggested that the leaf endophytic bacterial assembly in maize was markedly influenced by its domestication.</p>
<p>Altogether, our study contributes to the characterization of the leaf-associated endophytic microbiota composition of maize wild ancestors, landraces, and elite inbred lines. The insights from our research set the stage for advancements in biological control, biofertilizer technologies, and maize breeding strategies, particularly through the examination of microbiomes of wild relative genotypes. Identifying beneficial bacterial microbes and understanding their functions is essential for developing microbial technologies for enhancing the sustainability and resilience of agricultural practices.</p>
</sec>
</body>
<back>
<sec id="s6" sec-type="data-availability">
<title>Data availability statement</title>
<p>The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found below: <uri xlink:href="https://www.ncbi.nlm.nih.gov/bioproject/PRJNA1137996">https://www.ncbi.nlm.nih.gov/bioproject/PRJNA1137996</uri>.</p></sec>
<sec id="s7" sec-type="author-contributions">
<title>Author contributions</title>
<p>IT: Writing &#x2013; original draft, Data curation, Visualization, Methodology, Formal analysis. JB: Resources, Investigation, Conceptualization, Supervision, Methodology, Writing &#x2013; review &amp; editing, Data curation. SA: Writing &#x2013; review &amp; editing, Conceptualization, Supervision, Resources, Investigation, Funding acquisition.</p></sec>
<ack>
<title>Acknowledgments</title>
<p>We would like to thank Prof. Dr. Michael V. Kolomiets for providing Mexican and USA elite inbred line seeds, and Arial Black, Kathy Gonzalez, Elek Nagy, and Sabin Khanal for their generous help in plant harvesting. We thank Vanessa E. Thomas for helping with R codes and Sabin Khanal for the microbiome analyses pipeline.</p>
</ack>
<sec id="s9" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p></sec>
<sec id="s10" sec-type="ai-statement">
<title>Generative AI statement</title>
<p>The author(s) declared that generative AI was not used in the creation of this manuscript.</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p></sec>
<sec id="s11" sec-type="disclaimer">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p></sec>
<sec id="s12" sec-type="supplementary-material">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/frmbi.2026.1735358/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/frmbi.2026.1735358/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="SupplementaryFile1.docx" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document"/></sec>
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<p>Edited by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2360044">Divya Joshi</ext-link>, G. B. Pant University of Agriculture and Technology, India</p></fn>
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<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/219097">Eman Mohammad Khalaf</ext-link>, Damanhour University, Egypt</p>
<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2975441">Navdeep Sharma</ext-link>, Patanjali Research Institute, India</p></fn>
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