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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Microbiol.</journal-id>
<journal-title>Frontiers in Microbiology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Microbiol.</abbrev-journal-title>
<issn pub-type="epub">1664-302X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-meta>
<article-id pub-id-type="doi">10.3389/fmicb.2023.1334051</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Microbiology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Unveil of the role of fungal taxa in iron(III) reduction in paddy soil</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Li</surname>
<given-names>Ming-Jun</given-names>
</name>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Ye</surname>
<given-names>Xiao-Xin</given-names>
</name>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Da</surname>
<given-names>Yan-Mei</given-names>
</name>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Sun</surname>
<given-names>Qing-Ye</given-names>
</name>
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<contrib contrib-type="author" corresp="yes">
<name>
<surname>Zhou</surname>
<given-names>Guo-Wei</given-names>
</name>
<xref ref-type="corresp" rid="c001">
<sup>&#x002A;</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1352099/overview"/>
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<aff><institution>School of Resources and Environmental Engineering, Anhui University</institution>, <addr-line>Hefei</addr-line>, <country>China</country></aff>
<author-notes>
<fn fn-type="edited-by" id="fn0003"><p>Edited by: Dong Lu, Chinese Academy of Sciences (CAS), China</p></fn>
<fn fn-type="edited-by" id="fn0004"><p>Reviewed by: Li Hu, Chinese Academy of Sciences (CAS), China; Tao Peng, Shantou University, China</p></fn>
<corresp id="c001">&#x002A;Correspondence: Guo-Wei Zhou, <email>gwzhou@ahu.edu.cn</email></corresp>
</author-notes>
<pub-date pub-type="epub">
<day>24</day>
<month>01</month>
<year>2024</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>14</volume>
<elocation-id>1334051</elocation-id>
<history>
<date date-type="received">
<day>06</day>
<month>11</month>
<year>2023</year>
</date>
<date date-type="accepted">
<day>13</day>
<month>12</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2024 Li, Ye, Da, Sun and Zhou.</copyright-statement>
<copyright-year>2024</copyright-year>
<copyright-holder>Li, Ye, Da, Sun and Zhou</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p>
</license>
</permissions>
<abstract>
<p>Hitherto, research on iron(III)-reduction has mainly focused on bacteria rather than fungal communities. To acquire insight into fungi involved in iron(III) reduction, typical organic matters (containing cellulose, glucose, lactate, and acetate) and ferrihydrite were used as electron donors and acceptors, respectively, in the presence of antibiotics. After antibiotic addition, microbial iron(III) reduction was still detected at quite high rates. In comparison, rates of iron(III) reduction were significantly lower in cellulose-amended groups than those with glucose, lactate, and acetate under the antibiotic-added condition. Patterns of intermediate (e.g., acetate, pyruvate, glucose) turnover were markedly different between treatments with and without antibiotics during organic degradation. A total of 20 genera of potential respiratory and fermentative iron(III)-reducing fungi were discovered based on ITS sequencing and genome annotation. This study provided an insight into the diversity of iron(III)-reducing fungi, indicating the underestimated contribution of fungi to iron and the coupled carbon biogeochemical cycling in environments.</p>
</abstract>
<abstract abstract-type="graphical">
<title>Graphical abstract</title>
<p>
<graphic xlink:href="fmicb-14-1334051-gr0001.tif" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</p>
</abstract>
<kwd-group>
<kwd>fungal taxa</kwd>
<kwd>iron(III) reduction</kwd>
<kwd>organic metabolism</kwd>
<kwd>fermentative iron(III) reducers</kwd>
<kwd>respiratory iron(III) reducers</kwd>
</kwd-group>
<contract-num rid="cn1">42107143</contract-num>
<contract-num rid="cn2">GXXT-2021-061</contract-num>
<contract-num rid="cn3">Z010111022</contract-num>
<contract-sponsor id="cn1">National Natural Science Foundation of China<named-content content-type="fundref-id">10.13039/501100001809</named-content></contract-sponsor>
<contract-sponsor id="cn2">Science Foundation for Young Scholars of Anhui University and Collaborative Innovation Project of Anhui Universities</contract-sponsor>
<contract-sponsor id="cn3">Ecology Peak discipline program</contract-sponsor>
<counts>
<fig-count count="5"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="48"/>
<page-count count="10"/>
<word-count count="5967"/>
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<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Microbiological Chemistry and Geomicrobiology</meta-value>
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</front>
<body>
<sec sec-type="intro" id="sec1">
<label>1</label>
<title>Introduction</title>
<p>Microbial iron(III) reduction can be catalyzed by dissimilatory iron(III)-reducing microorganisms that rely on the utilization of organic matters (e.g., cellulose, glucose, short-chain fatty acids) as substances to support their growth (<xref ref-type="bibr" rid="ref24">Lovley, 1991</xref>; <xref ref-type="bibr" rid="ref17">Kappler et al., 2021</xref>). Iron(III) reducers widely spread under anoxic environments, especially in iron(III)-rich paddy soils (<xref ref-type="bibr" rid="ref25">Lovley, 2006</xref>; <xref ref-type="bibr" rid="ref17">Kappler et al., 2021</xref>). Hitherto, almost all explorations on iron(III) reduction focus on bacterial Fe(III) reducers, which are represented by the well-known <italic>Geobacter</italic> spp. and <italic>Shewanella</italic> spp. (<xref ref-type="bibr" rid="ref27">Lovley and Phillips, 1988</xref>; <xref ref-type="bibr" rid="ref30">Myerst and Nealson, 1990</xref>). The identified iron(III)-reducing bacteria are phylogenetically diverse, including members belonging to Proteobacteria, Chlorobia, Deferribacteracea, Thermodesulfobacteriaceae, etc. (<xref ref-type="bibr" rid="ref44">Weber et al., 2006</xref>). In fact, although the abundances of fungal members are lower than those of bacteria, they (yeast, yeast-like, and filamentous species) are widely distributed in terrestrial ecosystems (<xref ref-type="bibr" rid="ref3">Blackwell, 2011</xref>; <xref ref-type="bibr" rid="ref41">Tedersoo et al., 2014</xref>). Up to now, iron(III) reduction has only been verified for pure culture of a few species, e.g., <italic>Actinomucor repens</italic>, <italic>Alternaria tenuis</italic>, <italic>Fusarium oxysporum</italic>, <italic>F. solani,</italic> and <italic>Cladosporium</italic> spp. (<xref ref-type="bibr" rid="ref36">Ottow and von Klopotek, 1969</xref>; <xref ref-type="bibr" rid="ref31">Natarajan et al., 1997</xref>). Therefore, little is known about the role of iron(III) reduction in fungal communities and the diversity of Fe(III)-reducing fungal taxa in paddy soils.</p>
<p>Organic matters in paddy soils are abundant and complex, encompassing various components such as lignin, cellulose, humic acid, as well as simpler compounds like glucose, lactate, and acetate (<xref ref-type="bibr" rid="ref28">Maie et al., 2002</xref>; <xref ref-type="bibr" rid="ref18">K&#x00F6;gel-Knabner et al., 2010</xref>; <xref ref-type="bibr" rid="ref46">Yan et al., 2013</xref>). Bacteria-mediated Fe(III) reduction is coupled with oxidation of a variety of organic matter, containing fermentative sugars, peptone, organic acids, and H<sub>2</sub> (<xref ref-type="bibr" rid="ref44">Weber et al., 2006</xref>; <xref ref-type="bibr" rid="ref17">Kappler et al., 2021</xref>). Various bacteria which grow through fermentative metabolism are known to transfer just a few electrons to iron(III) oxides (<xref ref-type="bibr" rid="ref23">Lovley, 1987</xref>; <xref ref-type="bibr" rid="ref27">Lovley and Phillips, 1988</xref>). Dissimilarly, the Fe(III)-respiring microorganisms are phylogenetically and morphologically diverse and can conserve energy to support growth during iron(III) reduction coupled to oxidation of organic compounds or hydrogen (<xref ref-type="bibr" rid="ref23">Lovley, 1987</xref>; <xref ref-type="bibr" rid="ref27">Lovley and Phillips, 1988</xref>; <xref ref-type="bibr" rid="ref25">Lovley, 2006</xref>). Actually, abundant anaerobic fungi are also involved in cellulose degradation, sugar fermentation, and acetate dissimilation (<xref ref-type="bibr" rid="ref11">Hess et al., 2020</xref>). Moreover, many of them are recognized for their ability to reduce nitrate or nitrite associated with oxidizing glucose, glycerol, ethanol, acetate and formate (<xref ref-type="bibr" rid="ref47">Zhou et al., 2002</xref>; <xref ref-type="bibr" rid="ref19">Kuwazaki et al., 2003</xref>; <xref ref-type="bibr" rid="ref2">Aldossari and Ishii, 2021</xref>). Certain fungal species, such as <italic>Fusarium oxysporum</italic>, have demonstrated the capability to oxidize acetate coupled with sulfur reduction (<xref ref-type="bibr" rid="ref1">Abe et al., 2007</xref>). However, limited information is available regarding the response of anaerobic fungal communities to the reduction of iron(III) minerals associated with the oxidation of various organic substances.</p>
<p>We hypothesized that the capacity of anaerobic fungi to reduce iron(III) oxides is linked to the degradation of organic compounds. In this study, we employed anaerobic microcosm cultures using typical paddy soil. We amended the soil with common organics including cellulose, glucose, lactate, and acetate. In order to further highlight the potential role of fungi in iron(III) reduction, treatments with antibiotic combinations were set up simultaneously. The combination of antibiotics aimed to suppress bacterial activity by inhibiting the synthesis of cell wall and ribosomes by vancomycin and streptomycin during the incubation, respectively (<xref ref-type="bibr" rid="ref6">Cox et al., 1964</xref>; <xref ref-type="bibr" rid="ref39">Sieradzki and Tomasz, 1997</xref>). The main objective of this study was to: (1) prove that iron(III) reduction occurs in fungi by adding antibiotics to inhibit bacterial activity; (2) identify associated fungal taxa that can potentially reduce iron(III); (3) explore interaction between iron(III)-reducing fungi in response to different organic substrates in a paddy soil.</p>
</sec>
<sec sec-type="materials|methods" id="sec2">
<label>2</label>
<title>Materials and methods</title>
<sec id="sec3">
<label>2.1</label>
<title>Soil sample collection</title>
<p>Soil samples were collected on 11th in April (2022) from a paddy field irrigated by mining waste water in Yi&#x2019;an District, Tongling City, Anhui Province, China (117&#x00B0;79&#x2032; E, 30&#x00B0;95&#x2032; N), currently under soil remediation. The field is planted with rice crop twice a year with no additional fertilization. The temperature at the time of sampling was 14.8&#x00B0;C, and the rice seedlings were not transplanted after harvest. Paddy soil with 10&#x2009;cm below the water surface, was sampled in three parallels with a sterilized shovel. After removing stones and roots, soil was thoroughly mixed and quickly placed into a large self-sealing bag. The evenly mixed paddy soil was then transported to the laboratory while kept in ice and stored at &#x2212;20&#x00B0;C before microcosm incubations. pH of this soil was 6.59, which was determined using PHS-3E (Leici, China) according to the method described before (<xref ref-type="bibr" rid="ref48">Zhou et al., 2016</xref>). The measurement of total organic carbon (TOC) and iron(II) is based on colorimetric assay (<xref ref-type="bibr" rid="ref48">Zhou et al., 2016</xref>). The total organic carbon and iron in the soil were 30.10&#x2009;mg/kg and 59.07&#x2009;g&#x2009;kg<sup>&#x2212;1</sup>, respectively.</p>
</sec>
<sec id="sec4">
<label>2.2</label>
<title>Microcosm incubations</title>
<p>The operation of microcosm incubations was described earlier (<xref ref-type="bibr" rid="ref48">Zhou et al., 2016</xref>). In brief, the slurry was prepared by mixing paddy soil and sterilized ultrapure water (w: v&#x2009;=&#x2009;1: 5) in the 2&#x2009;L beaker in an ultraclean bench. After homogenization, the slurry was exposed to N<sub>2</sub>/CO<sub>2</sub> (v/v&#x2009;=&#x2009;80/20) for 1&#x2009;h, and aliquots (40&#x2009;mL) of the soil slurry were transferred into 50&#x2009;mL serum bottles. The headspace of the medium was flushed with N<sub>2</sub>/CO<sub>2</sub> for 20&#x2009;min and then vials were capped with butyl stoppers and aluminum seal. Pre-incubation of the slurry was performed at 30&#x00B0;C in the dark for 96&#x2009;h, aiming to consume the soluble organic matter including sugars and short-chain organic acids originally present in the paddy soil. In order to investigate the role of fungi in iron(III) reduction in the paddy soil, a total of eight ferrihydrite-added treatments (<italic>n</italic>&#x2009;=&#x2009;3, each) were established using various organic matters as electron donors: (1) the slurry was amended with 4&#x2009;g/L carboxymethylcellulose (termed as cellulose); (2) the slurry was amended with 4&#x2009;g/L carboxymethylcellulose and antibiotics containing 50&#x2009;mg/L streptomycin and 50&#x2009;mg/L vancomycin (cellulose + antibiotics); (3) the slurry was amended with 1&#x2009;mM glucose (glucose); (4) slurry was amended with 1&#x2009;mM glucose and antibiotics containing 50&#x2009;mg/L streptomycin and 50&#x2009;mg/L vancomycin (glucose + antibiotics); (5) the slurry was amended with 2&#x2009;mM sodium lactate (lactate); (6) the slurry was amended with 2&#x2009;mM sodium lactate and antibiotics containing 50&#x2009;mg/L streptomycin and 50&#x2009;mg/L vancomycin (lactate + antibiotics); (7) 3&#x2009;mM sodium acetate (acetate); (8) the slurry was amended with 3&#x2009;mM sodium acetate and antibiotics containing 50&#x2009;mg/L streptomycin and 50&#x2009;mg/L vancomycin (acetate + antibiotics). Ferrihydrite was prepared by adding KOH solution to Fe(NO<sub>3</sub>)<sub>3</sub>&#x00B7;9H<sub>2</sub>O solution and then making a pH adjustment to 6.8&#x2013;7.2 according to the previous description (<xref ref-type="bibr" rid="ref48">Zhou et al., 2016</xref>).</p>
</sec>
<sec id="sec5">
<label>2.3</label>
<title>Dynamic sampling and chemical analyses</title>
<p>The serum bottles were dynamically sampled on days 0, 9, 18, and 25 during incubation with sterile syringes in an ultra-clean bench. Then, 40&#x2009;mM sulfamic acid was used for iron(II) extraction, and total Fe was extracted with sulfamic acid (80&#x2009;mM) and hydroxylamine hydrochloride (80&#x2009;mM) (v:v&#x2009;=&#x2009;1:1) (<xref ref-type="bibr" rid="ref48">Zhou et al., 2016</xref>). After centrifugation of remaining culture suspensions at 10,000&#x2009;g for 10&#x2009;min, sediments were used for DNA extraction based on the kit manufacturer&#x2019;s instructions (MP Biochemicals; Solon, OH, United States), while supernatants were used to measure glucose according to the anthrone method (<xref ref-type="bibr" rid="ref42">Updegraff, 1969</xref>) and organic acids including acetate, lactate and pyruvate using ion chromatograph (Dionex ICS-1500 system; Diones, Sunnyvales, CA).</p>
</sec>
<sec id="sec6">
<label>2.4</label>
<title>High-throughput sequencing and data analysis</title>
<p>Fungal amplification of the ITS2 region was performed using primers Gis7 (GTGARTCATCGARTCTTTG) and ITS4 (TCCTCCGCTTATTGATATGC) (<xref ref-type="bibr" rid="ref10">Geng et al., 2022</xref>). PCR conditions were pre-denaturated at 94&#x00B0;C for 3&#x2009;min, then 35&#x2009;cycles were performed at 94&#x00B0;C for 30&#x2009;s, 58.3&#x00B0;C for 30&#x2009;s, and 72&#x00B0;C for 45&#x2009;s, and finally extended at 72&#x00B0;C for 10&#x2009;min. The PCR products were then purified, quantified, pooled, and sequenced on an Illumina Miseq PE 250 Platform (Novogene, Beijing, China). Sequencing data were analyzed using QIIME2 (version 2021.11) following the online instructions (<xref ref-type="bibr" rid="ref4">Bolyen et al., 2019</xref>). Deblur algorithm was used to determine amplicon sequence variants (ASVs) for the sequencing data by denoising in the QIIME2 platform, and UNITE v2020.2 reference databases were used to annotate fungal taxonomy (<xref ref-type="bibr" rid="ref4">Bolyen et al., 2019</xref>). R software loaded with EdgeR package was utilized for statistical analyses, and fungal species with a significant increase (<italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) in abundance between days were denoted as active taxa during the incubation. The ITS2 gene sequences have been deposited in the NCBI database with accession number PRJNA887227.</p>
<p><italic>16S rRNA</italic> gene of bacteria on day 9 during incubations was quantified by fluorogenic quantitative PCR (qPCR), and the condition and primer has been described before (<xref ref-type="bibr" rid="ref48">Zhou et al., 2016</xref>). In detail, The V4-V5 region of the <italic>16S rRNA</italic> gene was amplified using primers 515F (GTGCCAGCMGCCGCGG) and 907R (CCGTCAATTCMTTTRAGTTT). qPCR conditions were predenaturated at 94&#x00B0;C for 3&#x2009;min, then 35&#x2009;cycles were performed at 94&#x00B0;C for 30&#x2009;s, 55&#x00B0;C for 30&#x2009;s, and 72&#x00B0;C for 45&#x2009;s, and finally extended at 72&#x00B0;C for 10&#x2009;min.</p>
</sec>
<sec id="sec7">
<label>2.5</label>
<title>Metagenomic assembly, genome binning, gene annotation and its gene alignment</title>
<p>A total of 46 assembled fungal MAGs (<xref ref-type="supplementary-material" rid="SM1">Supplementary Table S1</xref>), which are phylogenetically close to the active fungal taxa identified during incubation, were retrieved from the NCBI database (<xref ref-type="supplementary-material" rid="SM1">Supplementary Tables S2&#x2013;S4</xref>). The MAGs were sequenced using several methods, including Illumina HiSeq, Illumina MiSeq, PacBio, and Nanopore, and the information about the sequencing method, assembly method, and the relevant references are detailed in <xref ref-type="supplementary-material" rid="SM1">Supplementary Table S1</xref>. Protein-coding regions were predicted using Prodigal (version 2.6.3) with the &#x201C;-p meta&#x201D; option (<xref ref-type="bibr" rid="ref14">Hyatt et al., 2010</xref>). The eggNOG-mapper (<xref ref-type="bibr" rid="ref13">Huerta-Cepas et al., 2017</xref>), KEGG server (BlastKOALA) (<xref ref-type="bibr" rid="ref16">Kanehisa et al., 2016</xref>), InterProScan tool (5.44&#x2013;79.0) (<xref ref-type="bibr" rid="ref15">Jones et al., 2014</xref>), and Diamond (0.9.22)-connected NCBI-nr database searched in May 2022 (<italic>E</italic>-value cutoff &#x2264;1e-5) were employed to annotate the protein-coding regions.</p>
<p>Fungal ITS2 gene sequences, including ITS2 gene from Illumina sequencing and extracted from fungal MAGs obtained from NCBI database, were aligned using NCBI BLAST.<xref ref-type="fn" rid="fn0001">
<sup>1</sup>
</xref> Ribosomal ITS2 genes in fungal MAGs were extracted by ITSx (version 1.1.3<xref ref-type="fn" rid="fn0002">
<sup>2</sup>
</xref>).</p>
</sec>
</sec>
<sec sec-type="results" id="sec8">
<label>3</label>
<title>Results</title>
<sec id="sec9">
<label>3.1</label>
<title>Iron(III) reduction in treatments with or without antibiotics</title>
<p>For almost all the groups, it displayed rapid iron(III) reduction in the first 9&#x2009;days during incubation (<xref ref-type="fig" rid="fig1">Figures 1A</xref>&#x2013;<xref ref-type="fig" rid="fig1">D</xref>). The rates of iron(III) reduction were around 0.46&#x2013;0.49&#x2009;mmol&#x2009;L<sup>&#x2212;1</sup> day<sup>&#x2212;1</sup> in no-antibiotics treatments with glucose, lactate, and acetate during 9-days incubation (<xref ref-type="fig" rid="fig1">Figures 1B</xref>&#x2013;<xref ref-type="fig" rid="fig1">D</xref>), which were significantly (<italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) higher than those in cellulose treatments without antibiotics (<xref ref-type="fig" rid="fig1">Figure 1A</xref>). The addition of antibiotics markedly decreased iron(III)-reducing rates in cellulose treatments during incubations (<xref ref-type="fig" rid="fig1">Figure 1A</xref>). Whereas, no significant difference in rates of iron(III) reduction was found between other setups (glucose, lactate, and acetate) with and without antibiotic addition (<xref ref-type="fig" rid="fig1">Figures 1B</xref>&#x2013;<xref ref-type="fig" rid="fig1">D</xref>).</p>
<fig position="float" id="fig1">
<label>Figure 1</label>
<caption>
<p>Dynamics of Fe(II) concentrations in treatments amended with cellulose <bold>(A)</bold>, glucose <bold>(B)</bold>, lactate <bold>(C)</bold>, and acetate <bold>(D)</bold> during days of incubation with or without antibiotics. Error bars represent standard deviations of three replications.</p>
</caption>
<graphic xlink:href="fmicb-14-1334051-g001.tif"/>
</fig>
</sec>
<sec id="sec10">
<label>3.2</label>
<title>Decomposition of organic matters in treatments with or without antibiotics</title>
<p>Cellulose degradation was accompanied by the generation of intermediates, including glucose, lactate, pyruvate, and acetate (<xref ref-type="fig" rid="fig2">Figures 2A</xref>&#x2013;<xref ref-type="fig" rid="fig2">D</xref>). Notably, there were fluctuations in the concentrations of glucose and acetate, reaching peak levels of 0.33 and 3.38&#x2009;mmol&#x2009;L<sup>&#x2212;1</sup> on day 18, respectively. Conversely, the concentrations of pyruvate and lactate showed no significant changes in cellulose treatments without antibiotics during the 25-day incubation period (<xref ref-type="fig" rid="fig2">Figures 2A</xref>&#x2013;<xref ref-type="fig" rid="fig2">D</xref>). In contrast, in setups with antibiotics added to cellulose, there was a conspicuous accumulation of pyruvate and lactate (<xref ref-type="fig" rid="fig2">Figures 2B</xref>,<xref ref-type="fig" rid="fig2">C</xref>). However, lower concentrations of acetate and glucose accumulated in cellulose amendments with antibiotics than those without antibiotics (<xref ref-type="fig" rid="fig2">Figures 2A</xref>,<xref ref-type="fig" rid="fig2">D</xref>).</p>
<fig position="float" id="fig2">
<label>Figure 2</label>
<caption>
<p>Time course of metabolite concentrations in treatments amended with cellulose <bold>(A&#x2013;D)</bold>, glucose <bold>(E&#x2013;H)</bold>, lactate <bold>(I&#x2013;K)</bold>, and acetate <bold>(A)</bold> during days of incubation with or without antibiotics. Error bars represent standard deviations of three replications.</p>
</caption>
<graphic xlink:href="fmicb-14-1334051-g002.tif"/>
</fig>
<p>Generation of lactate, pyruvate, and acetate was detected in glucose-amended groups during 25-day incubation (<xref ref-type="fig" rid="fig2">Figures 2E</xref>&#x2013;<xref ref-type="fig" rid="fig2">H</xref>). Glucose was exhausted on day 9 during the incubation, and there was no apparent distinction in rates and extents of glucose degradation between treatments with antibiotics and without antibiotics (<xref ref-type="fig" rid="fig2">Figure 2H</xref>). Additionally, the intermediates including lactate, pyruvate, and acetate evidently increased in glucose-adding groups with antibiotics, whereas acetate rapidly accumulated at the beginning of the incubation and then sharply depleted on day 9 in glucose treatments amended without antibiotics (<xref ref-type="fig" rid="fig2">Figures 2E</xref>&#x2013;<xref ref-type="fig" rid="fig2">G</xref>).</p>
<p>Similarly, the addition of antibiotics had no significant effect on the rate of lactate degradation (<xref ref-type="fig" rid="fig2">Figure 2K</xref>). Moreover, it was found higher amounts of pyruvate were generated in the antibiotic-present setups than in the antibiotic-absent ones, nevertheless, which exhibited an opposite trend to the acetate accumulation for these two treatments with lactate during 25-day incubation (<xref ref-type="fig" rid="fig2">Figures 2I</xref>,<xref ref-type="fig" rid="fig2">J</xref>).</p>
<p>With regard to treatments with acetate, additional antibiotics substantially inhibited its degradation rates during incubation (<xref ref-type="fig" rid="fig2">Figure 2L</xref>).</p>
</sec>
<sec id="sec11">
<label>3.3</label>
<title>Active fungal taxa in treatments with organic matters amended with and without antibiotics</title>
<p>The family Trichocomaceae was found with the highest relative abundances in all treatments with and without antibiotics (<xref ref-type="fig" rid="fig3">Figure 3</xref>), which shared 7 other families containing Pseudeurotiaceae, unclassified Hypocreales, Nectriaceae, Chaetomiaceae, Aspergillaceae, Sporormiaceae, Chaetomiaceae, and Hyaloscyphaceae enriched during the incubation with and without antibiotics (<xref ref-type="fig" rid="fig3">Figure 3</xref>). Comparably, there was no enrichment of Lasiosphaeriaceae and Coniochaetaceae in antibiotic-present/absent setups with glucose and lactate, respectively (<xref ref-type="fig" rid="fig3">Figure 3</xref>). In addition, the family Sordariaceae was specifically detected in treatments with glucose and lactate under conditions with and without antibiotics (<xref ref-type="fig" rid="fig3">Figure 3</xref>).</p>
<fig position="float" id="fig3">
<label>Figure 3</label>
<caption>
<p>Pattern of fungal community of top 10 taxa at the family level in treatments amended with cellulose <bold>(A)</bold>, glucose <bold>(B)</bold>, lactate <bold>(C)</bold>, and acetate <bold>(D)</bold> during days of incubation with or without antibiotics.</p>
</caption>
<graphic xlink:href="fmicb-14-1334051-g003.tif"/>
</fig>
<p>Active fungal taxa in this study referred to the genera of fungal whose abundances significantly increased (<italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) during incubations with cellulose, glucose, lactate, and acetate. A total of 10, 6, 14, and 10 active genera were detected during incubation with cellulose, glucose, lactate, and acetate under no addition of antibiotics, respectively (<xref ref-type="fig" rid="fig4">Figure 4</xref>). Moreover, all active genera found in organic matter degradation were members belonging to the top 10 most abundant families (<xref ref-type="fig" rid="fig3">Figures 3</xref>, <xref ref-type="fig" rid="fig4">4</xref>). The relative abundances of 7 genera including unidentified Coinochaetaceae, <italic>Podospora</italic>, <italic>Schizothecium</italic>, <italic>Paracremonium</italic>, <italic>Alternaria</italic>, <italic>Coprinopsis</italic>, <italic>Hypholoma</italic>, and unidentified <italic>Agricales</italic> increased, especially, in the first 9 or 18&#x2009;days, whereas, it was observed with a downward tendency in relative abundances of unidentified Pyrenochaetopsis and unidentified Sordariales during the incubation with cellulose (<xref ref-type="fig" rid="fig4">Figure 4</xref>). There were 5 (containing <italic>Coprinus</italic>, unidentified Coinochaetaceae, <italic>Fusarium</italic>, <italic>Hypholoma,</italic> and unidentified Leucosporidiales) and 1 (<italic>Mycosphaerella</italic>) genera with increase and decrease in relative abundances in no antibiotic-amended glucose treatments, respectively (<xref ref-type="fig" rid="fig4">Figure 4</xref>). In addition, the number of genera whose abundances increased with lactate and acetate addition were 7 and 6 during incubation for the first 9 or 18&#x2009;days of incubation, while the ones with decreasing abundances were more diverse in treatments with lactate (7 genera) and acetate (4 genera), respectively (<xref ref-type="fig" rid="fig4">Figure 4</xref>).</p>
<fig position="float" id="fig4">
<label>Figure 4</label>
<caption>
<p>Heatmap of relative abundances of fungal taxa with significant difference (<italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) in the genus level detected in treatments amended with cellulose, glucose, lactate and acetate during days of incubation without antibiotics. &#x2606;represented abundances of taxa increased during the incubation, which were denote as active taxa in this study.</p>
</caption>
<graphic xlink:href="fmicb-14-1334051-g004.tif"/>
</fig>
</sec>
<sec id="sec12">
<label>3.4</label>
<title>Physiological capability of active fungal taxa revealed by metagenome analysis</title>
<p>To comprehensively elucidate the metabolic capabilities of active fungal taxa, 46 fungal MAGs were selected based on the sequence alignment between the ITS2 gene extracted from MAGs and relevant ASV sequences detected in this study (<xref ref-type="supplementary-material" rid="SM1">Supplementary Tables S1&#x2013;S3</xref>), and most of the identity values were higher than 95% (<xref ref-type="supplementary-material" rid="SM1">Supplementary Table S4</xref>). Metagenomic inference revealed that all of these active fungi harbor genes encoding complete pathways for cellulose degradation, leading to the production of glucose (<xref ref-type="fig" rid="fig5">Figure 5</xref>; <xref ref-type="supplementary-material" rid="SM1">Supplementary Tables S5&#x2013;S8</xref>). Moreover, all of these MAGs possess genes encoding enzymes responding to glucose fermentation, lactate and acetate utilization, Krebs cycle, energy metabolism, and electron transfer (<xref ref-type="fig" rid="fig5">Figure 5</xref>; <xref ref-type="supplementary-material" rid="SM1">Supplementary Tables S5&#x2013;S8</xref>). However, MAGs excluding genera <italic>Gaeumannomyces</italic> and <italic>Leucosporidium</italic> lack genes catabolizing glucose to produce glucose-6p (<xref ref-type="fig" rid="fig5">Figure 5</xref>; <xref ref-type="supplementary-material" rid="SM1">Supplementary Figure S1</xref>; <xref ref-type="supplementary-material" rid="SM1">Supplementary Tables S5&#x2013;S8</xref>). In addition, genes involved in transporting glucose and acetate are identified in all the MAGs, nevertheless, being absent of genes driving lactate uptake for genera such as <italic>Coprinus</italic>, <italic>Cladosporium</italic>, <italic>Chaetomium</italic>, <italic>Meyerozyma</italic>, etc. (<xref ref-type="fig" rid="fig5">Figure 5</xref>; <xref ref-type="supplementary-material" rid="SM1">Supplementary Tables S5&#x2013;S8</xref>).</p>
<fig position="float" id="fig5">
<label>Figure 5</label>
<caption>
<p>Metabolic pathway of cellulose, glucose, lactate and acetate in active fungal taxa. <bold>(A)</bold> Gene homologs in active fungal MAGs. <bold>(B)</bold> Proposed active pathway in fungal taxa. Pathways were constructed based on fungal MAGs (<xref ref-type="supplementary-material" rid="SM1">Supplementary Table S1</xref>). &#x2606;indicates that ITS2 sequences were not extracted from the fungal MAGs. <bold>(C)</bold> Iron(III)-reducing potential fungi including fermentative and four organic matters metabolism with the reduction of Fe(III) to Fe(II) in cellulose, glucose, lactate and acetate amended setups. The gray arrows represented that cellulose, glucose, lactate and acetate degraded into CO<sub>2</sub> by fungal members and the orange arrows showed the products of glucose, lactate and acetate in the process of cellulose decomposition.</p>
</caption>
<graphic xlink:href="fmicb-14-1334051-g005.tif"/>
</fig>
</sec>
</sec>
<sec sec-type="discussion" id="sec13">
<label>4</label>
<title>Discussion</title>
<sec id="sec14">
<label>4.1</label>
<title>Activity of fungi to reduce iron(III) in a paddy soil</title>
<p>Paddy soil contains a rich supply of organic matter, including cellulose, glucose, lactate, and acetate (<xref ref-type="bibr" rid="ref26">Lovley and Phillips, 1986</xref>). Additionally, the bacterial community plays a crucial role in the process of iron reduction in paddy soils (<xref ref-type="bibr" rid="ref44">Weber et al., 2006</xref>; <xref ref-type="bibr" rid="ref17">Kappler et al., 2021</xref>). The abundances of bacterial <italic>16S rRNA</italic> genes in the treatments with antibiotics were significantly (<italic>p</italic>&#x2009;&#x003C;&#x2009;0.0001) decreased compared to incubation without antibiotics (<xref ref-type="supplementary-material" rid="SM1">Supplementary Figure S3</xref>). However, treatments with organics were still detected with the exhaustion of iron(III) within 9&#x2009;days after antibiotic addition (<xref ref-type="fig" rid="fig1">Figure 1</xref>) suggesting the strong capability of iron(III) reduction by fungal communities in treatments with cellulose, glucose, lactate, and acetate.</p>
<p>During the ferrihydrite reduction, cellulose decomposition occurred with the production of glucose, pyruvate, lactate, and acetate in treatments with and without antibiotics (<xref ref-type="fig" rid="fig2">Figures 2A</xref>,<xref ref-type="fig" rid="fig2">D</xref>), unveiling the existence of cellulolytic fungi during the incubation. Cellulose hydrolysis, which may be followed by forming cellobiose as intermediates, can be catalyzed by 1,4-beta-D-glucan cellobiohydrolase, 1, 4-beta cellobiohydrolase and beta-glucosidase to produce glucose (<xref ref-type="bibr" rid="ref21">Leschine, 1995</xref>). Since this process contains no redox reactions, there would be no transfer of electrons for iron(III) reduction. By contrast, the oxidation of glucose and lactate can supply prolific electron donors for dissimilatory iron(III) reducers (<xref ref-type="bibr" rid="ref44">Weber et al., 2006</xref>; <xref ref-type="bibr" rid="ref17">Kappler et al., 2021</xref>). Throughout the incubation with antibiotics, the fluctuations in concentrations of glucose, pyruvate, and lactate (<xref ref-type="fig" rid="fig2">Figures 2E</xref>&#x2013;<xref ref-type="fig" rid="fig2">K</xref>) indicated fermentative iron(III)-reducing fungal community were active to employ cellulose, glucose, and acetate as electron donors. In addition, the strong ability of respiratory iron(III) reduction by fungal members was revealed by the rapid decrease in acetate and iron(III) (<xref ref-type="fig" rid="fig1">Figures 1</xref>, <xref ref-type="fig" rid="fig2">2I</xref>) during the acetate-added groups under conditions with or without antibiotics (<xref ref-type="bibr" rid="ref25">Lovley, 2006</xref>).</p>
</sec>
<sec id="sec15">
<label>4.2</label>
<title>The diversity of fermentative iron(III)-reducing fungi in a paddy soil</title>
<p>Iron-reducing organisms were divided into two categories, respiratory and fermentative iron reducers. Fermentative iron fungi concurrently consume fermentative organic substrates (e.g., glucose or pyruvate) to produce Fe(II) and acquire a small amount of energy from iron reduction to support growth (<xref ref-type="bibr" rid="ref9">Dong et al., 2017</xref>). The potential fermentative iron(III)-reducing fungal members constituted five active genera for glucose oxidation, including <italic>Coprinus</italic>, unidentified Coniochaetaceae, <italic>Fusarium</italic>, <italic>Hypholoma</italic>, and unidentified Leucosporidiales, and 7 active genera for lactate utilization, e.g., <italic>Coprinus</italic>, <italic>Chaetomium</italic>, <italic>Stemphylium</italic>, <italic>Hypholoma</italic>, <italic>Nigrospora</italic>, etc. For glucose metabolization, unidentified Leucosporidiales (<xref ref-type="fig" rid="fig4">Figures 4</xref>, <xref ref-type="fig" rid="fig5">5A,C</xref>), which can refer to the phylogenetically related Leucosporidium, may take the responsibility to catabolize glucose with generating glucose-6-phosphate and other active taxa may jointly complete glycolysis (<xref ref-type="fig" rid="fig4">Figures 4</xref>, <xref ref-type="fig" rid="fig5">5A</xref>). MAGs of all the active genera encode enzymes linked to lactate catabolism and the Krebs cycle, and <italic>Coniochaeta</italic>&#x2019;s genome is equipped with a lactate transporter-relevant gene (<xref ref-type="fig" rid="fig5">Figure 5</xref>), which further supports their ability to utilize lactate during incubation. As a result, a total of 10 genera were considered as possible fermentative iron(III)-reducing fungal communities.</p>
</sec>
<sec id="sec16">
<label>4.3</label>
<title>The diversity of respiratory iron(III)-reducing fungi in a paddy soil</title>
<p>Conversely, respiratory iron(III)-reducing fungi metabolize non-fermentative substances (eg. acetate) to reduce ferrihydrite. Moreover, as a non-fermentative substrate is used as an electron donor only, the electron transfer strategy determines the occurrence of dissimilatory iron reduction (<xref ref-type="bibr" rid="ref32">Nealson and Saffarini, 1994</xref>). There were 7 genera (<italic>Aspergillus</italic>, <italic>Penicillium</italic>, <italic>Cistella</italic>, <italic>Schizothecium</italic>, <italic>Gaeumannomyces</italic>, <italic>Alternaria</italic>, and <italic>Hypholoma</italic>) affiliated to 6 families, actively taking up acetate during ferrihydrite reduction (<xref ref-type="fig" rid="fig4">Figures 4</xref>, <xref ref-type="fig" rid="fig5">5A,C</xref>), were though as potential respiratory iron(III)-reducing fungal microorganisms attribute to the non-fermentable property of acetate. Moreover, the complete metabolic pathway of acetate equipped by most active taxa-relevant MAGs (<xref ref-type="fig" rid="fig5">Figures 5A</xref>,<xref ref-type="fig" rid="fig5">B</xref>) is consistent with this conclusion. Up to date, the diversity of fungal species associated with iron(III) reduction was limitedly documented except for members belonging to the genus <italic>Fusarium</italic>, <italic>Alternaria</italic>, and <italic>Aspergillus</italic> (<xref ref-type="bibr" rid="ref36">Ottow and von Klopotek, 1969</xref>). Both <italic>Fusarium</italic> and <italic>Alternaria</italic> show activity to reduce hematite through using glucose as the substrate (<xref ref-type="bibr" rid="ref36">Ottow and von Klopotek, 1969</xref>). Our results align with the former, while the latter specifically utilized acetate during incubation in our study (<xref ref-type="fig" rid="fig4">Figure 4</xref>). The species <italic>Aspergillus niger</italic> has been reported to bioleach iron from a clay mineral under acidic conditions with pH ranging from 1.7 to 3 (<xref ref-type="bibr" rid="ref12">Hosseini et al., 2007</xref>). Besides, Lalinsk&#x00E1;-Volekov&#x00E1; et al. have reported that <italic>Coprinus</italic> is abundant in environments rich in hydrous ferric oxides (<xref ref-type="bibr" rid="ref20">Lalinska-Volekova et al., 2022</xref>). Similarly, <italic>Stemphylium botryosum</italic> (belongs to the genera <italic>Stemphylium</italic>) showed a high capacity to use citrate to reduce external ferric iron (<xref ref-type="bibr" rid="ref29">Manulis et al., 1987</xref>). <italic>Penicillium</italic> sp. is capable of leaching Fe<sup>3+</sup> from jarosite minerals and reducing Fe<sup>3+</sup> to Fe<sup>2+</sup> (<xref ref-type="bibr" rid="ref33">Oggerin et al., 2014</xref>). The functional genes involved in iron(III) reduction were not identified yet, leading to difficulty in the identification and confirmation of functional iron(III)-reducing fungal candidates. However, the relevant MAGs of these potential fermentative iron(III)-reducing fungi harbored genes encoding nitrate reductase, hinting at their possible role in nitrate reduction under anaerobic conditions. Most iron-reducing microorganisms (facultative anaerobic bacteria, fungi, and yeasts) are simultaneously nitrate-reductase inducible (<xref ref-type="bibr" rid="ref34">Ottow, 1969</xref>; <xref ref-type="bibr" rid="ref36">Ottow and von Klopotek, 1969</xref>; <xref ref-type="bibr" rid="ref35">Ottow and Glathe, 1971</xref>).</p>
</sec>
<sec id="sec17">
<label>4.4</label>
<title>Contribution of potential iron(III)-reducing fungi to cellulose degradation</title>
<p>Most of the active fungal members such as Coniochaetaceae, Lasiosphaeriaceae, Nectriaceae, and Pleosporaceae belonged to the phylum <italic>Ascomycota</italic> (<xref ref-type="fig" rid="fig4">Figure 4</xref>), which has been reported as saprophytic fungi (<xref ref-type="bibr" rid="ref45">Weber et al., 2011</xref>; <xref ref-type="bibr" rid="ref38">Qin et al., 2014</xref>). Specifically, the relevant MAGs of these active fungal taxa, including unidentified Coniochaetaceae, <italic>Podospora</italic>, <italic>Schizothecium</italic>, <italic>Paracremonium</italic>, <italic>Alternaria</italic>, <italic>Coprinopsis</italic> and unidentified Agaricales, encode enzymes including 1,4-beta-D-glucan cellobiohydrolase, 1, 4-beta cellobiohydrolase, glucan 1,3-beta-glucosidase, glycoside hydrolase and beta-glucosidase to participate in breaking bond of cellulose with yielding glucose (<xref ref-type="fig" rid="fig5">Figures 5A</xref>&#x2013;<xref ref-type="fig" rid="fig5">C</xref>; <xref ref-type="supplementary-material" rid="SM1">Supplementary Tables S5&#x2013;S8</xref>). This enzymatic profile aligned well with the observed glucose production during cellulose incubation (<xref ref-type="fig" rid="fig2">Figure 2D</xref>). Moreover, these 7 active fungal taxa are capable of hydrolyzing cellulose in anaerobic or aerobic environments such as damp chamber cultures, plant biomass, wheat straw-amended soil, mangrove and cattle rumen (<xref ref-type="bibr" rid="ref7">Croan, 2000</xref>; <xref ref-type="bibr" rid="ref22">Liu et al., 2010</xref>; <xref ref-type="bibr" rid="ref40">&#x0160;najdr et al., 2010</xref>; <xref ref-type="bibr" rid="ref8">Deep et al., 2014</xref>; <xref ref-type="bibr" rid="ref37">Poidevin et al., 2014</xref>; <xref ref-type="bibr" rid="ref5">Carrillo et al., 2016</xref>; <xref ref-type="bibr" rid="ref43">Velasco-Rodr&#x00ED;guez et al., 2022</xref>). Intermediates of cellulose containing glucose, lactate, pyruvate, and acetate were identified in the cellulose incubation with antibiotics amendments (<xref ref-type="fig" rid="fig2">Figures 2A</xref>&#x2013;<xref ref-type="fig" rid="fig2">D</xref>), reflecting the fungal activity in further breaking down cellulose. With the oxidation of glucose, lactate, pyruvate, and acetate, the active members in cellulose treatments containing unidentified Coniochaetaceae, <italic>Schizothecium,</italic> and <italic>Alternaria</italic> probably (<xref ref-type="fig" rid="fig2">Figures 2</xref>, <xref ref-type="fig" rid="fig4">4</xref>) were likely to accept the released electrons to reduce ferrihydrite, which offers a plausible explanation for their increased abundances during the incubation.</p>
</sec>
</sec>
<sec sec-type="conclusions" id="sec18">
<label>5</label>
<title>Conclusion</title>
<p>In summary, the introduction of antibiotics had a pronounced effect on the iron(III) reduction rate within cellulose-amended groups, markedly slowing down the process, while exhibiting negligible impact on the other groups. Furthermore, metabolic rates of organic substrates and intermediates significantly altered with antibiotics amendment during incubation. Besides, there were several active genera for the metabolism of cellulose (e.g., <italic>Podospora</italic>, <italic>Schizothecium</italic>, <italic>Paracremonium</italic>, <italic>Alternaria</italic>, <italic>Coprinopsis</italic>), glucose (e.g., <italic>Coprinus</italic>, <italic>Fusarium</italic>, <italic>Hypholoma</italic>), lactate (e.g., <italic>Coprinus</italic>, <italic>Chaetomium</italic>, <italic>Stemphylium</italic>) and acetate (e.g., <italic>Aspergillus</italic>, <italic>Penicillium</italic>, <italic>Cistella</italic>), whose genomes possess complete metabolic pathways for degradation of the typical organic matters. Furthermore, the investigation revealed the presence of 20 genera (e.g., <italic>Fusarium</italic>, <italic>Alternaria</italic>) with the potential for respiratory and fermentative iron(III) reduction particularly in experimental setups amended with four distinct organic substances. In conclusion, it was proven that the potential and diversity of iron(III)-reducing fungi, clarified the underestimated function of fungi in directly driving the carbon and iron biogeochemical cycling, and provided a new perspective for further understanding of carbon and iron cycling in environments.</p>
</sec>
<sec sec-type="data-availability" id="sec19">
<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 in the article/<xref ref-type="supplementary-material" rid="SM1">Supplementary material</xref>.</p>
</sec>
<sec sec-type="author-contributions" id="sec20">
<title>Author contributions</title>
<p>M-JL: Data curation, Formal analysis, Investigation, Methodology, Visualization, Writing &#x2013; original draft. X-XY: Conceptualization, Investigation, Methodology, Supervision, Visualization, Writing &#x2013; review &#x0026; editing. Y-MD: Investigation, Methodology, Software, Visualization, Writing &#x2013; review &#x0026; editing. Q-YS: Conceptualization, Formal analysis, Methodology, Supervision, Writing &#x2013; review &#x0026; editing. G-WZ: Conceptualization, Funding acquisition, Methodology, Project administration, Supervision, Writing &#x2013; review &#x0026; editing.</p>
</sec>
</body>
<back>
<sec sec-type="funding-information" id="sec21">
<title>Funding</title>
<p>The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This research was supported by the National Natural Science Foundation of China (42107143), Science Foundation for Young Scholars of Anhui University and Collaborative Innovation Project of Anhui Universities (GXXT-2021-061), and Ecology Peak discipline program (Z010111022).</p>
</sec>
<sec sec-type="COI-statement" id="sec22">
<title>Conflict of interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="sec100" 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 sec-type="supplementary-material" id="sec23">
<title>Supplementary material</title>
<p>The Supplementary material for this article can be found online at: <ext-link xlink:href="https://www.frontiersin.org/articles/10.3389/fmicb.2023.1334051/full#supplementary-material" ext-link-type="uri">https://www.frontiersin.org/articles/10.3389/fmicb.2023.1334051/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Table_1.XLSX" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
<fn-group>
<fn id="fn0001"><p><sup>1</sup><ext-link xlink:href="https://blast.ncbi.nlm.nih.gov/Blast.cgi" ext-link-type="uri">https://blast.ncbi.nlm.nih.gov/Blast.cgi</ext-link></p></fn>
<fn id="fn0002"><p><sup>2</sup><ext-link xlink:href="https://microbiology.se/tag/itsx/" ext-link-type="uri">https://microbiology.se/tag/itsx/</ext-link></p></fn>
</fn-group>
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