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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Hortic.</journal-id>
<journal-title>Frontiers in Horticulture</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Hortic.</abbrev-journal-title>
<issn pub-type="epub">2813-3595</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fhort.2023.1061456</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Horticulture</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Diversity and abundance of bacterial and fungal communities in rhizospheric soil from smallholder banana producing agroecosystems in Kenya</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Wahome</surname>
<given-names>Caroline N.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/2104357"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Maingi</surname>
<given-names>John M.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/425128"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Ombori</surname>
<given-names>Omwoyo</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/399722"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Njeru</surname>
<given-names>Ezekiel Mugendi</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/304775"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Muthini</surname>
<given-names>Morris</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Kimiti</surname>
<given-names>Jacinta Malia</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/425374"/>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>Department of Biochemistry, Microbiology and Biotechnology, Kenyatta University</institution>, <addr-line>Nairobi</addr-line>, <country>Kenya</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Department of Plant Sciences, Kenyatta University</institution>, <addr-line>Nairobi</addr-line>, <country>Kenya</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>Department of Forestry and Land Resources Management, South Eastern Kenya University</institution>, <addr-line>Kitui</addr-line>, <country>Kenya</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Metin Turan, Yeditepe University, T&#xfc;rkiye</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Ees Ahmad, National Bureau of Agriculturally Important Microorganisms (ICAR), India; Hayssam M. Ali, King Saud University, Saudi Arabia</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: John M. Maingi, <email xlink:href="mailto:maingijohn@gmail.com">maingijohn@gmail.com</email>
</p>
</fn>
<fn fn-type="other" id="fn002">
<p>This article was submitted to Olericulture, a section of the journal Frontiers in Horticulture</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>08</day>
<month>02</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>2</volume>
<elocation-id>1061456</elocation-id>
<history>
<date date-type="received">
<day>04</day>
<month>10</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>18</day>
<month>01</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2023 Wahome, Maingi, Ombori, Njeru, Muthini and Kimiti</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Wahome, Maingi, Ombori, Njeru, Muthini and Kimiti</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>In agroecosystems, microbial communities play a crucial role in delivery of various ecosystem services. These microbial communities are affected by several factors such as soil physicochemical properties which contribute to the diversity of bacterial and fungal communities. In this study, we investigated the soil physicochemical parameters and the diversity and abundance of bacterial and fungal communities in rhizospheric soil collected from banana growing regions in Kisii, Nyamira and Embu Counties of Kenya. Rhizospheric soil samples from the three regions showed significant differences at (P= 0.01) with the lowest recorded pH being 4.43 in Embu County. Based on Next-generation sequencing results, there was a significant diversity and abundance of bacterial division Proteobacteria while the predominant fungal division was basidiomycota, Several genera in the fungal division such as <italic>Penicillium</italic> and <italic>Cladosporium</italic> as well as bacterial genera such as <italic>Acidobacterium</italic> and <italic>Pseudomonas</italic> sp. were those associated with soil. There were several plant pathogenic and beneficial bacteria and fungi. Based on redundancy analysis (RDA) the distribution of these microbes was affected negatively by soil parameters such as total organic carbon (TOC) and pH. In conclusion, Soil health and continuous mono-cropping systems play a significant role in the diversity and abundance of both beneficial and harmful soil microbes. Metagenomics approaches in studying microbial communities in agroecosystems is a revolutionary approach which will aid in the development of sustainable tools in agriculture that improve microbiome structures as well as overall productivity.</p>
</abstract>
<kwd-group>
<kwd>microbiome</kwd>
<kwd>metagenomics</kwd>
<kwd>banana rhizosphere</kwd>
<kwd>soil parameters</kwd>
<kwd>diversity</kwd>
</kwd-group>
<counts>
<fig-count count="7"/>
<table-count count="3"/>
<equation-count count="0"/>
<ref-count count="42"/>
<page-count count="10"/>
<word-count count="3550"/>
</counts>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<title>Introduction</title>    <p>Banana farming is a major economic activity in Kenya. However, the current production trends by the smallholder farmers who form 85% of the banana producers in Kenya do not meet the market demand (<xref ref-type="bibr" rid="B28">Okumu et&#xa0;al., 2011</xref>). This is because there are various factors directly affecting production such as soil health as well as pests and diseases (<xref ref-type="bibr" rid="B23">K&#xf6;berl et&#xa0;al., 2017</xref>).</p>    <p>There has been increasing interest in soil health, specifically microbial diversity in soil habitat. This is because soil microbial communities are considered as essential in improving soil health and quality. A wide range of microorganisms are essential in soil function since microbial communities are key contributors to sustainable agriculture. Microbes are known to act as mediators in many processes that are involved in agricultural production (<xref ref-type="bibr" rid="B24">Lupwayi et&#xa0;al., 1998</xref>; <xref ref-type="bibr" rid="B32">Rondon et&#xa0;al., 2000</xref> and <xref ref-type="bibr" rid="B20">Gupta et&#xa0;al., 2018</xref>).</p>
<p>It has been observed that farm practices such as conservation tillage and legume-based crop rotation supports soil microbial communities and may have direct positive effects on agricultural ecosystems (<xref ref-type="bibr" rid="B26">Nguyen et&#xa0;al., 2018</xref>). The culturing techniques of studying microorganisms are not efficient in their study since majority of the microbes are unculturable (<xref ref-type="bibr" rid="B17">Goel et&#xa0;al., 2018</xref>)). Advances in molecular application in determining microbial diversity in nature shows that there is a lot of information that was not previously accessible (<xref ref-type="bibr" rid="B20">Gupta et&#xa0;al., 2018</xref>). Therefore, understanding the factors that influence microbial communities can assist greatly in the innovation of new agricultural tools for sustainable environment (<xref ref-type="bibr" rid="B20">Gupta et&#xa0;al., 2018</xref>).</p>
<p>There are numerous soil borne diseases that act as limiting factors in banana production all over the world (<xref ref-type="bibr" rid="B23">K&#xf6;berl et&#xa0;al., 2017</xref>). Most farmers use conventional methods in their control that mainly target pathogens using antibacterial agents, pesticides and fungicides and this has the potential of reducing the soil microbial community (<xref ref-type="bibr" rid="B9">Dita et&#xa0;al., 2018</xref>). Therefore, studying microbial communities can aid in creating tools to mitigate problems affecting essential microbial communities (<xref ref-type="bibr" rid="B6">Chaparro et&#xa0;al., 2012</xref>).</p>
<p>Recent reports indicate that stressors that affect soil biodiversity such as human activities, the decline in soil organic matter and degradation of land has led to the loss of aboveground and below ground biodiversity (<xref ref-type="bibr" rid="B29">Orgiazzi et&#xa0;al., 2016</xref>). The decline in soil health and fertility including biological degradation (organic matter) is a worrying trend and has the potential to lower productivity significantly. Constant monitoring of soil health status is an essential factor in processes of development of land management systems that ensure the sustainability of soil resources (<xref ref-type="bibr" rid="B40">Tilhou et&#xa0;al., 2021</xref>). In order to reclaim the damage to soil and ensure global agricultural sustainability, the identification of these stressors as well as development of sustainable methods such as bioremediation is important (<xref ref-type="bibr" rid="B38">Tahat et&#xa0;al., 2020</xref>).</p>
<p>The soil microbial communities in agroecosystems play a crucial role in plant growth and health. Recent studies have been focusing on microbial communities in continuous cropping systems and their roles. Understanding their roles as well as environmental factors that affect the communities is important in improving banana production (<xref ref-type="bibr" rid="B4">Berg et&#xa0;al., 2017</xref> and <xref ref-type="bibr" rid="B18">G&#xf3;mez-Lama et&#xa0;al., 2021</xref>). Studying soil microbial diversity in relation to other soil physicochemical parameters is essential. This aids greatly in identifying factors affecting beneficial microbial communities, thus highlighting the need for adoption and development of tools for sustainable agricultural practices (<xref ref-type="bibr" rid="B18">G&#xf3;mez-Lama et&#xa0;al., 2021</xref>). The current study was aimed at determining microbial diversity and abundance in banana rhizospheric soil from banana producing regions in Kenya and the influence of soil physicochemical parameters on the distribution of fungal and bacterial communities.</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<title>Materials and methods</title>
<sec id="s2_1">
<title>Soil sampling and characterization</title>
<p>Rhizospheric soils samples were collected from the farmers&#x2019; fields in Kisii, Nyamira and Embu Counties at a depth of 15-20&#xa0;cm using a sterile hand shovel. The GPS coordinates were used to create a map where soil sampling was carried out (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>). Soil sampling was carried out across and diagonally from 20 points per field and were mixed to form a composite sample which was packed in sterile bags for transportation to Kenyatta University, Tissue Culture Laboratory and stored in a freezer at -30 &#xb0;C. Soil physicochemical parameters were determined according to the standard procedures described by <xref ref-type="bibr" rid="B1">Anderson and Ingram (1993)</xref> and <xref ref-type="bibr" rid="B27">Okalebo et&#xa0;al. (2002)</xref>.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>Map of Kenya showing the sampling sites in the study regions of Kisii, Nyamira and Embu Counties. Source: Generated using GPS co-ordinates.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fhort-02-1061456-g001.tif"/>
</fig>
</sec>
<sec id="s2_2">
<title>Soil DNA extraction and next generation sequencing (NGS) of soil metagenome targeting 16S rDNA and ITS regions</title>
<p>DNA for metagenomic analysis was extracted from 200 mg composite soil samples using soil DNA extraction kit (Invitrogen by Thermofisher Scientific) according to the manufacturer&#x2019;s instructions. The DNA pellets were washed with 70% ethanol and stained using SYBR Green dye and subjected to gel electrophoresis in 1.2% agarose gel in 0.5X TBE buffer at 80&#xa0;V for 20 minutes. A 100 bp gene ruler was used to estimate the band sizes (<xref ref-type="bibr" rid="B20">Gupta et&#xa0;al., 2018</xref>).</p>
<p>The 16S rRNA primer pair, 515F GTGYCAGCMGCCGCGGTAA/806R GGACTACNVGGGTWTCTAAT for bacterial communities and the internal transcribed spacer (ITS) primer pair, ITS1F CTTGGTCATTTAGAGGAAGTAA/ITS4R TCCTCCGCTTATTGATATGC for fungal communities were used to evaluate microbial ecology of each sample on the Illumina NovaSeq with methods <italic>via</italic> the bTEFAP<sup>&#xae;</sup> DNA analysis service. Prokaryotic and eukaryotic libraries were constructed and each sample underwent a single-step 35 cycle PCR using HotStarTaq Plus Master Mix Kit (Qiagen, Valencia, CA). The PCR amplification conditions were as follows: initial denaturation at 95&#xb0;C for 10 minutes, followed by 35 cycles (denaturation at 95&#xb0;C for 30 seconds; annealing at 53&#xb0;C for 40 seconds and elongation at 72&#xb0;C for 1 minute) and a final elongation step at 72&#xb0;C for 10 minutes. Following PCR, all amplicon products from different samples were purified using SPRI beads (<xref ref-type="bibr" rid="B34">Soliman et&#xa0;al., 2017</xref>). Samples were sequenced utilizing the Illumina NovaSeq chemistry following manufacturer&#x2019;s instruction (<xref ref-type="bibr" rid="B16">Gastauer et&#xa0;al., 2019</xref>).</p>
</sec>
<sec id="s2_3">
<title>Statistical analysis</title>    <p>The open source package DADA 2 running under R was used to process the raw reads. The Q25 sequence data derived from the sequencing process was processed using the MR DNA ribosomal and functional gene analysis pipeline (<uri xlink:href="http://www.mrdnalab.com">www.mrdnalab.com</uri>, MR DNA, Shallowater, TX). The unique sequences were deionized and identified with illumina sequencing.PCR point errors were removed, followed by chimera removal, thereby providing a or zOTU. Final sequence operational taxonomic units (zOTUs) were taxonomically classified using BLAST against a curated database derived from NCBI (<uri xlink:href="http://www.ncbi.nlm.nih.gov">www.ncbi.nlm.nih.gov</uri>) and compiled into each taxonomic level into both counts and percentages. Counts files contain the actual number of sequences while the percent files contain the relative (proportion) percentage of sequences within each sample that map to the designated taxonomic classification. Statistical analysis was performed using a variety of computer packages including XLstat (<xref ref-type="bibr" rid="B10">Dowd et&#xa0;al., 2008a</xref>), NCSS 2007 (<xref ref-type="bibr" rid="B11">Dowd et&#xa0;al., 2008b</xref>), &#x201c;R&#x201d; (<xref ref-type="bibr" rid="B39">Tasnim et&#xa0;al., 2017</xref>); and NCSS 2010 (<xref ref-type="bibr" rid="B12">Eren et&#xa0;al., 2011</xref> and <xref ref-type="bibr" rid="B37">Swanson et&#xa0;al., 2011</xref>). Alpha and beta diversity analysis was conducted as described previously using Qiime 2 (<xref ref-type="bibr" rid="B5">Bolyen et&#xa0;al., 2018</xref>). Based on the analysis, percentages, counts and diversity indices with a P value &lt; 0.05 were recorded as significant.</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<title>Results</title>
<sec id="s3_1">
<title>Soil composition</title>
<p>Soil samples collected from Kisii, Nyamira and Embu counties had varied physicochemical parameters. The samples obtained from the three counties varied in soil organic carbon levels with majority of the soil samples from Embu and Nyamira containing moderate organic carbon levels (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>). The study showed the average pH recorded in the soils obtained from the Counties was 4.94. Additionally, there was a significant difference in the pH between the three Counties (P= 0.01).</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Soil physico- chemical properties of rhizospheric soil obtained from Kisii, Nyamira and Embu Counties.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="bottom" align="left"/>
<th valign="middle" align="center">Embu</th>
<th valign="middle" align="center">Kisii</th>
<th valign="middle" align="center">Nyamira</th>
<th valign="middle" align="center">P- Value</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="center">
<bold>pH</bold>
</td>
<td valign="middle" align="center">4.94 &#xb1; 0.12a</td>
<td valign="middle" align="center">6.15 &#xb1; 0.24b</td>
<td valign="middle" align="center">5.09 &#xb1; 0.17b</td>
<td valign="middle" align="center">0.01</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>TN</bold>
</td>
<td valign="middle" align="center">0.61 &#xb1; 0.30a</td>
<td valign="middle" align="center">0.16 &#xb1; 0.01a</td>
<td valign="middle" align="center">0.21 &#xb1; 0.01a</td>
<td valign="middle" align="center">0.14</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>TOC</bold>
</td>
<td valign="middle" align="center">18.20 &#xb1; 11.20a</td>
<td valign="middle" align="center">1.72 &#xb1; 0.10b</td>
<td valign="middle" align="center">2.39 &#xb1; 0.11b</td>
<td valign="middle" align="center">0.03</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>TP</bold>
</td>
<td valign="middle" align="center">37.35 &#xb1; 7.07a</td>
<td valign="middle" align="center">36.30 &#xb1; 3.40a</td>
<td valign="middle" align="center">32.00 &#xb1; 3.27a</td>
<td valign="middle" align="center">0.71</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>TK</bold>
</td>
<td valign="middle" align="center">1.15 &#xb1; 0.20a</td>
<td valign="middle" align="center">1.04 &#xb1; 0.14a</td>
<td valign="middle" align="center">1.50 &#xb1; 0.44a</td>
<td valign="middle" align="center">0.62</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Ca</bold>
</td>
<td valign="middle" align="center">1.28 &#xb1; 0.50ab</td>
<td valign="middle" align="center">3.32 &#xb1; 0.66a</td>
<td valign="middle" align="center">1.50 &#xb1; 0.44ab</td>
<td valign="middle" align="center">0.02</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Mg</bold>
</td>
<td valign="middle" align="center">2.09 &#xb1; 0.23a</td>
<td valign="middle" align="center">3.07 &#xb1; 0.30a</td>
<td valign="middle" align="center">2.21 &#xb1; 0.40a</td>
<td valign="middle" align="center">0.08</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Mn</bold>
</td>
<td valign="middle" align="center">1.32 &#xb1; 0.22a</td>
<td valign="middle" align="center">1.27 &#xb1; 0.11a</td>
<td valign="middle" align="center">1.10 &#xb1; 0.33a</td>
<td valign="middle" align="center">0.97</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Cu</bold>
</td>
<td valign="middle" align="center">2.39 &#xb1; 1.12a</td>
<td valign="middle" align="center">1.84 &#xb1; 0.24a</td>
<td valign="middle" align="center">2.52 &#xb1; 0.63a</td>
<td valign="middle" align="center">0.71</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Fe</bold>
</td>
<td valign="middle" align="center">54.70 &#xb1; 6.50b</td>
<td valign="middle" align="center">70.76 &#xb1; 4.03ab</td>
<td valign="middle" align="center">84.20 &#xb1; 11.70a</td>
<td valign="middle" align="center">0.05</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Zn</bold>
</td>
<td valign="middle" align="center">9.31 &#xb1; 1.97b</td>
<td valign="middle" align="center">16.65 &#xb1; 3.92a</td>
<td valign="middle" align="center">19.84 &#xb1; 3.12a</td>
<td valign="middle" align="center">0.04</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Na</bold>
</td>
<td valign="middle" align="center">1.40 &#xb1; 0.70ab</td>
<td valign="middle" align="center">0.34 &#xb1; 0.06a</td>
<td valign="middle" align="center">0.34 &#xb1; 0.06a</td>
<td valign="middle" align="center">0.05</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>pH, acidity/basicity; TN, total nitrogen; TOC, total organic carbon; TP, total phosphorus; TK, total potassium; Ca, calcium; Mg, magnesium; Mn, Manganese; Cu, Copper; Fe, Iron; Zn, Zinc and Na, Sodium. Different letters indicate significantly different between treatments (P &lt; 0.05) according to Tukeys honest significance test (HSD).</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s3_2">
<title>Microbial distribution</title>
<p>The bacterial communities varied in the different rhizospheric soil samples obtained from the three Counties. A total of 420000 sequences were parsed and 335089 were then mapped to (operational taxonomic units (OTUs), 324697 sequences identified within the Bacteria and Archaea domains. The dominant bacterial phyla were Actinobacteria, Proteobacteria, Acidobacteria (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Relative abundance of total observed bacteria and archea domain phyla in banana soil rhizosphere samples from Nyamira County (N1, N4, N6, N8), Kisii County (C11, C14, C16, C19) and Embu County (C3, C5, C7, C10).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fhort-02-1061456-g002.tif"/>
</fig>
<p>A total of 391220 sequences were parsed and 314531 sequences identified within the Fungi kingdom and were the basis of identification of fungal phyla (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). Fungal diversity was higher in soil samples obtained from Kisii County based on Shannon diversity metrics.</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Relative abundance of total observed fungi kingdom phyla in banana rhizosphere soil samples from Nyamira County (N1, N4, N6, N8), Kisii County (C11, C14, C16, C19) and Embu County (C3, C5, C7, C10).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fhort-02-1061456-g003.tif"/>
</fig>
<p>Based on the dual hierarchal dendrogram, there was a lack of distinct clustering between the presumed sample groups N and C (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>). There was no clear evidence of a significant difference between sample groups. The heatmap obtained from the dual hierarchal classification of the predominant genera enabled the visualization and analysis of multi-dimensional datasets such as data obtained from this study.</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Dual hierarchal dendrogram evaluation of the taxonomic classification data of bacterial genera, with each sample clustered on the X-axis labeled based soil sample from Nyamira County (N1, N4, N6, N8), Embu County (C3, C5, C7, C10) and Kisii County (C11, C14, C16, C19). The heatmap represents the relative percentages of each genus. The predominant genera are represented along the Y-axis (right).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fhort-02-1061456-g004.tif"/>
</fig>
<p>A dual hierarchal dendrogram displayed the predominant genera with clustering related to the different groups. Based on the lack of distinct clustering between the presumed sample groups N and C (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>), there is no clear evidence of a significant difference between sample groups. Based on the results, <italic>Fusarium</italic> sp., a commonly known plant pathogenic genera was significantly abundant in soil samples from Nyamira County (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>).</p>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Dual Hierarchal dendrogram evaluation of the taxonomic classification data of fungal genera, with each sample clustered on the X-axis labeled based soil sample from Nyamira County (N1, N4, N6, N8), Embu County (C3, C5, C7, C10) and Kisii County (C11, C14, C16, C19). The heatmap represents the relative percentages of each genus. The predominant genera are represented along the Y-axis (right).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fhort-02-1061456-g005.tif"/>
</fig>
<p>Plant beneficial fungi (<italic>Trichoderma</italic>, <italic>Talaromyces</italic> and arbuscular mycorrhiza fungal species such as <italic>Gigaspora</italic>) commonly used as bioenhancers were detected in some samples but at low abundance levels.</p>
</sec>
<sec id="s3_3">
<title>Microbial diversity and richness</title>
<p>To determine the alpha diversity, the Shannon-Wiener Index at 20,000 reads were sufficient. This indicated that all the samples were equally and sufficiently sampled and the sequence depth was sufficient to capture all the fungal community diversity. Based on Shannon diversity metrics, the highest bacterial diversity was recorded in a soil sample obtained from Embu County (<xref ref-type="table" rid="T2">
<bold>Table&#xa0;2</bold>
</xref>).</p>
<table-wrap id="T2" position="float">
<label>Table&#xa0;2</label>
<caption>
<p>Alpha and Beta diversity bacterial communities analysis of banana rhizosphere soil samples.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="bottom" align="left">Sample Identity</th>
<th valign="bottom" align="center">Shannon-Wiener Index</th>
<th valign="bottom" align="center">Faith</th>
<th valign="bottom" align="center">PCoA</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="bottom" align="left">C14</td>
<td valign="bottom" align="center">8.961142</td>
<td valign="bottom" align="center">79.44049</td>
<td valign="bottom" align="center">-0.072402585</td>
</tr>
<tr>
<td valign="bottom" align="left">N4</td>
<td valign="bottom" align="center">8.215836</td>
<td valign="bottom" align="center">45.39901</td>
<td valign="bottom" align="center">0.156259897</td>
</tr>
<tr>
<td valign="bottom" align="left">N8</td>
<td valign="bottom" align="center">9.310428</td>
<td valign="bottom" align="center">78.61191</td>
<td valign="bottom" align="center">0.291114114</td>
</tr>
<tr>
<td valign="bottom" align="left">C10</td>
<td valign="bottom" align="center">8.518025</td>
<td valign="bottom" align="center">75.05421</td>
<td valign="bottom" align="center">-0.070074251</td>
</tr>
<tr>
<td valign="bottom" align="left">C11</td>
<td valign="bottom" align="center">9.292135</td>
<td valign="bottom" align="center">108.6745</td>
<td valign="bottom" align="center">-0.050913035</td>
</tr>
<tr>
<td valign="bottom" align="left">C16</td>
<td valign="bottom" align="center">8.637193</td>
<td valign="bottom" align="center">67.11941</td>
<td valign="bottom" align="center">-0.001735964</td>
</tr>
<tr>
<td valign="bottom" align="left">C19</td>
<td valign="bottom" align="center">8.623961</td>
<td valign="bottom" align="center">66.22904</td>
<td valign="bottom" align="center">-0.009044414</td>
</tr>
<tr>
<td valign="bottom" align="left">C3</td>
<td valign="bottom" align="center">8.73809</td>
<td valign="bottom" align="center">91.60279</td>
<td valign="bottom" align="center">-0.101475774</td>
</tr>
<tr>
<td valign="bottom" align="left">C5</td>
<td valign="bottom" align="center">9.301601</td>
<td valign="bottom" align="center">106.0649</td>
<td valign="bottom" align="center">-0.057552317</td>
</tr>
<tr>
<td valign="bottom" align="left">C7</td>
<td valign="bottom" align="center">8.948829</td>
<td valign="bottom" align="center">80.48075</td>
<td valign="bottom" align="center">-0.077219799</td>
</tr>
<tr>
<td valign="bottom" align="left">N1</td>
<td valign="bottom" align="center">8.275062</td>
<td valign="bottom" align="center">48.58578</td>
<td valign="bottom" align="center">0.280032429</td>
</tr>
<tr>
<td valign="bottom" align="left">N6</td>
<td valign="bottom" align="center">5.36682</td>
<td valign="bottom" align="center">15.70566</td>
<td valign="bottom" align="center">-0.286988302</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Key: Shannon-Wiener Index, faith and Principal coordinate analysis (PCoA) indices of soil sample from Nyamira County (N1, N4, N6, N8), Embu County (C3, C5, C7, C10) and Kisii County (C11, C14, C16, C19).</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>The &#x3b1;- and &#x3b2;-diversity of the bacterial and fungal communities in the sampled farms showed no significant differences. The Shannon diversity metrics of fungal communities were low especially in samples obtained from Nyamira County (N1, N4, N6 and N8). However, bacterial community diversity metrics were higher with the lowest diversity recorded in soil sample N6 obtained from Nyamira County (<xref ref-type="table" rid="T3">
<bold>Table&#xa0;3</bold>
</xref>).</p>
<table-wrap id="T3" position="float">
<label>Table&#xa0;3</label>
<caption>
<p>Alpha and Beta diversity metrics of the fungal communities&#x2019; analysis of banana rhizospere soil samples.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="bottom" align="left">Sample Identity</th>
<th valign="bottom" align="center">Shannon-Wiener Index</th>
<th valign="bottom" align="center">Faith</th>
<th valign="bottom" align="center">PCoA</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="bottom" align="left">N6</td>
<td valign="bottom" align="center">0.677111</td>
<td valign="bottom" align="center">3.814889</td>
<td valign="bottom" align="center">-0.40025</td>
</tr>
<tr>
<td valign="bottom" align="left">N1</td>
<td valign="bottom" align="center">3.26986</td>
<td valign="bottom" align="center">11.92947</td>
<td valign="bottom" align="center">0.269778</td>
</tr>
<tr>
<td valign="bottom" align="left">N4</td>
<td valign="bottom" align="center">3.667344</td>
<td valign="bottom" align="center">10.82037</td>
<td valign="bottom" align="center">-0.56726</td>
</tr>
<tr>
<td valign="bottom" align="left">N8</td>
<td valign="bottom" align="center">3.22053</td>
<td valign="bottom" align="center">8.366606</td>
<td valign="bottom" align="center">0.295455</td>
</tr>
<tr>
<td valign="bottom" align="left">C14</td>
<td valign="bottom" align="center">6.686194</td>
<td valign="bottom" align="center">52.56977</td>
<td valign="bottom" align="center">0.032562</td>
</tr>
<tr>
<td valign="bottom" align="left">C16</td>
<td valign="bottom" align="center">5.792565</td>
<td valign="bottom" align="center">39.74698</td>
<td valign="bottom" align="center">0.020006</td>
</tr>
<tr>
<td valign="bottom" align="left">C19</td>
<td valign="bottom" align="center">6.079599</td>
<td valign="bottom" align="center">31.46444</td>
<td valign="bottom" align="center">0.025211</td>
</tr>
<tr>
<td valign="bottom" align="left">C5</td>
<td valign="bottom" align="center">4.189097</td>
<td valign="bottom" align="center">14.2502</td>
<td valign="bottom" align="center">-0.00526</td>
</tr>
<tr>
<td valign="bottom" align="left">C10</td>
<td valign="bottom" align="center">5.496617</td>
<td valign="bottom" align="center">44.34761</td>
<td valign="bottom" align="center">0.03522</td>
</tr>
<tr>
<td valign="bottom" align="left">C11</td>
<td valign="bottom" align="center">4.805027</td>
<td valign="bottom" align="center">23.60839</td>
<td valign="bottom" align="center">-0.08128</td>
</tr>
<tr>
<td valign="bottom" align="left">C3</td>
<td valign="bottom" align="center">5.985529</td>
<td valign="bottom" align="center">30.4308</td>
<td valign="bottom" align="center">-0.01315</td>
</tr>
<tr>
<td valign="bottom" align="left">C7</td>
<td valign="bottom" align="center">6.531445</td>
<td valign="bottom" align="center">47.61447</td>
<td valign="bottom" align="center">-0.01128</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Key: Shannon-Wiener Index, faith and Principal coordinate analysis (PCoA) indices of soil sample from Nyamira County (N1, N4, N6, N8), Embu County (C3, C5, C7, C10) and Kisii County (C11, C14, C16, C19).</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>A Bray-Curtis dissimilarity matrix using principal coordinate analysis (PCoA) of the microbial communities showed that there appears to be phylogenetic grouping amongst sample group N1, N4, N6, sample group C3, C5, C7, C10 that is distinct from sample group C11, C14, C16, C19. Primary vector explains 45.1% of the variation between the samples. Beta diversity analysis showed the microbial community structure of the different soil samples. A principal coordinate analysis allowed for visualization and comparison of the communities of microbes as a whole taking into account differences in the samples and phylogenetic relatedness.</p>
<p>There were variations in bacterial and fungal communities which closely correlated with the soil parameters based on Canonical correspondence analysis. These included soil pH, total organic carbon (TOC), and total nitrogen which were the main drivers of microbial community distribution (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6</bold>
</xref>).</p>
<fig id="f6" position="float">
<label>Figure&#xa0;6</label>
<caption>
<p>Canonical correspondence analysis <bold>(A)</bold> Beneficial and <bold>(B)</bold> Pathogenic bacterial species and soil chemical parameters for banana rhizospheric soil. Red arrows represent fungal species while the blue arrows represent soil physico-chemical parameters.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fhort-02-1061456-g006.tif"/>
</fig>
<p>Plant beneficial bacteria species such as <italic>Bradyrhizobium, Azotobacter</italic> and <italic>Rhizobium</italic> species distribution was mainly affected by soil pH, soil P (Phosphorus), Total Nitrogen (TN) and TOC. In plant pathogenic bacterial species TN, TOC and soil pH were the main drivers, in which soils with high pH, adequate TN and TOC had low incidences of pathogenic bacterial species such as <italic>Xanthomonas</italic> and <italic>Ralstonia</italic>.</p>
<p>The distribution and abundance of beneficial fungal species such as arbuscular mycorrhiza fungi (AMF) which includes <italic>Gigaspora</italic> sp was affected by soil pH with low counts observed in highly acidic soil. The abundance of fungal genera such as <italic>Acaulospora</italic> were affected by total nitrogen (TN) and total organic carbon (TOC) (<xref ref-type="fig" rid="f7">
<bold>Figure&#xa0;7</bold>
</xref>). Population of plant pathogenic species such as <italic>Colletotrichum</italic> and <italic>Verticillium</italic> were TOC and TN while majority of <italic>Fusarium</italic> species were affected by soil pH and P.</p>
<fig id="f7" position="float">
<label>Figure&#xa0;7</label>
<caption>
<p>Canonical correspondence analysis of the <bold>(A)</bold> Beneficial and <bold>(B)</bold> Pathogenic fungal species and soil chemical parameters for banana rhizospheric soil. Red arrows represent fungal species while the blue arrows represent soil physico-chemical parameters.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fhort-02-1061456-g007.tif"/>
</fig>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<title>Discussion</title>
<p>Soil health plays a critical role in ensuring the stability of microbial communities. Soil organic carbon levels are a good indicator of the health status of soil and positively correlate to the yield of crops (<xref ref-type="bibr" rid="B2">Bennett et&#xa0;al., 2010</xref>). Highly acidic conditions were detected in the majority of soil samples collected from Embu and Nyamira which is worrying. <xref ref-type="bibr" rid="B8">Delgado and G&#xf3;mez (2016)</xref> has reported that a pH of below 5.5 is harmful to agroecosystems since it negatively influences plant and environment interaction, indicating that the soil pH in Embu County poses a great danger to agroecosystems.</p>
<p>It has been reported that rhizospheric soil that is closest to the root system and is essential in studying microbial communities (<xref ref-type="bibr" rid="B3">Berendsen et&#xa0;al., 2012</xref>). <xref ref-type="bibr" rid="B36">Sui et&#xa0;al. (2019)</xref> and <xref ref-type="bibr" rid="B7">Chaudhary et&#xa0;al. (2021)</xref> <xref ref-type="bibr" rid="B42">Zhu et&#xa0;al. (2018)</xref>, reported that Actinobacteria are among the most identified rhizospheric bacteria phyla in banana plants. The abundance of Proteobacteria and Actinobacteria has been previously linked to long periods of production (<xref ref-type="bibr" rid="B30">Pang et&#xa0;al., 2021</xref>). However, Actinobacteria have been reported to produce antibiotics as well as having an important role in organic matter decomposition (<xref ref-type="bibr" rid="B41">Zhang et&#xa0;al., 2017</xref>). <xref ref-type="bibr" rid="B3">Berendsen et&#xa0;al. (2012)</xref> reported that microbial community composition in rhizosperic soil are linked to soil quality as well as the health of the crop grown. Microbiota associated with soil has great influence on how plants are able to adapt and respond to changes in the environments such as emergence of stressors such as salinity and drought (<xref ref-type="bibr" rid="B41">Zhang et&#xa0;al., 2017</xref>). High abundance were noted in the phyla Basidiomycota and Ascomycota similar to results by <xref ref-type="bibr" rid="B35">Sommermann et&#xa0;al. (2018)</xref> and <xref ref-type="bibr" rid="B18">G&#xf3;mez-Lama et&#xa0;al. (2021)</xref>.</p>
<p>
<xref ref-type="bibr" rid="B33">Rossmann et&#xa0;al. (2012)</xref> reported the presence of potential plant, human and insect pathogens similar to the results obtained in this study. <xref ref-type="bibr" rid="B19">Gu et&#xa0;al. (2016)</xref> utilized high-throughput gene expression to visualize hierarchal classification and species richness, similar to this study. Plant beneficial bacteria genera diversity such as <italic>Rhizobium</italic> and <italic>Azotobacter</italic> differed with that of probable plant pathogenic bacteria genera such as <italic>Ralstonia</italic> in all the soil samples similar to results reported by Kepler et al (<xref ref-type="bibr" rid="B22">Kepler et&#xa0;al., 2020</xref>). The presence of <italic>Rhizoctonia</italic>, <italic>Colletotrichium</italic> and <italic>Verticillium</italic> was an indicator of disease causing fungal pathogens in some of the soil samples similar to results by <xref ref-type="bibr" rid="B35">Sommermann et&#xa0;al. (2018)</xref>.</p>    <p>Investigation of abundance of plant beneficial fungi such as those used as biocontrol agents in agroecosystems is a field that has not been extensively studied (<xref ref-type="bibr" rid="B21">Harman et&#xa0;al., 2004</xref>). The variations in bacterial genera indicate differences in land use strategies resulting in changes in microbial community structure and diversity (<xref ref-type="bibr" rid="B25">Lynn et&#xa0;al., 2017</xref>). <xref ref-type="bibr" rid="B13">Fan et&#xa0;al. (2020)</xref> reported variations in bacterial and fungal communities in relation to soil parameters. It has been reported that many soil variables such as soil organic matter, salinity and pH have a lot of impact on soil microbial populations (<xref ref-type="bibr" rid="B15">Gans et&#xa0;al., 2005</xref>). Additionally, these microbial communities cannot recover to their natural state even after many years (<xref ref-type="bibr" rid="B31">Pellegrino et&#xa0;al., 2014</xref>). Based on previous studies pH impacts soil microbial communities therefore defines taxonomic composition of microbial communities (<xref ref-type="bibr" rid="B8">Delgado and G&#xf3;mez, 2016</xref>).</p>
<p>It has been established that soil composition and function are associated with plant soil borne disease outbreaks in which healthy fields have different microbial communities from the infected ones (<xref ref-type="bibr" rid="B41">Zhang et&#xa0;al., 2017</xref>). <xref ref-type="bibr" rid="B14">Frac et&#xa0;al. (2018)</xref> reported that the diversity and fungi activity is regulated by biotic and abiotic factors such as soil pH, structure and some nutrients.</p>
</sec>
<sec id="s5" sec-type="conclusion">
<title>Conclusion</title>
<p>Based on the results obtained from this study, there were variations in soil composition and microbial populations in the different regions. The soil physicochemical properties played a significant role in the rhizosphere soil microbial communities. It has been established that plants modify the rhizosphere through various modes such as changes in microbiome composition and function. Studying the interaction between plants, microorganisms and soil physicochemical conditions enables one to understand how each plays a role in ecosystem balance and well as productivity in agroecosystems. The results show that studying soil microbiome in monocropping systems is a great tool in determining ideal microbial community structures for the crops. In addition, application of metagenomics techniques in studying microbial communities in agroecosystems will aid in designing banana production systems as well as targeted approaches in disease management.</p>
</sec>
<sec id="s6" sec-type="data-availability">
<title>Data availability statement</title>
<p>The data presented in the study are deposited on Figshare (<ext-link ext-link-type="uri" xlink:href="https://doi.org/10.6084/m9.figshare.21939977">https://doi.org/10.6084/m9.figshare.21939977</ext-link>).</p>
</sec>
<sec id="s7" sec-type="author-contributions">
<title>Author contributions</title>
<p>JM, OO, EN, and JK conceived and designed the research and data collection tools and participated in drafting the manuscript. CW collected the data, participated in the data analyses, and wrote the manuscript. MM was involved in molecular work and data analyses. All authors contributed to the article and approved the submitted version.</p>
</sec>
</body>
<back>
<sec id="s8" sec-type="funding-information">
<title>Funding</title>
<p>This research was funded by The National Research fund (NRF), Kenya.</p>
</sec>
<ack>
<title>Acknowledgments</title>
<p>We are grateful to the farmers in Kisii, Nyamira and Embu Counties for working with us and Mr DNA Shallowater, TX for their contribution in Next Generation Sequencing.</p>
</ack>
<sec id="s9" sec-type="COI-statement">
<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="s10" 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>
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