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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Plant Sci.</journal-id>
<journal-title>Frontiers in Plant Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Plant Sci.</abbrev-journal-title>
<issn pub-type="epub">1664-462X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fpls.2024.1492424</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Plant Science</subject>
<subj-group>
<subject>Review</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Effects of microbial biocontrol agents on tea plantation microecology and tea plant metabolism: a review</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Xie</surname>
<given-names>Yixin</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/2734159"/>
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<role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Cao</surname>
<given-names>Chunxia</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/funding-acquisition/"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Huang</surname>
<given-names>Daye</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/software/"/>
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</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Gong</surname>
<given-names>Yan</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/conceptualization/"/>
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</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Wang</surname>
<given-names>Beibei</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/1537166"/>
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<aff id="aff1">
<sup>1</sup>
<institution>National Biopesticide Engineering Research Centre, Hubei Biopesticide Engineering Research Centre, Hubei Academy of Agricultural Sciences</institution>, <addr-line>Wuhan</addr-line>, <country>China</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>College of Food Science and Technology, Huazhong Agricultural University</institution>, <addr-line>Wuhan</addr-line>, <country>China</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Ankush Prasad, Palack&#xfd; University Olomouc, Czechia</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Sudipta Sankar Bora, Assam Agricultural University, India</p>
<p>Changlong Shu, Institute of Plant Protection (CAAS), China</p>
<p>Deepak Rathi, Palack&#xfd; University, Czechia</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Yan Gong, <email xlink:href="mailto:gongyan@nberc.com">gongyan@nberc.com</email>; Beibei Wang, <email xlink:href="mailto:wangbei_zju@163.com">wangbei_zju@163.com</email>
</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>20</day>
<month>01</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2024</year>
</pub-date>
<volume>15</volume>
<elocation-id>1492424</elocation-id>
<history>
<date date-type="received">
<day>06</day>
<month>09</month>
<year>2024</year>
</date>
<date date-type="accepted">
<day>26</day>
<month>12</month>
<year>2024</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Xie, Cao, Huang, Gong and Wang</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Xie, Cao, Huang, Gong and Wang</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>The quality of fresh tea leaves is crucial to the final product, and maintaining microbial stability in tea plantations is essential for optimal plant growth. Unique microbial communities play a critical role in shaping tea flavor and enhancing plant resilience against biotic stressors. Tea production is frequently challenged by pests and diseases, which can compromise both yield and quality. While biotic stress generally has detrimental effects on plants, it also activates defense metabolic pathways, leading to shifts in microbial communities. Microbial biocontrol agents (MBCAs), including entomopathogenic and antagonistic microorganisms, present a promising alternative to synthetic pesticides for mitigating these stresses. In addition to controlling pests and diseases, MBCAs can influence the composition of tea plant microbial communities, potentially enhancing plant health and resilience. However, despite significant advances in laboratory research, the field-level impacts of MBCAs on tea plant microecology remain insufficiently explored. This review provides insights into the interactions among tea plants, insects, and microorganisms, offering strategies to improve pest and disease management in tea plantations.</p>
</abstract>
<kwd-group>
<kwd>tea</kwd>
<kwd>biotic stress</kwd>
<kwd>biological control</kwd>
<kwd>metabolomics</kwd>
<kwd>tea quality</kwd>
</kwd-group>    <contract-sponsor id="cn001">Hubei Academy of Agricultural Sciences<named-content content-type="fundref-id">10.13039/501100019952</named-content>
</contract-sponsor>
<counts>
<fig-count count="2"/>
<table-count count="3"/>
<equation-count count="0"/>
<ref-count count="215"/>
<page-count count="17"/>
<word-count count="8279"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Plant Symbiotic Interactions</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>Tea is one of the three major non-alcoholic beverages in the world. Global tea demand has increased significantly during the COVID-19 pandemic (<xref ref-type="bibr" rid="B30">Castellana et&#xa0;al., 2021</xref>), a trend that may be closely related to the potential benefits of bioactive substances in tea (<xref ref-type="bibr" rid="B61">Gilbert, 2019</xref>; <xref ref-type="bibr" rid="B7">Bag et&#xa0;al., 2022b</xref>). Reports from the International Tea Committee (ITC) and the Food and Agriculture Organization of the United Nations (FAO) indicated that in 2022, the global annual value of tea production exceeded $17 billion, with the world tea trade amounting to approximately $9.5 billion (<xref ref-type="bibr" rid="B54">FAO, 2022</xref>). The tea industry is among the key agricultural activities in many countries, which is vital in sustaining rural economies (<xref ref-type="bibr" rid="B82">Jayasinghe and Kumar, 2021</xref>; <xref ref-type="bibr" rid="B16">Berm&#xfa;dez et&#xa0;al., 2024</xref>). To ensure the production of high-quality tea, tea farmers and researchers have long been committed to these pursuits. Tea production primarily relies on tea trees (<italic>Camellia sinensis</italic>), and the quality of fresh tea leaves forms the foundation for high-quality finished tea. The growth conditions of tea plants, including growth environment, soil quality, climate, and cultivation practices, significantly impact the quality of fresh tea leaves. However, during the growth process, tea plants frequently face threats from pests and diseases.</p>
<p>Biotic stress factors such as tea blister blight (caused by <italic>Exobasidium vexans</italic> Massee), tea anthracnose (caused by <italic>Colletotrichum</italic> spp.), tea looper (<italic>Ectropis oblique</italic>), and tea red spider mite (<italic>Oligonychus coffeae</italic>) have long threatened tea yield and quality. If not effectively controlled, these pests and diseases can lead to production losses of up to 55% (<xref ref-type="bibr" rid="B69">Hazarika et&#xa0;al., 2009</xref>). Although precise data on economic losses is difficult to determine, it is estimated that these impacts may amount to billions of dollars annually. In recent years, climate change has increased the risk of new pathogens and pests in tea plantations. Rising temperatures, altered rainfall patterns, and extreme weather have expanded the range of these threats, enabling them to thrive in previously unsuitable areas (<xref ref-type="bibr" rid="B131">Pandey et&#xa0;al., 2021b</xref>). Additionally, Biotic stress activates the expression of the defense genes in tea plants such as caffeine, catechins, L-theanine, and volatile compounds (<xref ref-type="bibr" rid="B198">Zeng et&#xa0;al., 2024</xref>), thereby impacting its flavor and health benefits (<xref ref-type="bibr" rid="B15">Berg and Smalla, 2009</xref>). Traditionally, chemical pesticides have long been the primary method for controlling these pests and diseases in tea plantations. However, many studies have demonstrated that the application of synthetic pesticides directly affects environmental microorganisms (<xref ref-type="bibr" rid="B170">Wang and Cernava, 2020</xref>; <xref ref-type="bibr" rid="B176">Win et&#xa0;al., 2021</xref>) and may also indirectly influence them by interfering with plant metabolic pathways (<xref ref-type="bibr" rid="B110">Liu et&#xa0;al., 2018</xref>). For instance, glyphosate can severely weaken the defense mechanisms of glyphosate-sensitive plants (including tea plants) against microbial diseases by disrupting the shikimate pathway, thereby significantly enhancing its efficacy as an herbicide (<xref ref-type="bibr" rid="B120">Martinez et&#xa0;al., 2018</xref>).</p>
<p>In contrast, microbial control methods have increasingly shown advantages in tea plantations (<xref ref-type="bibr" rid="B3">Ahirwar et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B80">Idris et&#xa0;al., 2020</xref>). Microbial biocontrol agents (MBCAs) primarily consist of entomopathogenic and antagonistic microorganisms, which specifically target pests and pathogens while minimizing harm to non-target organisms and the environment (<xref ref-type="bibr" rid="B139">Roy and Muraleedharan, 2014</xref>). Compared to chemical pesticides, MBCAs offer safer and more sustainable pest management solutions. However, since MBCAs contain large quantities of exogenous microorganisms, their impact extends beyond just pest and disease control, influencing the broader tea plant ecosystem (<xref ref-type="bibr" rid="B64">Grosch et&#xa0;al., 2012</xref>). Microorganisms play a crucial role in tea plant growth by forming symbiotic relationships within and on plant surfaces, contributing to a balanced and dynamic ecosystem (<xref ref-type="bibr" rid="B167">Trivedi et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B163">Tan et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B88">Jibola-Shittu et&#xa0;al., 2024</xref>). These microbial communities primarily influence the plant&#x2019;s metabolism or produce bioactive compounds, affecting the plant&#x2019;s characteristic metabolites (<xref ref-type="bibr" rid="B106">Liao et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B177">Wu et&#xa0;al., 2024a</xref>). These interactions shape the community structure and succession of tea plant microorganisms, which are intricately linked to plant health, resilience, and overall growth (<xref ref-type="bibr" rid="B74">Hu et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B181">Xie et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B70">Hazarika et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B6">Bag et&#xa0;al., 2022a</xref>). For example, Xin et&#xa0;al (<xref ref-type="bibr" rid="B182">Xin et&#xa0;al., 2024</xref>)identified specific microorganisms in the root microbiomes of high-theanine and low-theanine tea varieties that may regulate theanine levels by influencing nitrogen metabolism. Similarly, Sun et&#xa0;al (<xref ref-type="bibr" rid="B160">Sun et&#xa0;al., 2019</xref>). isolated an endophytic bacterium (<italic>Luteibacter</italic> spp.) from tea seedlings, which exhibited biocatalytic activity by converting glutamine and ethylamine into theanine. The stability of these microbial communities is affected by various factors (<xref ref-type="bibr" rid="B63">Gong et&#xa0;al., 2024</xref>), such as pesticide application (<xref ref-type="bibr" rid="B53">Duke, 2018</xref>; <xref ref-type="bibr" rid="B66">Hage-Ahmed et&#xa0;al., 2019</xref>), biotic stress (<xref ref-type="bibr" rid="B78">Huang et&#xa0;al., 2023</xref>), abiotic stress (<xref ref-type="bibr" rid="B199">Zeng et&#xa0;al., 2019a</xref>; <xref ref-type="bibr" rid="B22">Bora et&#xa0;al., 2022b</xref>), etc. MBCAs act directly on the microbial community within the tea plant ecosystem and may indirectly influence tea quality by altering the structure of the microbial community (<xref ref-type="bibr" rid="B32">Cernava et&#xa0;al., 2019</xref>). Bora et&#xa0;al (<xref ref-type="bibr" rid="B20">Bora et&#xa0;al., 2022a</xref>). found that using microbial consortia to combat grey blight disease (caused by <italic>Pseudopestalotiopsis curvatispora</italic> Petch) not only suppressed the pathogens effectively but also increased rhizosphere microbial diversity and enhanced leaf nutrient content. Certain MBCAs may also induce systemic resistance in tea plants and improve their nutritional status as biofertilizers. Nevertheless, current research on commercially MBCAs has predominantly focused on the initial screening of biocontrol strains, with relatively less attention given to their practical impacts on ecological microorganisms and tea plant metabolism.</p>
<p>In light of these considerations, this review aims to provide a concise overview of the main types and mechanisms of commercially available or promising MBCAs used in tea plantations, their colonization efficacy, and their impact on the tea plant&#x2019;s microbial community. Additionally, this review explores the influence of biotic stress and exogenous microorganisms on tea plant metabolism, while briefly introducing newly discovered microorganisms and their potential applications in the outlook section. The interactions between the main factors discussed in this review are illustrated in <xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>. By offering new insights into the interactions among tea plants, insects, and microorganisms, this review aims to advance practical pest and disease management strategies in tea plantations and support the biocontrol agent industry.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>The interactions between MBCAs, tea plant microorganisms, insects, tea plant pathogens, and tea plant metabolism. MBCAs, microbial biocontrol agents; ISR, induced systemic resistance; SAR, systemic acquired resistance.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpls-15-1492424-g001.tif"/>
</fig>
</sec>
<sec id="s2">
<label>2</label>
<title>Types and mechanisms of microbial biocontrol agents applied in pests and diseases control of tea</title>
<p>To understand the impact of MBCAs on the micro-ecosystem of tea plantations and the metabolism of tea plants, it is essential first to identify the types of biocontrol agents used and their underlying mechanisms. Some microbial resources discovered in tea plantations exhibit specific activity against pests and pathogens through unique mechanisms, highlighting their significant potential for development. Therefore, in addition to presenting MBCAs that are already widely commercialized in tea plantations, this review also introduces promising biocontrol agents with potential for future application. The MBCAs targeting major pests and pathogens in tea plantations are listed in <xref ref-type="table" rid="T1">
<bold>Tables&#xa0;1</bold>
</xref>, <xref ref-type="table" rid="T2">
<bold>2</bold>
</xref>, respectively.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Microorganisms with biocontrol effects on major tea pests.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center">Target Pest</th>
<th valign="middle" align="center">Microbial Classification</th>
<th valign="middle" align="left">Microbial Species/Strain</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" rowspan="3" align="center">
<italic>Ectropis obliqua</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">Bacillus thuringiensis (<xref ref-type="bibr" rid="B12">Barthakur, 2011</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Metarhizium anisopliae</italic> (<xref ref-type="bibr" rid="B207">Zhao et&#xa0;al., 2023a</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Virus</td>
<td valign="middle" align="left">Ectropis obliqua nuclear polyhedrosis virus (<xref ref-type="bibr" rid="B194">Ye et&#xa0;al., 2014</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Caloptilia theivora</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus thuringiensis</italic> (<xref ref-type="bibr" rid="B12">Barthakur, 2011</xref>), <italic>Enterobactor</italic> sp (<xref ref-type="bibr" rid="B45">De et&#xa0;al., 2008</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Scirtothrips dorsalis</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus thuringiensis</italic> (<xref ref-type="bibr" rid="B65">Gurusubramanian et&#xa0;al., 2008</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Eterusia magnifica</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus thuringiensis</italic> (<xref ref-type="bibr" rid="B123">Mukhopadhyay et&#xa0;al., 2010</xref>)</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="center">
<italic>Microtermes obesi</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus thuringiensis</italic> (<xref ref-type="bibr" rid="B152">Singha et&#xa0;al., 2010</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Beauveria bassiana</italic> (<xref ref-type="bibr" rid="B155">Singha et&#xa0;al., 2011</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Paralepidosaphes tubulorum</italic> Ferris</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B194">Ye et&#xa0;al., 2014</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Chrysomphalus ficus</italic> L</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B194">Ye et&#xa0;al., 2014</xref>)</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="center">
<italic>Oligonychus coffeae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Pseudomonas fluorescens</italic> (<xref ref-type="bibr" rid="B138">Roobak Kumar et&#xa0;al., 2011</xref>), <italic>Bacillus velezensis</italic> (<xref ref-type="bibr" rid="B21">Bora et&#xa0;al., 2023</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Metarhizium anisopliae</italic> (<xref ref-type="bibr" rid="B46">Deka et&#xa0;al., 2022a</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Buzura suppressaria</italic>
</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Beauveria bassiana</italic> (<xref ref-type="bibr" rid="B60">Ghatak and Reza, 2007</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Empoasca vitis</italic>
</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Beauveria bassiana</italic> (<xref ref-type="bibr" rid="B55">Feng et&#xa0;al., 2004</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Myllocerinus aurolineatus</italic>
</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Beauveria bassiana</italic> (<xref ref-type="bibr" rid="B128">Pandey et&#xa0;al., 2021a</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Helopeltis theivora</italic> Waterhouse</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Beauveria bassiana</italic> (<xref ref-type="bibr" rid="B47">Deka et&#xa0;al., 2021</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Aleurocanthus camphalus</italic>
</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Paecilomyces cinnamomeus</italic> (<xref ref-type="bibr" rid="B141">Saito et&#xa0;al., 2012</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Microcerotermes beesoni</italic> Snyder</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Metarhizium anisopliae</italic> (<xref ref-type="bibr" rid="B99">Kumhar et&#xa0;al., 2020</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Homona magnanima</italic>
</td>
<td valign="middle" align="center">virus</td>
<td valign="middle" align="left">Granulosis virus (<xref ref-type="bibr" rid="B147">Sato et&#xa0;al., 1986</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Adoxophyes</italic> sp.</td>
<td valign="middle" align="center">virus</td>
<td valign="middle" align="left">Granulosis virus (<xref ref-type="bibr" rid="B147">Sato et&#xa0;al., 1986</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Euproctis pseudoconspersa</italic>
</td>
<td valign="middle" align="center">virus</td>
<td valign="middle" align="left">Euproctis pseudoconspersa nuclear polyhedrosis virus (<xref ref-type="bibr" rid="B194">Ye et&#xa0;al., 2014</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Myllocerinus aurolineatus</italic> Voss</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Metarhizium pingshaense</italic> (<xref ref-type="bibr" rid="B59">Fu et&#xa0;al., 2023</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Hyposidra talaca</italic> Walker</td>
<td valign="middle" align="center">virus</td>
<td valign="middle" align="left">Hyposidra talaca NPV (<xref ref-type="bibr" rid="B48">Deka et&#xa0;al., 2023</xref>)</td>
</tr>
</tbody>
</table>
</table-wrap>
<table-wrap id="T2" position="float">
<label>Table&#xa0;2</label>
<caption>
<p>Microorganisms with biocontrol effects on tea plant pathogens.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center">Target Pathogens</th>
<th valign="middle" align="center">Microbial Classification</th>
<th valign="middle" align="center">Microbial Species/Strain</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="center">
<italic>Curvularia eragrostidis</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>)</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="center">
<italic>Pestalotiopsis theae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>),<break/>
<italic>Paecilomyces lilacinus</italic> (<xref ref-type="bibr" rid="B188">Xu et&#xa0;al., 2023a</xref>), <italic>Bacillus subtilis</italic> (<xref ref-type="bibr" rid="B97">Kolandasamy et&#xa0;al., 2023</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Virus</td>
<td valign="middle" align="left">Pestalotiopsis theae chrysovirus-1 (<xref ref-type="bibr" rid="B211">Zhou et&#xa0;al., 2021</xref>)</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="center">
<italic>Colletotrichum camelliae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>); <italic>Bacillus velezensis</italic> (<xref ref-type="bibr" rid="B71">He et&#xa0;al., 2024</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Rhizophagus intraradices</italic> (<xref ref-type="bibr" rid="B37">Chen et&#xa0;al., 2022</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Lasiodiplodia theobromae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Rhizoctonia solani</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Sphaerostilbe repens</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Fomes lamaoensis</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>), <italic>Bacillus megaterium</italic> (<xref ref-type="bibr" rid="B33">Chakraborty et&#xa0;al., 2006</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Poria hypobrunae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Ustulina zonata</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>)</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="center">
<italic>Corticium theae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus</italic> sp (<xref ref-type="bibr" rid="B81">Islam et&#xa0;al., 2018</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Fungi</td>    <td valign="middle" align="left">
<italic>Aspergillus niger</italic>, <italic>Trichoderma atroviride, Trichoderma cithnoviride</italic> (<xref ref-type="bibr" rid="B165">Thoudam and Dutta, 2012</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Colletotrichum theae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus subtilis</italic> (<xref ref-type="bibr" rid="B96">Kim et&#xa0;al., 2009</xref>)</td>
</tr>
<tr>
<td valign="middle" rowspan="3" align="center">
<italic>Phomopsis theae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus megaterium</italic> (<xref ref-type="bibr" rid="B97">Kolandasamy et&#xa0;al., 2023</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Streptomyces</td>
<td valign="middle" align="left">
<italic>Streptomyces</italic> sp (<xref ref-type="bibr" rid="B119">Marimuthu et&#xa0;al., 2020</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Trichoderma viride</italic> (<xref ref-type="bibr" rid="B97">Kolandasamy et&#xa0;al., 2023</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Macrophoma theicola</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus amyloliquefaciens</italic> (<xref ref-type="bibr" rid="B86">Jeyaraman and Robert, 2018</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Colletotrichum fructicola</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus velezensis</italic> (<xref ref-type="bibr" rid="B71">He et&#xa0;al., 2024</xref>)</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="center">
<italic>Colletotrichum gloeosporioides</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus velezensis</italic> (<xref ref-type="bibr" rid="B71">He et&#xa0;al., 2024</xref>), <italic>Bacillus altitudinis</italic> (<xref ref-type="bibr" rid="B178">Wu et&#xa0;al., 2024b</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Trichoderma Asperellum</italic> (<xref ref-type="bibr" rid="B150">Shang et&#xa0;al., 2020</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Colletotrichum siamense</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus velezensis</italic> (<xref ref-type="bibr" rid="B71">He et&#xa0;al., 2024</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Colletotrichum kahawae</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Bacillus velezensis</italic> (<xref ref-type="bibr" rid="B71">He et&#xa0;al., 2024</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Exobasidium vexans</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Ochrobactrum anthropi</italic> (<xref ref-type="bibr" rid="B158">Sowndhararajan et&#xa0;al., 2013</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Cercospora theae</italic>
</td>
<td valign="middle" align="center">Streptomyces</td>
<td valign="middle" align="left">
<italic>Streptomyces sannanensis</italic> (<xref ref-type="bibr" rid="B62">Gnanamangai and Ponmurugan, 2012</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Fusarium solani</italic>
</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Trichoderma asperellum</italic>, <italic>Trichoderma harzianum</italic>, <italic>Trichoderma asperellum</italic> (<xref ref-type="bibr" rid="B99">Kumhar et&#xa0;al., 2020</xref>); <italic>Trichoderma reesei</italic> (<xref ref-type="bibr" rid="B130">Pandey et&#xa0;al., 2023</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Pseudopestalotiopsis theae</italic>
</td>
<td valign="middle" align="center">Fungi</td>
<td valign="middle" align="left">
<italic>Trichoderma reesei</italic> (<xref ref-type="bibr" rid="B129">Pandey et&#xa0;al., 2022</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Curvularia eragrostidis</italic>
</td>
<td valign="middle" align="center">Bacteria</td>
<td valign="middle" align="left">
<italic>Serratia marcescens</italic> (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>)</td>
</tr>
</tbody>
</table>
</table-wrap>
<sec id="s2_1">
<label>2.1</label>
<title>Entomopathogenic microorganisms</title>
<p>Entomopathogenic microorganisms predominantly consist of bacteria, fungi, and viruses (<xref ref-type="bibr" rid="B49">Deka et&#xa0;al., 2022b</xref>). Bacterial entomopathogens primarily achieve insecticidal effects by secreting toxic proteins that inhibit pest growth (<xref ref-type="bibr" rid="B127">Pan et&#xa0;al., 2024</xref>). Research indicates that almost all insect-pathogenic bacteria isolated from tea pests belong to <italic>Bacillus thuringiensis</italic> (Bt) (<xref ref-type="bibr" rid="B194">Ye et&#xa0;al., 2014</xref>). The insecticidal mechanism of Bt involves the production of insecticidal crystal proteins (ICPs) within the sporangium during the sporulation phase, which exert stomach poisoning and contact toxicity effects on pests. These ICPs exhibit high specificity, becoming toxic only upon activation within specific host insects (<xref ref-type="bibr" rid="B5">Azizoglu et&#xa0;al., 2023</xref>). In the 1970s and 1980s, China employed Bt to manage <italic>Lepidopteran</italic> pests, achieving control efficacy rates of over 95% (<xref ref-type="bibr" rid="B12">Barthakur, 2011</xref>). With the continuous discovery of new strains, Bt has demonstrated effective control against other common tea plantation pests, such as tea thrips (<italic>Scirtothrips dorsalis</italic>) (<xref ref-type="bibr" rid="B65">Gurusubramanian et&#xa0;al., 2008</xref>), red slug caterpillar (<italic>Eterusia magnifica</italic>) (<xref ref-type="bibr" rid="B123">Mukhopadhyay et&#xa0;al., 2010</xref>), and tea termite (<italic>Microterms obesi</italic>) (<xref ref-type="bibr" rid="B152">Singha et&#xa0;al., 2010</xref>). Not only in tea plantations, but Bt has become the most widely used commercial bacterial insecticide worldwide (<xref ref-type="bibr" rid="B27">Bravo et&#xa0;al., 2011</xref>). Current research suggests that Bt&#x2019;s effectiveness in tea plantation ecosystems could be further enhanced through the use of highly virulent strains (<xref ref-type="bibr" rid="B9">Banik et&#xa0;al., 2019</xref>), new delivery systems (<xref ref-type="bibr" rid="B127">Pan et&#xa0;al., 2024</xref>), or combined use with entomopathogenic fungi (<xref ref-type="bibr" rid="B169">Vimala Devi et&#xa0;al., 2020</xref>).</p>
<p>Apart from Bt, several other bacteria have shown potential in controlling tea plantation pests. Damayanti et&#xa0;al (<xref ref-type="bibr" rid="B45">De et&#xa0;al., 2008</xref>). isolated <italic>Enterobacter</italic> sp. from <italic>Caloptilia theivora</italic>, which exhibited an LC50 value of 363.1 &#x3bc;g/ml (bacterial weight/volume of water) against <italic>C.theivora</italic> larvae. Additionally, Wang et&#xa0;al (<xref ref-type="bibr" rid="B194">Ye et&#xa0;al., 2014</xref>). discovered that <italic>Serratia marcescens</italic> showed pathogenicity against two scale insects, <italic>Paralepidosaphes tubulorum</italic> Ferris and <italic>Chrysomphalus ficus</italic> (<xref ref-type="bibr" rid="B138">Roobak Kumar et&#xa0;al., 2011</xref>). Popy et&#xa0;al (<xref ref-type="bibr" rid="B21">Bora et&#xa0;al., 2023</xref>)found that <italic>Pseudomonas fluorescens</italic> and <italic>Bacillus velezensis</italic> exhibited lethal activity against the <italic>Oligonychus coffeae</italic> by secreting hydrolytic enzymes and secondary metabolites. However, most of these bacteria, aside from Bt, face significant challenges such as development difficulties, high costs, and unstable activity, which limit their extensive application in tea plantations.</p>
<p>Entomopathogenic fungi (EPF) thrive in ecosystems with humidity above 80%, making valuable for pest control in the hot, humid climates of tropical and subtropical tea plantations (<xref ref-type="bibr" rid="B194">Ye et&#xa0;al., 2014</xref>). The potential of <italic>Beauveria bassiana</italic> as a non-chemical pest control agent was first reported in 1837, leading to increased attention on EPF (<xref ref-type="bibr" rid="B18">Bhattacharyya et&#xa0;al., 2022</xref>). The main genera involved include <italic>Beauveria</italic>, <italic>Metarhizium</italic>, <italic>Paecilomyces</italic>, <italic>Hirsutella</italic>, and <italic>Nomuraea</italic> (<xref ref-type="bibr" rid="B141">Saito et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B139">Roy and Muraleedharan, 2014</xref>; <xref ref-type="bibr" rid="B39">Cheramgoi et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B1">Abdel-Raheem et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B28">Canassa et&#xa0;al., 2020</xref>). Notably, <italic>B.bassiana</italic> and <italic>Metarhizium anisopliae</italic> have been registered as biopesticides and are extensively employed for managing tea pests in regions including China, India, and Sri Lanka (<xref ref-type="bibr" rid="B80">Idris et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B121">McGuire and Northfield, 2020</xref>). Unlike bacteria, fungi infect insects primarily by spreading spores. The fungal hyphae penetrate the insect cuticle through mechanical pressure and the action of hydrolytic enzymes, thereby exerting a contact insecticidal effect (<xref ref-type="bibr" rid="B171">Wang et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B149">Shang et&#xa0;al., 2024</xref>). For example, <italic>B.bassiana</italic> has shown significant effectiveness in controlling various pests in tea plantations, including the tea looper (<italic>Buzura suppressaria</italic>) (<xref ref-type="bibr" rid="B60">Ghatak and Reza, 2007</xref>), false-eye leafhopper (<italic>Empoasca vitis</italic>) (<xref ref-type="bibr" rid="B55">Feng et&#xa0;al., 2004</xref>), tea weevil (<italic>Myllocerinus aurolineatus</italic>) (<xref ref-type="bibr" rid="B128">Pandey et&#xa0;al., 2021a</xref>), wood-eating tea termite (<italic>Microtermes obesi</italic>) (<xref ref-type="bibr" rid="B155">Singha et&#xa0;al., 2011</xref>), and tea mosquito bug (<italic>Helopeltis theivora</italic>) (<xref ref-type="bibr" rid="B47">Deka et&#xa0;al., 2021</xref>). Additionally, a study conducted in Japan demonstrated that a concentration of 1&#xd7;10<sup>7</sup> conidia/ml of <italic>Paecilomyces cinnamomeus</italic> led to a 90% infection rate of whiteflies (<italic>Aleurocanthus camphalus</italic>), which was significantly higher than other fungal insecticides available on the market (<xref ref-type="bibr" rid="B141">Saito et&#xa0;al., 2012</xref>). The spore suspension of <italic>M.anisopliae</italic> can achieve a mortality rate of 78% in <italic>O.coffeae</italic> (<xref ref-type="bibr" rid="B46">Deka et&#xa0;al., 2022a</xref>). However, most entomopathogenic fungi have poor compatibility with chemical pesticides (<xref ref-type="bibr" rid="B93">Joshi et&#xa0;al., 2018</xref>), while rainfall can promote the extensive growth of these pathogens in insects.</p>
<p>Insect viruses are classified into six major categories: nuclear polyhedrosis viruses (NPV), granulosis viruses (GV), entomopoxviruses, iridoviruses, ascoviruses, and picornaviruses. As pathogenic natural enemies, these viruses exhibit a high degree of specificity towards their target pests (<xref ref-type="bibr" rid="B157">Sood et&#xa0;al., 2019</xref>). They infect hosts by penetrating the body, replicating and producing specific proteins that disrupt host cells, ultimately causing insect mortality (<xref ref-type="bibr" rid="B132">Payne, 1982</xref>).In the 1990s, Kagoshima Prefecture in Japan used a mixture of GV for the biological control of pests <italic>Homona magnanima</italic> and <italic>Adoxophyes</italic> sp., achieving pest mortality rates of 60-75% (<xref ref-type="bibr" rid="B147">Sato et&#xa0;al., 1986</xref>). To date, 82 viruses associated with tea plant insects have been identified and reported in China. Among these, the Ectropis obliqua nuclear polyhedrosis virus (EcobNPV) and Euproctis pseudoconspersa nuclear polyhedrosis virus (EpNPV) have been registered as biopesticides in China and commercialized (<xref ref-type="bibr" rid="B194">Ye et&#xa0;al., 2014</xref>). However, viral biopesticides are currently used sparingly in tea plantations, primarily due to the narrow host ranges. Moreover, the term &#x201c;virus&#x201d; may negatively impact consumer and farmer perceptions.</p>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Pathogen antagonistic microorganisms</title>
<p>In tea plantations, where fungal pathogens are the primary cause of diseases, research has predominantly focused on fungal antagonistic microorganisms. Antagonistic microorganisms inhibit pathogenic growth through mechanisms such as competition, siderophore production, antibiotic secretion, and quorum sensing (<xref ref-type="bibr" rid="B56">Fenta et&#xa0;al., 2023</xref>), with their effects often being complex and multifaceted. Some plant growth-promoting rhizobacteria (PGPR) not only exhibit growth-promoting characteristics but also possess antibacterial, insecticidal, and plant resistance-inducing properties (<xref ref-type="bibr" rid="B95">Khoso et&#xa0;al., 2024</xref>). In this context, they are discussed as MBCAs. For instance, <italic>Serratia marcescens</italic> ETR17, isolated from the rhizosphere of tea plants, demonstrated <italic>in vitro</italic> antagonistic activity against nine tea plant pathogens (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>). This antagonism was primarily achieved through the secretion of various hydrolytic enzymes (chitinase, protease, lipase, cellulase) and antibiotics (pyrrolnitrin and prodigiosin). Additionally, ETR17 also produced the plant hormone indole-3-acetic acid (IAA) and siderophore. This suggests that MBCAs may simultaneously play a role in both biocontrol and improving the quality of tea.</p>
<p>
<italic>Bacillus</italic> species are known for their rapid growth, production of various antimicrobial metabolites and enzymes, and widespread application in plant disease management. Yuan et&#xa0;al (<xref ref-type="bibr" rid="B71">He et&#xa0;al., 2024</xref>). isolated <italic>Bacillus velezensis</italic> CSUFT-BV4 from healthy oil tea (<italic>Camellia oleifera</italic>) leaves, which exhibited up to 73.2% inhibition against five pathogens causing tea oil anthracnose. Among the Actinobacteria members, <italic>Streptomyces</italic> are recognized for their abilities to produce antifungal, insecticidal, and growth-promoting metabolites (<xref ref-type="bibr" rid="B23">Borah et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B43">Das et&#xa0;al., 2024</xref>). Marimuthu et&#xa0;al (<xref ref-type="bibr" rid="B119">Marimuthu et&#xa0;al., 2020</xref>). identified <italic>Streptomyces</italic> sp. SLR03 from river soil samples, which demonstrated effective antagonistic activity against the tea pathogen <italic>Pestalotiopsis theae</italic>. Studies have demonstrated that internal control mechanisms are more effective than external applications, highlighting endophytes as a valuable source of biocontrol agents. Thoudam et&#xa0;al (<xref ref-type="bibr" rid="B165">Thoudam and Dutta, 2012</xref>). evaluated the efficacy of several epiphytic fungi on tea plants for controlling <italic>Corticium theae</italic> Bernard, which causes black rot. Their findings indicated that <italic>Aspergillus niger</italic> exhibited the most effective inhibition, followed by <italic>Trichoderma atroviride</italic> and <italic>Trichoderma cithnoviride</italic>.</p>
<p>
<italic>Trichoderma</italic> species are considered among the most promising antagonistic fungi (<xref ref-type="bibr" rid="B164">Thambugala et&#xa0;al., 2020</xref>). Research has demonstrated that <italic>T.atroviride</italic>, <italic>T. asperellum</italic>, and <italic>T. harzianum</italic> effectively control the wilt pathogen <italic>Fusarium solani</italic>, with inhibition rates ranging from 64.6% to 71.7%. Additionally, these fungi significantly promote the development of new shoots in tea plants (<xref ref-type="bibr" rid="B99">Kumhar et&#xa0;al., 2020</xref>). Kolandasamy et&#xa0;al (<xref ref-type="bibr" rid="B97">Kolandasamy et&#xa0;al., 2023</xref>). reported that <italic>Bacillus subtilis VBS3</italic> and <italic>Trichoderma viride</italic> VTV7, isolated from tea rhizospheres, effectively inhibited the mycelial growth and spore germination of <italic>Phomopsis theae</italic> by producing high levels of chitinase and &#x3b2;-1,3-glucanase. Shang et&#xa0;al (<xref ref-type="bibr" rid="B150">Shang et&#xa0;al., 2020</xref>). found that <italic>T. asperellum</italic> TC01 significantly reduced the severity of tea anthracnose caused by <italic>Colletotrichum gloeosporioides</italic>, with a reduction rate of 58.37%. Pandey et&#xa0;al (<xref ref-type="bibr" rid="B129">Pandey et&#xa0;al., 2022</xref>, <xref ref-type="bibr" rid="B130">2023</xref>) observed that the strain <italic>Trichoderma reesei</italic> TRPATH01 exhibited antagonistic activities of 81.3% and 82.6% against the pathogens <italic>Pseudopestalotiopsis theae</italic> and <italic>F.solani</italic>, respectively on tea plants, through the production of inhibitory metabolites. Furthermore, Avascular Mycorrhizal Fungi (AMF) can also exhibit antagonistic activity. <italic>Rhizophagus intraradices</italic> BGC JX04B were able to reduce lesions caused by <italic>Colletotrichum camelliae</italic> in tea plants by 35.29% (<xref ref-type="bibr" rid="B37">Chen et&#xa0;al., 2022</xref>).</p>
<p>Fungal viruses have also shown potential in managing fungal diseases in tea plantations. For instance, Pestalotiopsis theae chrysovirus-1 (PtCV1), a fungal virus isolated from the tea pathogen <italic>P.theae</italic>, belongs to the family Chrysoviridae and the genus Alphachrysovirus. This virus significantly reduces the growth rate and virulence of its host fungus, effectively converting it into a non-pathogenic endophyte on tea leaves (<xref ref-type="bibr" rid="B211">Zhou et&#xa0;al., 2021</xref>). Furthermore, research indicates that plants can participate in the spread of fungal viruses (<xref ref-type="bibr" rid="B67">Hai et&#xa0;al., 2024</xref>). For example, after infection with <italic>Sclerotinia sclerotiorum</italic>, the concentration of proline in the plant significantly increases. This rise in proline weakens the fungus&#x2019;s non-self-recognition response, thereby facilitating the spread of fungal viruses within the plant.</p>
<p>Despite the significant success of MBCAs in managing pests and diseases, their effectiveness still falls short compared to some chemical formulations. The efficacy of MBCAs in field conditions largely depends on factors such as their intrinsic activity, interactions with the natural microbiome, colonization ability within the ecosystem, and environmental adaptability (<xref ref-type="bibr" rid="B51">do Nascimento et&#xa0;al., 2022</xref>). Combining MBCAs with chemical treatments may offer effective pest and disease control while reducing the reliance on chemical agents (<xref ref-type="bibr" rid="B85">Jeyaraman and Robert, 2017</xref>). Additionally, the development of synthetic metal nanoparticles with biological activity represents an emerging and promising direction (<xref ref-type="bibr" rid="B124">Mythili Gnanamangai et&#xa0;al., 2017</xref>). However, it is essential to consider the broader ecological impacts of introducing exogenous microorganisms into tea plantations. Beyond their role in controlling pests and pathogens, studies have shown that some MBCAs can promote tea plant growth and enhance tea quality (<xref ref-type="bibr" rid="B50">Dhar Purkayastha et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B17">Bhattacharyya et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B99">Kumhar et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B20">Bora et&#xa0;al., 2022a</xref>; <xref ref-type="bibr" rid="B129">Pandey et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B71">He et&#xa0;al., 2024</xref>). Despite these findings, the underlying mechanisms remain largely unexplored. It is hypothesized that these effects may result from the complex interactions between the microorganisms and the tea plants. Therefore, further research is needed to elucidate the impact of MBCAs on the microecological dynamics of tea plantations and the metabolic processes of tea plants, ensuring a comprehensive understanding of their potential benefits and limitations.</p>
</sec>
</sec>
<sec id="s3">
<label>3</label>
<title>Comprehensive impact of microbial biocontrol agents in tea plantations</title>
<sec id="s3_1">
<label>3.1</label>
<title>Colonization efficacy of microbial biocontrol agents in tea plantations</title>
<p>Tea grower generally expect MBCAs to fulfill two key criteria: effective suppression of pathogens or pests and sustained survival in the environment. When conditions are favorable, MBCAs can be released as inoculants and remain in the microecosystem to prevent pest outbreaks or inhibit pathogen proliferation (<xref ref-type="bibr" rid="B121">McGuire and Northfield, 2020</xref>). One example is that MBCAs products containing <italic>Pseudomonas fluorescens</italic> in the U.S. often failed because these non-sporulating bacteria cannot survive long-term in natural environments (<xref ref-type="bibr" rid="B41">Choudhary and Johri, 2009</xref>). But studies have shown that sporulating Bt also exhibits poor colonization ability on plant leaves (<xref ref-type="bibr" rid="B133">Pedersen et al., 1995</xref>), likely due to its limited competitive ability in foliar environments (<xref ref-type="bibr" rid="B117">Maduell et&#xa0;al., 2008</xref>). The colonization of MBCAs on host plants is influenced by multiple factors, including inoculation methods, microbial species, crop types, growth conditions, and carriers (<xref ref-type="bibr" rid="B8">Bamisile et&#xa0;al., 2018</xref>), cannot be attributed to a single factor. Research on the colonization efficacy of microbial agents on tea plants is crucial for advancing microbial control strategies.</p>
<p>Nutritional supplements may aid in enhancing the survival of MBCAs under adverse conditions (<xref ref-type="bibr" rid="B109">Lin et&#xa0;al., 2023a</xref>). Certain strains adapted to tea plantation environments, such as <italic>Streptomyces sannanensis</italic>, are particularly suited for tea cultivation due to their ability to thrive in acidic soils (<xref ref-type="bibr" rid="B62">Gnanamangai and Ponmurugan, 2012</xref>). Furthermore, due to the saprophytic nature of <italic>Trichoderma harzianum</italic>, <italic>Gliocladium virens</italic>, <italic>P.fluorescens</italic>, and <italic>Trichoderma atroviride</italic>, they can occupy advantageous ecological niches in both soil and tea leaves, thereby altering the ecological functions of microbial communities (<xref ref-type="bibr" rid="B145">Sanjay et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B118">Manjukarunambika et&#xa0;al., 2013</xref>). These biocontrol agents also form biofilms and produce various cell wall-degrading enzymes upon colonizing host plants, thereby serving as effective barriers against pathogen invasion.</p>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Impact on tea plant growth and tea quality</title>
<p>The ultimate goal of employing various management strategies in tea plantations is to enhance tea quality and mitigate adverse factors affecting. Key metabolic compounds in tea are critical indicators of quality. For instance, caffeine and catechins jointly influence the color and bitterness of tea. Non-protein amino acids, particularly theanine, are closely associated with the freshness and sweetness of tea. Volatile compounds such as linalool and cis-3-hexenol determine the aroma of tea (<xref ref-type="bibr" rid="B203">Zhang et&#xa0;al., 2020b</xref>). Stress from pests and pathogens, along with various exogenous factors, can affect the metabolic responses of tea plants, thereby altering the types and concentrations of metabolites in the tea leaves (<xref ref-type="bibr" rid="B105">Liao et&#xa0;al., 2019</xref>). Some MBCAs, in addition to their insecticidal and antimicrobial properties, have been shown to improve tea quality (<xref ref-type="bibr" rid="B2">Afridi et&#xa0;al., 2024</xref>). For example, growth-promoting effects associated with endophytic colonization by <italic>B.bassiana</italic> (<xref ref-type="bibr" rid="B142">S&#xe1;nchez-Rodr&#xed;guez et&#xa0;al., 2018</xref>) and <italic>Metarhizium</italic> species (<xref ref-type="bibr" rid="B4">Ahmad et&#xa0;al., 2020</xref>) have been observed in various plants. The growth-promoting mechanisms of MBCAs encompass the synthesis of phytohormones and siderophore, phosphate solubilization, potassium release, and nitrogen fixation (<xref ref-type="bibr" rid="B11">Barelli et&#xa0;al., 2020</xref>).</p>
<p>In tea plants, the antagonistic microorganism <italic>Streptomyces sannanensis</italic> has been shown to significantly improve both tea yield and quality parameters (<xref ref-type="bibr" rid="B62">Gnanamangai and Ponmurugan, 2012</xref>). Similarly, <italic>Ochrobactrum anthropi</italic> BMO&#x2010;111 has been reported to significantly increase the levels of chlorophyll, polyphenols, and catechins in tea buds. However, the observed increase in these indicators may be a result of the plant&#x2019;s recovery from pathogen infection (<xref ref-type="bibr" rid="B158">Sowndhararajan et&#xa0;al., 2013</xref>). In another study, the rhizosphere strain <italic>O. anthropi</italic> TRS-2 demonstrated phosphate solubilization, iron carrier production, and IAA synthesis <italic>in vitro</italic>, confirming its plant growth-promoting mechanisms (<xref ref-type="bibr" rid="B34">Chakraborty et&#xa0;al., 2009</xref>). Huang et&#xa0;al (<xref ref-type="bibr" rid="B76">Huang et&#xa0;al., 2022</xref>). found that foliar application of <italic>Bacillus amyloliquefaciens</italic> to tea plants resulted in a decrease in the ratio of tea polyphenols to amino acids (TP/AA), catechin, and caffeine content, while the theanine content increased, with catechin reduction being associated with the biosynthesis pathway of flavonoids. Moreover, treatments with <italic>T.asperellum</italic> TC01 (<xref ref-type="bibr" rid="B150">Shang et&#xa0;al., 2020</xref>) and <italic>T.reesei</italic> TRPATH01 (<xref ref-type="bibr" rid="B130">Pandey et&#xa0;al., 2023</xref>) significantly enhanced parameters such as shoot height, stem diameter, weight of buds and roots in tea plants. These studies indicate that exogenous MBCAs may have a positive impact on tea quality. However, is this impact always beneficial? Although no direct reports have been found indicating adverse effects of MBCAs on tea plant growth, similar outcomes have been observed in other crops. For example, <italic>Pseudomonas chlororaphis</italic> IDV1 and <italic>Pseudomonas putida</italic> RA2, which antagonize the tomato pathogen <italic>Ralstonia solanacearum</italic>, exhibited good survival in maize rhizospheres but caused slight inhibition of maize growth (<xref ref-type="bibr" rid="B98">Kozdr&#xf3;j et&#xa0;al., 2004</xref>). Whether such effects arise from changes in the plant&#x2019;s microecological structure, direct interference with plant metabolic processes, or other biological factors remains unclear.</p>
</sec>
<sec id="s3_3">
<label>3.3</label>
<title>Effects on non-target organisms and safety evaluation</title>
<p>As biological control agent use expands, it is essential to assess their potential impacts on non-target organisms in tea plantations. Non-target organisms, including non-tea plants, soil microbes, and wildlife. These organisms play significant roles within ecosystems, and disturbances to them could lead to ecological imbalances. Research has identified harmful effects of certain biocontrol agents on non-target species. For example, <italic>B.bassiana</italic> has been shown to have detrimental effects on some natural enemies (<xref ref-type="bibr" rid="B103">Li et&#xa0;al., 2024</xref>), while Bt exhibits toxicity to bees (<xref ref-type="bibr" rid="B24">Borges et&#xa0;al., 2021</xref>) and silkworms (<xref ref-type="bibr" rid="B143">Sandeep Kumar et&#xa0;al., 2016</xref>), which limits its application in sericulture countries such as India (<xref ref-type="bibr" rid="B44">Dashora et&#xa0;al., 2017</xref>). However, Bt proteins, particularly the ICPs, are highly specific and fully biodegradable, with no observed risk of toxic accumulation in the environment (<xref ref-type="bibr" rid="B26">Brar et&#xa0;al., 2007</xref>). Additionally, studies have indicated that injecting Bt crystal proteins into mice does not produce toxic effects (<xref ref-type="bibr" rid="B137">Rom&#xe1;n Calder&#xf3;n et&#xa0;al., 2007</xref>). Nevertheless, another study found that Bt inoculation might inhibit the root colonization of AMF by releasing suppressive compounds (<xref ref-type="bibr" rid="B57">Ferreira et&#xa0;al., 2003</xref>).</p>
<p>Plant-derived insecticides such as sophoridine and neem extract have not shown significant impacts on the populations of ladybugs, spiders, or parasitic wasps in tea plantations (<xref ref-type="bibr" rid="B166">Tian et&#xa0;al., 2020</xref>). However, neem extract has demonstrated adverse effects on the rhizosphere microbial communities of leguminous plants, resembling the effects of chemical pesticides (<xref ref-type="bibr" rid="B151">Singh et&#xa0;al., 2015a</xref>, <xref ref-type="bibr" rid="B153">2015b</xref>). Notably, research has shown that bacterial inoculants can mitigate such negative impacts (<xref ref-type="bibr" rid="B154">Singh et&#xa0;al., 2022</xref>). Additionally, some Gram-negative bacteria used in biological control, such as <italic>O. anthropi</italic> strains, have potential as human pathogens. However, in murine models, the pathogenicity of <italic>O. anthropi</italic> strain BMO-111 was not observed, even with high inoculum concentrations (0.5 ml of 1 &#xd7; 10<sup>7</sup> CFU ml<sup>&#x2212;1</sup>) orally administered to mice (<xref ref-type="bibr" rid="B158">Sowndhararajan et&#xa0;al., 2013</xref>).</p>
</sec>
</sec>
<sec id="s4">
<label>4</label>
<title>Impact of microbial biocontrol methods on tea plant microbial communities</title>
<p>Microbial communities associated with tea plants can be broadly categorized into three main types: phyllosphere, rhizosphere, and endophytic microorganisms. Each of these groups plays a unique role in the plant&#x2019;s microecology and overall health. Under-standing their characteristics and interactions is crucial for effectively applying microbial biocontrol methods to improve tea plant resilience and productivity.</p>
<sec id="s4_1">
<label>4.1</label>
<title>Phyllosphere microorganisms</title>
<p>Phyllosphere microorganisms refer to the microbial communities associated with the aerial parts of plants (<xref ref-type="bibr" rid="B189">Xu et&#xa0;al., 2022a</xref>). The phyllosphere functions as an open system, making it susceptible to external factors such as ultraviolet radiation, air pollution, and microbial inoculation. Plant genotypes play a key role, shaping tissue structure and secondary metabolites (<xref ref-type="bibr" rid="B126">Ohler et&#xa0;al., 2022</xref>). In tea plants, the phyllosphere microbial community predominantly consists of <italic>Proteobacteria</italic>, <italic>Actinobacteria</italic>, <italic>Bacteroidetes</italic>, and <italic>Firmicutes</italic> at the phylum level. At the genus level, the core microbial taxa include bacteria such as <italic>Herbaspirillum</italic>, <italic>Massilia</italic>, <italic>Methylobacterium</italic>, <italic>Pantoea</italic>, <italic>Pseudomonas</italic>, and <italic>Sphingomonas</italic>. The diversity of phyllosphere fungi is generally lower than that of bacteria. These fungi can inhabit the phyllosphere in either epiphytic or endophytic forms, with predominant taxa including <italic>Basidiomycota</italic>, <italic>Ascomycota</italic>, and <italic>Mortierella</italic> (<xref ref-type="bibr" rid="B187">Xu et&#xa0;al., 2023b</xref>). Fungi and bacteria in the phyllosphere can collaborate in the metabolic processes of tea plants, with this interaction being more pronounced in young leaves (<xref ref-type="bibr" rid="B108">Lin et&#xa0;al., 2022</xref>).</p>
<p>The assembly of phyllosphere microbial communities and their interactions with host metabolites are crucial for the health of tea plants. Xu et&#xa0;al (<xref ref-type="bibr" rid="B183">Xu et&#xa0;al., 2022b</xref>). demonstrated that the phyllosphere microbiota varies with the metabolic products of tea leaves at different developmental stages, although a stable core microbial community exhibits antagonistic effects against various pathogens (<xref ref-type="bibr" rid="B183">Xu et&#xa0;al., 2022b</xref>). Microorganisms such as <italic>Sphingomonas</italic>, <italic>Herbaspirillum</italic>, and <italic>Massilia</italic> can migrate from the soil to the leaves and maintain phyllosphere homeostasis (<xref ref-type="bibr" rid="B187">Xu et&#xa0;al., 2023b</xref>). Additionally, Bt is also a common component of many plant phyllosphere microbiota, where it can interact with and kill herbivorous insect larvae (<xref ref-type="bibr" rid="B168">Uribe et&#xa0;al., 2003</xref>; <xref ref-type="bibr" rid="B42">Collier et&#xa0;al., 2005</xref>). Key drivers of microbial community assembly in tea plants include metabolites like caffeine and epigallocatechin gallate (<xref ref-type="bibr" rid="B183">Xu et&#xa0;al., 2022b</xref>), suggesting that tea plants may recruit beneficial microorganisms by secreting specific metabolites under biotic stress. Similarly, Xie et&#xa0;al (<xref ref-type="bibr" rid="B180">Xie et&#xa0;al., 2022</xref>). found that tea plants influence rhizosphere bacterial diversity, community structure, and nitrogen cycling-related gene abundance through the secretion of L-theanine into the rhizosphere. This indicates the presence of complex interactions among insects, microorganisms, and tea plants.</p>
<p>The use of chemical agents in agriculture can disrupt phyllosphere microbiota (<xref ref-type="bibr" rid="B36">Chen et&#xa0;al., 2021</xref>). For example, a study on wheat found that while the herbicide S-metolachlor did not significantly affect plant physiology, it reduced the diversity of the phyllosphere microbiota, indicating that microbial communities are sensitive indicators of short-term plant stress (<xref ref-type="bibr" rid="B186">Xu et&#xa0;al., 2020</xref>). MBCAs have shown significant impacts on the microbiota of various crops (<xref ref-type="bibr" rid="B202">Zhang et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B161">Sylla et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B134">Perazzolli et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B174">Wang et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B136">Qin et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B68">Hao et&#xa0;al., 2021</xref>), though some studies have reached the opposite conclusion (<xref ref-type="bibr" rid="B175">Wei et&#xa0;al., 2016</xref>). For instance, Bt does not significantly alter the bacterial community on the leaves of cabbage (<italic>Brassica oleracea</italic>) (<xref ref-type="bibr" rid="B140">Russell et&#xa0;al., 1999</xref>) or the phyllosphere bacterial community of <italic>Oryza sativa</italic> (<xref ref-type="bibr" rid="B174">Wang et&#xa0;al., 2014</xref>), likely due to Bt&#x2019;s weak competitive ability (<xref ref-type="bibr" rid="B117">Maduell et&#xa0;al., 2008</xref>). Evidence also suggests that combined microbial inoculants have a more pronounced effect on microbial community structure compared to single-agent applications (<xref ref-type="bibr" rid="B184">Xu and Jeger, 2013</xref>), and repeated application of MBCAs may increase opportunities for establishing active populations (<xref ref-type="bibr" rid="B175">Wei et&#xa0;al., 2016</xref>). However, microbial combinations can lead to competitive or antagonistic relationships, necessitating careful consideration. While research on MBCAs in tea plant phyllosphere microbiota is limited, studies on other crops indicate that MBCAs may influence tea plants. Further research is needed to understand the specific mechanisms by which MBCAs affect tea plant phyllosphere microbiota.</p>
</sec>
<sec id="s4_2">
<label>4.2</label>
<title>Rhizosphere microorganisms</title>
<p>In the rhizosphere of tea plants, AMF and various other microorganisms play key roles in processes such as phosphate solubilization, nitrogen fixation, iron chelation, stress tolerance, and auxin production (<xref ref-type="bibr" rid="B35">Chen et&#xa0;al., 2023</xref>). In tea plantations, soil fungi predominantly belong to <italic>Ascomycota</italic>, <italic>Mortierellomycota</italic>, and <italic>Basidiomycota</italic>, while the dominant bacterial phyla are <italic>Acidobacteria</italic>, <italic>Actinobacteria</italic>, and <italic>Proteobacteria</italic> (<xref ref-type="bibr" rid="B88">Jibola-Shittu et&#xa0;al., 2024</xref>). Research suggests that more complex soil ecological networks may contribute to the suppression of tobacco wilt disease (<xref ref-type="bibr" rid="B191">Yang et&#xa0;al., 2017</xref>). Additionally, rhizosphere bacteria from tea plantations, such as <italic>Burkholderia</italic> sp. AULS-B3, has been found to both metabolize the pesticide endosulfan and promote tea plant growth (<xref ref-type="bibr" rid="B79">Huidrom and Sharma, 2024</xref>).</p>
<p>The stability of tea plant rhizosphere microbial communities is shaped by agronomic practices (<xref ref-type="bibr" rid="B215">Zou et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B205">Zhang et&#xa0;al., 2023</xref>). Lin et&#xa0;al (<xref ref-type="bibr" rid="B162">Tan et&#xa0;al., 2019</xref>). observed that organic tea plantations (OTP) exhibit significantly higher alpha diversity and Chao1 indices than conventional tea plantations (CTP) (<xref ref-type="bibr" rid="B144">Sang and Kim, 2012</xref>). Exogenous microbial applications can also influence native rhizosphere microbiome, though the effects may be ambiguous. For instance, lower concentrations of <italic>Beauveria bassiana</italic> spore suspensions improved paddy soil yields by affecting microbial community structure and enzyme activity (<xref ref-type="bibr" rid="B52">Du et&#xa0;al., 2013</xref>). In soybeans (<italic>Glycine max</italic>), Bt did not alter cultivable heterotrophic bacteria or saprophytic fungi in the rhizosphere (<xref ref-type="bibr" rid="B57">Ferreira et&#xa0;al., 2003</xref>). Similarly, applying <italic>Pseudomonas fluorescens</italic> DR54 to barley (<italic>Hordeum vulgare</italic>) temporarily shifted the rhizosphere microbiome (<xref ref-type="bibr" rid="B91">Johansen and Olsson, 2005</xref>) due to competition with native microbes, causing DR54 decline. This phenomenon explains why most MBCAs rapidly decline in number after soil introduction, and microbial communities tend to recover quickly.</p>
<p>The relationship between rhizosphere microorganisms and their host plants is highly intricate. For instance, the soil-dwelling insect-pathogenic fungus <italic>Metarhizium robertsii</italic> possesses two adhesin genes: MAD1, which facilitates attachment to the insect cuticle, and MAD2, which aids in adhesion to plants, highlighting its association with plant hosts (<xref ref-type="bibr" rid="B146">Sasan and Bidochka, 2012</xref>). Similar to the phyllosphere, plant roots release signaling molecules into the soil under stress, recruiting beneficial microorganisms to alleviate various environmental pressures. These signaling molecules are likely plant hormones or other secondary metabolites. For example, research by Berendsen et&#xa0;al (<xref ref-type="bibr" rid="B14">Berendsen et&#xa0;al., 2018</xref>). showed that plants can attract beneficial microorganisms by regulating hormone levels when infected by pathogens. Studies suggest that pathogen-infected roots secrete more amino acids, nucleic acids, and long-chain organic acids, which alter the root microbiome and enhance disease resistance (<xref ref-type="bibr" rid="B197">Yuan et&#xa0;al., 2018</xref>). The application of MBCAs can also change plant hormone levels, indicating that these microbial shifts are the result of multiple interacting factors, often regulated by the plant itself. This underscores the mutualistic relationship between plants and microorganisms, suggesting that selecting beneficial MBCAs could promote an ideal symbiosis.</p>
</sec>
<sec id="s4_3">
<label>4.3</label>
<title>Endophytic microorganisms</title>
<p>Endophytic microorganisms, which reside within plant tissues, have a particularly close relationship with their host plants (<xref ref-type="bibr" rid="B170">Wang and Cernava, 2020</xref>). Research highlights their critical role in promoting plant growth and health (<xref ref-type="bibr" rid="B13">Bastias et&#xa0;al., 2017</xref>). For instance, endophytic bacteria can enhance plant resistance to herbivorous insects through jasmonic acid (JA)-mediated defense pathways (<xref ref-type="bibr" rid="B13">Bastias et&#xa0;al., 2017</xref>). Most isolated endophytes, primarily from the <italic>Bacillus</italic> genus, exhibit plant growth-promoting abilities. However, the evaluation of MBCAs often neglects the impact on endophytes (<xref ref-type="bibr" rid="B94">Kabir et&#xa0;al., 2023</xref>). This omission may be due to the cryptic endophytic environment, the diversity and heterogeneous distribution of endophytes, which pose significant research challenges. Because endophytes are frequently grouped together with phyllosphere microorganisms in studies. While this simplifies experimental design, it overlooks the unique functions of endophytes. Future research should emphasize the interactions between tea plant microbiota and MBCAs, particularly in diverse ecological systems and management practices. Understanding how these interactions alter microbial communities is essential for developing beneficial microecologies that enhance tea plant resistance and quality.</p>
</sec>
</sec>
<sec id="s5">
<label>5</label>
<title>Insects, microorganisms, and tea plant metabolism</title>
<p>The intricate interplay between insects, microorganisms, and tea plant metabolism significantly influences the overall health and productivity of tea plants. Understanding tea plant metabolic responses to pest and disease stress is crucial for developing effective management strategies. Additionally, MBCAs not only control pests and diseases but also influence tea plant metabolism, enhancing resilience and quality. This section examines into the response mechanisms of tea plant metabolism under stress and explores the role of MBCAs in mediating these metabolic processes (<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>The respective impacts of MBCAs and biological stress factors on the metabolic mechanisms of tea plants. HAMPs, herbivore-associated molecular patterns; PAMPs, pathogen-associated molecular patterns; MAMPs, microbe-associated molecular patterns; SAR, systemic acquired resistance; ISR, induced systemic resistance; KPIs, proteinase inhibitors; ROS, reactive oxygen species; MYB, MYB transcription factors; VOCs, volatile organic compounds.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpls-15-1492424-g002.tif"/>
</fig>
<sec id="s5_1">
<label>5.1</label>
<title>Response mechanisms of tea plant metabolism under pest and disease stress</title>
<p>Tea plants have evolved complex metabolic pathways and defense mechanisms. Pathogen attacks trigger systemic acquired resistance (SAR) in uninfected tissues, providing broad-spectrum resistance (<xref ref-type="bibr" rid="B84">Jeyaraj et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B72">Hilleary and Gilroy, 2018</xref>; <xref ref-type="bibr" rid="B125">Naskar et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B204">Zhang et&#xa0;al., 2024</xref>). Local responses triggered by herbivore-associated molecular patterns (HAMPs) and pathogen-associated molecular patterns (PAMPs) are rapid and intense, while systemic responses involve secondary metabolites, proteinase inhibitors (KPIs), reactive oxygen species (ROS), and plant hormones to combat further assaults (<xref ref-type="bibr" rid="B58">Fu and Dong, 2013</xref>; <xref ref-type="bibr" rid="B125">Naskar et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B92">Jomova et&#xa0;al., 2024</xref>). Under stress from pests and pathogens, tea plants also exhibit significant changes in primary metabolic pathways. Primary metabolites such as carbohydrates, amino acids, and organic acids are not only fundamental to tea plant growth and development but also play crucial roles in its defense mechanisms (<xref ref-type="bibr" rid="B212">Zhou et&#xa0;al., 2015</xref>).</p>
<p>For example, tea looper (<italic>Ectropis obliqua</italic>) feeding induces systemic carbon and nitrogen redistribution to bolster secondary metabolism for defense (<xref ref-type="bibr" rid="B77">Huang et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B192">Yang et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B102">Li et&#xa0;al., 2020</xref>). During this process, L-theanine is primarily synthesized by CsTSI in the roots and transported through the vascular system to new tea shoots (<xref ref-type="bibr" rid="B107">Lin et&#xa0;al., 2023b</xref>), while caffeine (1,3,7-trimethylxanthine) is predominantly synthesized in chloroplasts (<xref ref-type="bibr" rid="B179">Xia et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B106">Liao et&#xa0;al., 2022</xref>). This coordinated metabolic reorganization helps tea plants maintain a balance between growth and defense when facing external pressures. RNA sequencing (RNA-Seq) analysis has revealed 1,859 differentially expressed genes (949 upregulated and 910 downregulated) in tea plants subjected to <italic>E. oblique</italic> infestation compared to controls. These genes are involved in signal transduction, insect defense response transcription factors, phenylpropanoid pathways, herbivory-induced plant volatiles (HIPVs), and caffeine biosynthesis (<xref ref-type="bibr" rid="B173">Wang et&#xa0;al., 2016b</xref>). Similarly, <italic>Exobasidium vexans</italic> infection revealed 149 defense-related genes in resistant tea genotypes, including defense-related enzymes, resistance genes, multidrug-resistant transporters, transcription factors, retrotransposons, metacaspases, and chaperones (<xref ref-type="bibr" rid="B83">Jayaswall et&#xa0;al., 2016</xref>). Beyond local responses, tea plants also activate defense-related genes in adjacent leaves through signaling mechanisms (<xref ref-type="bibr" rid="B213">Zhou et&#xa0;al., 2020</xref>).</p>
<p>Plant hormones play a crucial regulatory role in the defense responses of tea plants (<xref ref-type="bibr" rid="B105">Liao et&#xa0;al., 2019</xref>, <xref ref-type="bibr" rid="B106">2022</xref>; <xref ref-type="bibr" rid="B192">Yang et&#xa0;al., 2019</xref>). Jasmonic acid (JA) and salicylic acid (SA) are key signaling molecules that activate defense pathways (<xref ref-type="bibr" rid="B206">Zhang et&#xa0;al., 2020a</xref>; <xref ref-type="bibr" rid="B73">Hou and Tsuda, 2022</xref>), JA is primarily involved in tea plant responses to folivorous insects, while SA predominantly mediates immune responses to microbial pathogens (<xref ref-type="bibr" rid="B214">Zhu et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B75">Hu et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B159">Sultana et&#xa0;al., 2024</xref>). Studies have shown that JA and SA play important roles in shaping the root microbiome (<xref ref-type="bibr" rid="B101">Lebeis et&#xa0;al., 2015</xref>). Additionally, other plant hormones such as ethylene (ET), abscisic acid (ABA), auxin (indole-3-acetic acid, IAA), cytokinins (CTK), and gibberellins (GA) are required to ensure proper coordination between growth and defense (<xref ref-type="bibr" rid="B19">Bigeard et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B193">Ye et&#xa0;al., 2021</xref>). Although JA and SA are generally considered antagonistic (<xref ref-type="bibr" rid="B87">Jiao et&#xa0;al., 2022</xref>), studies have shown that they can also act synergistically (<xref ref-type="bibr" rid="B111">Liu et&#xa0;al., 2016</xref>). For instance, attacks by both piercing-sucking insects like the tea green leafhopper (<italic>Empoasca onukii</italic>) and chewing insects like tea looper (<italic>Ectropis grisescens</italic>) lead to increased levels of both JA and SA (<xref ref-type="bibr" rid="B89">Jin et&#xa0;al., 2020</xref>). Notably, <italic>E. onukii</italic> attack also raises ABA levels, which may relate to the insect&#x2019;s mode of injury (<xref ref-type="bibr" rid="B105">Liao et&#xa0;al., 2019</xref>). Conversely, simulated attacks by piercing-sucking insects alone elevate JA and ABA levels in tea leaves, with no significant change in SA levels. This raises the question of whether SA variation might be related to insect salivary effectors or microbial interactions (<xref ref-type="bibr" rid="B185">Xu et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B156">Smets and Koskella, 2020</xref>). Furthermore, Zhao et&#xa0;al (<xref ref-type="bibr" rid="B208">Zhao et&#xa0;al., 2020b</xref>). found that invasion by <italic>E. onukii</italic> upregulated genes related to the biosynthesis of phenylpropanoids and flavonoids and induced the synthesis of cuticular waxes, leading to increased levels of C29 alkanes. Tea plants infected with <italic>Pseudopestalotiopsis camelliae-sinensis</italic> may enhance lignin content in young tea shoots through the CsmiR397a-CsLAC17 module, thereby reducing stem tenderness and increasing resistance to tea leaf spot disease (<xref ref-type="bibr" rid="B190">Yang et&#xa0;al., 2024</xref>). The dynamic adjustment of these metabolic pathways not only enhances tea plant survival but also impacts the flavor and aroma of the tea.</p>
<p>As previously discussed, characteristic metabolites in tea plants, such as terpenoids, phenolic compounds (flavonoids, anthocyanins, lignins, and tannins), and nitrogen-containing compounds (such as alkaloids and non-protein amino acids), not only protect the tea plant but also determine the overall flavor and health benefits of tea (<xref ref-type="bibr" rid="B72">Hilleary and Gilroy, 2018</xref>; <xref ref-type="bibr" rid="B196">Yu and Yang, 2020</xref>; <xref ref-type="bibr" rid="B210">Zhao et&#xa0;al., 2020a</xref>, <xref ref-type="bibr" rid="B209">2023b</xref>; <xref ref-type="bibr" rid="B201">Zeng et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B104">Li et&#xa0;al., 2022</xref>). It has been demonstrated that catechins and caffeine can inhibit pathogen growth <italic>in vitro</italic> (<xref ref-type="bibr" rid="B10">Bansal et&#xa0;al., 2012</xref>). For instance, infestations by <italic>E.oblique</italic> and <italic>Colletotrichum fructicola</italic> increase the biosynthesis of flavonoids and caffeine in tea leaves, accompanied by elevated expression of related synthesis genes (<xref ref-type="bibr" rid="B172">Wang et&#xa0;al., 2016a</xref>). Interestingly, certain <italic>Pseudomonas</italic> species in the gut microbiota of the coffee borer beetle (<italic>Hypothenemus hampei</italic>) use caffeine as their sole carbon and nitrogen source (<xref ref-type="bibr" rid="B31">Ceja-Navarro et&#xa0;al., 2015</xref>), suggesting that some insects may have evolved adaptive detoxification systems for caffeine, which could be relevant for research on tea plants as well. Additionally, changes in metabolite levels evidently influence microbial communities. For example, after infection with <italic>E.vexans</italic>, the dominant endophytic fungal community in tea plants shifted from <italic>Ascomycota</italic> to <italic>Basidiomycota</italic>, while the relative abundance of <italic>Actinobacteria</italic> in bacteria increased (<xref ref-type="bibr" rid="B29">Cao et&#xa0;al., 2023</xref>).</p>
<p>Tea plant volatile organic compounds (VOCs) play a dual role in both aromatic and defensive functions (<xref ref-type="bibr" rid="B200">Zeng et&#xa0;al., 2019b</xref>). They can repel pests (<xref ref-type="bibr" rid="B90">Jing et&#xa0;al., 2021</xref>), attract natural enemies (<xref ref-type="bibr" rid="B200">Zeng et&#xa0;al., 2019b</xref>), and trigger immune responses in neighboring plants (<xref ref-type="bibr" rid="B25">Bouwmeester et&#xa0;al., 2019</xref>). For instance, after feeding by <italic>E.oblique</italic>, tea plants release compounds such as S-linalool and &#x3b2;-ocimene, which significantly attract the parasitic wasp <italic>Parapanteles hyposidrae</italic> (<xref ref-type="bibr" rid="B112">Liu et&#xa0;al., 2024a</xref>). Due to the aromatic properties of VOCs, the impact of pest infestations on tea quality is not always negative. For example, feeding by the green leafhopper (<italic>Jacobiasca formosana</italic>) increases the release of (S)-linalool and geraniol, and induces the production of diene alcohol I. This process contributes to the Oriental Beauty Oolong tea, which is known for its distinctive aroma (<xref ref-type="bibr" rid="B40">Cho et&#xa0;al., 2007</xref>).</p>
<p>Overall, tea plants exhibit a sophisticated metabolic regulatory system in response to pest and pathogen pressures. These mechanisms encompass not only the accumulation of plant hormones and secondary metabolites but also the regulation of carbon and nitrogen metabolism, the generation and scavenging of reactive oxygen species, the release of volatile organic compounds, and systemic defense responses in adjacent leaves. These insights offer new possibilities for pest and disease management in tea cultivation. For example, exogenous application of JA and SA can enhance both the quantity and quality of volatile compounds (<xref ref-type="bibr" rid="B38">Chen et&#xa0;al., 2020</xref>). Additionally, inducing tea plant disease resistance genes through external agents may improve the plant&#x2019;s disease resistance (<xref ref-type="bibr" rid="B148">Senthilkumar et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B115">Lu et&#xa0;al., 2019</xref>). Future research could further elucidate the specific regulatory mechanisms of these metabolic pathways, potentially providing novel strategies for genetic improvement and integrated pest and disease management in tea cultivation.</p>
</sec>
<sec id="s5_2">
<label>5.2</label>
<title>Microbial biocontrol agents mediating tea plant metabolism</title>
<p>In tea plants, inoculation with weak pathogens or non-pathogenic microbial agents can trigger an enhanced resistance state known as induced systemic resistance (ISR) (<xref ref-type="bibr" rid="B135">Pieterse et&#xa0;al., 2014</xref>). Typically, plant immune responses are triggered by microbe-associated molecular patterns (MAMPs), leading to microbe-associated molecular pattern-triggered immunity (MTI). MTI functions by recognizing pathogen-associated molecular patterns and activating defense signaling pathways. However, this defense response often leads to a reallocation of resources, consequently inhibiting plant growth (<xref ref-type="bibr" rid="B150">Shang et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B116">Ma et&#xa0;al., 2021</xref>). Unlike MTI, ISR regulates the expression of defense genes through the jasmonic acid (JA) and ethylene signaling pathways, promoting the accumulation of defense metabolites and protecting distal tissues. While both MTI and ISR enhance disease resistance, ISR also has the potential to promote plant growth, providing additional growth advantages alongside conventional immune defenses via MTI (<xref ref-type="bibr" rid="B100">Kusajima et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B195">Yu et&#xa0;al., 2022</xref>). However, this advantage may come with potential trade-offs due to differences in resource allocation.</p>
<p>In studies conducted in India, the application of <italic>Pseudomonas fluorescens</italic> and <italic>Pseudomonas aeruginosa</italic> strains RRLJ 134 and RRLJ 04, respectively, has been shown to activate systemic resistance in tea plants against <italic>Fomes lamoensis</italic> and <italic>Ustulina zonata</italic> (<xref ref-type="bibr" rid="B122">Mishra et&#xa0;al., 2014</xref>). These treatments, along with antagonistic microorganisms <italic>Bacillus altitudinis</italic> GS-16 and <italic>T. reesei</italic> TRPATH01, significantly enhanced key defense enzyme activities in tea plants (<xref ref-type="bibr" rid="B129">Pandey et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B178">Wu et&#xa0;al., 2024b</xref>). Additionally, antagonistic fungi <italic>Trichoderma asperellum</italic> TC01 treatment activated the expression of genes associated with flavonoids, phenylpropanoids, jasmonic acid, and ethylene (<xref ref-type="bibr" rid="B150">Shang et&#xa0;al., 2020</xref>). Treatment with the AMF <italic>Rhizophagus intraradices</italic> BGC JX04B resulted in a significant increase in superoxide anion levels, as well as the activities of catalase and peroxidase in young tea seedlings. This response is likely mediated through pathways involved in plant hormone signaling, mitogen-activated protein kinase (MAPK) signaling, and phenylpropanoid biosynthesis (<xref ref-type="bibr" rid="B37">Chen et&#xa0;al., 2022</xref>).</p>
<p>In other crops, a method analogous to the use of &#x201c;inactivated vaccines&#x201d; in medicine involves the application of fungal pathogen <italic>Stemphylium lycopersici</italic> mycelial suspensions, which have been attenuated by infection with Stemphylium lycopersici Alternavirus 1 (SlAV1), to enhance plant resistance against virulent strains and convert pathogenic fungi into biocontrol agents (<xref ref-type="bibr" rid="B113">Liu et&#xa0;al., 2022</xref>). Overall, MBCAs have a significant impact on the metabolism of tea plants, with some changes in metabolic pathways resembling the plant&#x2019;s response to pathogen and pest stress. As shown in <xref ref-type="table" rid="T3">
<bold>Table&#xa0;3</bold>
</xref>, both stress and the application of MBCAs can enhance the resistance of tea plants.</p>
<table-wrap id="T3" position="float">
<label>Table&#xa0;3</label>
<caption>
<p>The impact of exogenous biological factors on tea tree metabolism.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center">Biological Factors</th>
<th valign="middle" align="center">The Impact on Tea Tree Metabolism</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="center">
<italic>Ectropis oblique</italic>
</td>
<td valign="middle" align="center">Signal transduction, Carbon and nitrogen resource allocation, Phenylpropanoid biosynthesis; Flavonoids and caffeine biosynthesis, Herbivory-induced plant volatiles (HIPVs) (<xref ref-type="bibr" rid="B173">Wang et&#xa0;al., 2016b</xref>; <xref ref-type="bibr" rid="B192">Yang et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B102">Li et&#xa0;al., 2020</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Empoasca onukii</italic>
</td>
<td valign="middle" align="center">Plant hormones (JA, SA and ABA), Phenylpropanoid and cuticular wax biosynthesis, Flavonoids biosynthesis, (S)-Linalool, Geraniol, Diene diol I (<xref ref-type="bibr" rid="B40">Cho et&#xa0;al., 2007</xref>; <xref ref-type="bibr" rid="B89">Jin et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B208">Zhao et&#xa0;al., 2020b</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Ectropis grisescens</italic>
</td>
<td valign="middle" align="center">Plant hormones (JA, ethylene and auxin), Three catechin compounds (epicatechin, [+]-catechin and epigallocatechin) (<xref ref-type="bibr" rid="B104">Li et&#xa0;al., 2022</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Exobasidium vexans</italic>
</td>
<td valign="middle" align="center">Defense related enzymes, Resistance genes, Multidrug resistant transporters, Transcription factors, Retrotransposons, Metacaspases and chaperons, Dominant microorganisms change (<xref ref-type="bibr" rid="B83">Jayaswall et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B29">Cao et&#xa0;al., 2023</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Colletotrichum fructicola</italic>
</td>
<td valign="middle" align="center">S-Adenosylmethionine Synthetase (SAMS), Tea Caffeine Synthase1 (TCS1) &#x548c;Leucoanthocyanidin Reductase (LAR) (<xref ref-type="bibr" rid="B172">Wang et&#xa0;al., 2016a</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Pseudopestalotiopsis camelliae-sinensis</italic>
</td>
<td valign="middle" align="center">CsmiR397a-CsLAC17 module (<xref ref-type="bibr" rid="B190">Yang et&#xa0;al., 2024</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Toxoptera aurantii</italic> Boyer</td>
<td valign="middle" align="center">Flavonoids biosynthesis, Plant hormones (JA) (<xref ref-type="bibr" rid="B114">Liu et&#xa0;al., 2024b</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Pseudomonas</italic> sp.</td>
<td valign="middle" align="center">Defense related enzymes (L-phenylalanine ammonia-lyase, Peroxidase, Polyphenol oxidase) (<xref ref-type="bibr" rid="B122">Mishra et&#xa0;al., 2014</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Bacillus megaterium</italic>
</td>
<td valign="middle" align="center">Defense related enzymes (Peroxidase, Chitinase, &#x3b2;-1,3-glucanase, Phenylalanine ammonia-lyase) (<xref ref-type="bibr" rid="B33">Chakraborty et&#xa0;al., 2006</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Bacillus altitudinis</italic>
</td>
<td valign="middle" align="center">Defense related enzymes (Polyphenol oxidase, Superoxide dismutase, Phenylalanine ammonia-Lyase) (<xref ref-type="bibr" rid="B178">Wu et&#xa0;al., 2024b</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Trichoderma Asperellum</italic>
</td>
<td valign="middle" align="center">Plant hormones (JA and ET), Flavonoids and phenylpropanoid biosynthesis (<xref ref-type="bibr" rid="B150">Shang et&#xa0;al., 2020</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Trichoderma reesei</italic>
</td>
<td valign="middle" align="center">Defense related enzymes (Polyphenol oxidase, Peroxidase, Phenylalanine ammonia-lyase, Phenolic compounds, &#x3b2;-1,3-glucanase, Chitinase) (<xref ref-type="bibr" rid="B129">Pandey et&#xa0;al., 2022</xref>)</td>
</tr>
<tr>
<td valign="middle" align="center">
<italic>Rhizophagus intraradices</italic>
</td>
<td valign="middle" align="center">Plant hormones, Mitogen-Activated Protein Kinase (MAPK), Signal transduction, Phenylpropanoid biosynthesis (<xref ref-type="bibr" rid="B37">Chen et&#xa0;al., 2022</xref>)</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
</sec>
<sec id="s6">
<label>6</label>
<title>Conclusions and future perspectives</title>
<p>This review primarily summarizes the potential of microbial biocontrol agents (MBCAs) in enhancing both the management of tea tree diseases and the quality of tea leaves. The use of MBCAs represents a shift from merely targeting and killing pests or pathogens to protecting tea trees and improving their overall health. Integrating MBCAs into tea plantation management practices can bolster the natural defenses of tea trees and improve the overall quality of tea by fostering beneficial microbial communities. This approach also provides a valuable model for the application of microbial biocontrol agents in other perennial crop systems. However, existing research faces challenges such as limited effectiveness, stability issues, high costs, and gaps in understanding the molecular mechanisms of MBCAs. Future research directions should focus on:</p>
<list list-type="order">
<list-item>
<p>Development and Application of Novel Microbial Biocontrol Agents: Future studies should aim to discover and develop more effective MBCAs, especially those targeting specific diseases or pests affecting tea trees. Additionally, research should explore the integration of MBCAs with tea plantation management practices such as fertilization, irrigation, and crop rotation. Optimizing these integrated management strategies could lead to a comprehensive microbial biocontrol approach for tea plantation management.</p>
</list-item>
<list-item>
<p>Mechanisms of MBCAs on Tea Quality: Understanding how MBCAs improve tea quality is essential. Research should focus on how these agents influence the metabolic pathways of tea trees, especially in terms of nutrient uptake, stress responses, and the production of secondary metabolites that contribute to tea flavor and aroma. Investigating how MBCAs improve tea quality by modulating the metabolic pathways of tea trees and promoting the establishment of beneficial microbial communities is essential. Understanding these mechanisms will help establish the relationship between tea tree microecology and tea quality, providing a scientific basis for optimizing ecological pest control in tea plantations and enhancing tea quality.</p>
</list-item>
<list-item>
<p>Addressing Limitations and Enhancing Efficiency of MBCAs: Current challenges with MBCAs include issues related to their stability, limited range of effectiveness, and high costs. Future research could focus on developing new carriers to maintain microbial activity, combining MBCAs with other control methods to enhance efficacy, and optimizing fermentation processes to reduce production and application costs. These efforts aim to make the use of MBCAs in tea plantation management more economically viable and effective.</p>
</list-item>    </list>
</sec>
</body>
<back>
<sec id="s7" sec-type="author-contributions">
<title>Author contributions</title>
<p>YX: Methodology, Writing &#x2013; original draft. CC: Funding acquisition, Methodology, Project administration, Writing &#x2013; review &amp; editing. DH: Software, Visualization, Writing &#x2013; review &amp; editing. YG: Conceptualization, Funding acquisition, Methodology, Resources, Supervision, Writing &#x2013; review &amp; editing. BW: Conceptualization, Funding acquisition, Methodology, Writing &#x2013; original draft.</p>
</sec>
<sec id="s8" sec-type="funding-information">
<title>Funding</title>
<p>The author(s) declare that financial support was received for the research, authorship, and/or publication of this article. This research was funded by the National Natural Science Foundation of China (32302449), and Science and Youth Science Fund Project of Hubei Academy of Agricultural Sciences (2023NKYJJ27), Hubei Provincial Key Research and Development Project (2023BBB148).</p>
</sec>
<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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