Your new experience awaits. Try the new design now and help us make it even better

ORIGINAL RESEARCH article

Front. Microbiomes, 28 November 2025

Sec. Environmental Microbiomes

Volume 4 - 2025 | https://doi.org/10.3389/frmbi.2025.1666691

This article is part of the Research TopicEcological Roles and Functional Contributions of Environmental Microbiomes in Ecosystem DynamicsView all articles

Identification of microbial communities associated with Phymatotrichopsis omnivora sclerotia in two Texas fields

  • 1Department of Plant Pathology and Microbiology, Texas A&M University, College, Station, TX, United States
  • 2Department of Horticultural Sciences, Texas A&M University, College, Station, TX, United States

The soilborne fungus Phymatotrichopsis omnivora causes a mid- to late-season disease known as cotton root rot (CRR). In the United States, P. omnivora is primarily found in Arizona, New Mexico, Oklahoma, and Texas in soils that are alkaline, calcareous, and rarely freeze deeply. This fungus has a wide host range, and can cause substantial losses in cotton crops. In Texas, not all cotton-producing soils have widespread CRR despite having the characteristics to support P. omnivora. Considering the lack of CRR in some Texas soils, we hypothesize that this absence could be due to the microbial composition associated with sclerotia of P. omnivora. The objective of this study was to identify the taxa that make up microbial communities associated with P. omnivora sclerotia in different soils during both the cotton-growing and off seasons. The microbiota associated with P. omnivora sclerotia were identified by burying lab-generated sclerotia in cotton-producing soils. These sclerotia were recovered, along with soil samples for metabarcoding targeting the 16S rRNA gene and the internal transcribed spacer region. When compared to bulk soil, microbial communities associated with sclerotia differed in community composition and taxa relative abundance between a soil with widespread CRR and one in which the disease is absent. Within these soil communities, potential bacterial and fungal biomarkers that reduce CRR were identified. Furthermore, microbial communities of P. omnivora sclerotia changed seasonally. This study presents the first detailed characterization of microorganisms associated with P. omnivora sclerotia in different cotton-producing soils. Our findings support the view that P. omnivora sclerotia serve as ecological hubs, shaping microbial communities with possible implications for disease suppression. Several enriched taxa are culturable, offering candidates for future biocontrol studies that could inform disease management strategies that focus on increased microbial competition.

1 Introduction

Cotton root rot (CRR), caused by the soilborne fungal plant pathogen Phymatotrichopsis omnivora (Duggar) Hennebert 1973, is a mid- to late-season disease affecting economically important crops in the American southwest such as cotton, pecan trees, winegrape, and alfalfa. P. omnivora forms sclerotia in soils from southwestern Arkansas, through the majority of Texas, to southern Arizona (Streets and Bloss, 1973). Annual losses from CRR in Texas cotton can reach $29 million in years that are especially conducive to disease progression (Isakeit, 2021), and in the 2024 growing season, an estimated 20,026 bales were lost to CRR in the southwestern cotton crop (Faske and Sisson, 2025). Even though CRR can have a significant impact in Texas, the disease is not present in all parts of the state, including cotton-producing soils with the characteristics to support the pathogen, specifically, alkaline, calcareous, and rarely freezing deeply (Percy, 1983). We hypothesize that the absence of CRR could be due to a suppressive microbial composition. The relationship between P. omnivora and other soil microorganisms has been of interest for many years. A study by Chavez et al. (1976) showed that increased microbial diversity, through the addition of green manure to a field, can reduce the incidence of CRR. Furthermore, sclerotia of P. omnivora support bacterial communities that include fluorescent pseudomonads and actinomycetes (Zuberer et al., 1988). There are several examples of soil microbiomes mediating plant disease including microbial richness and diversity affecting fusarium wilt in vanilla (Vanilla planifolia; F. oxysporum f. sp. vanilla) and banana (Musa species; F. oxysporum f. sp. cubense Tropical Race 4) (Xiong et al., 2017; Jamil et al., 2023), community composition affecting potato scab (Streptomyces species) incidence (Shi et al., 2019), populations of Firmicutes and Actinobacteria in the tomato rhizosphere protecting the plant against bacterial wilt (Ralstonia solanacearum) (Lee et al., 2021), and rhizosphere selection over successive wheat plantings affecting root disease caused by Rhizoctonia solani (Yin et al., 2021).

Fairly recently, the concept of the pathobiome has emerged as a compelling area of study. Pathogen-associated microorganisms can affect the ability of that pathogen to infect a host, or even create a scenario in which a commensal microbe turns pathogenic due to a change in the microbiome (Vayssier-Taussat et al., 2014). The term for microbes associated with pathogens is “pathobionts”, and they can have a great impact on disease (Jochum and Stecher, 2020). Some pathobionts live within fungal partners as endohyphal bacteria, influencing the virulence of fungal plant pathogens, as well as contributing to the survival of fungi through the modulation of hormones and metabolites (Moses and Carter, 2025). Obasa et al. (2019) demonstrated that two endohyphal strains of Enterobacter increased macroconidia and fumonisin production in F. fujikuroi, leading to higher levels of virulence. Thomas and Antony-Babu (2024) identified the core bacterial hyphosphere of a Fusarium wilt pathogen, F. oxysporum f. sp. niveum, which shed light on pathobionts contributing to virulence, and strengthens the idea that pathogens are not lone invaders when they gain access to a host. This work was expanded upon by Thomas et al. (2025) when it was shown that the microbial community structure of the F. oxysporum f. sp. cubense tropical race 4 hyphosphere was highly correlated with the microbial community structure of diseased tissue colonized by the pathogen. Additionally, Jakuschkin et al. (2016) investigating microbial interactions on oak leaves (Quercus robur L.), found that oak powdery mildew (Erysiphe alphitoides) is both positively and negatively associated with discrete operational taxonomic units (OTUs) in the phyllosphere. Looking to cotton as a system for the study of bacterial-fungal interactions, Antony-Babu et al. (2025) showed that members of the genus Pseudomonas were preferentially selected for in the F. oxysporum f. sp. vasinfectum Race 4 (FOV4) hyphosphere, a fungus that causes Fusarium wilt in cotton. This finding has implications for virulence and survival of FOV4 because several Pseudomonas isolates that were associated with hyphal tips significantly promoted hyphal growth.

In addition to contributing to fungal virulence, there are also bacterial members of the pathobiome that feed on fungi, exhibiting mycophagy. Bacterial mycophagy can be defined as a set of behaviors that allow bacteria to convert fungal biomass into a nutrient source (de Boer et al., 2005; Fritsche et al., 2006). These mycophagous bacteria have implications for suppressive soils if they are able to feed on plant pathogenic fungi. Mycophagous bacteria exhibit three strategies to derive nutrients from fungi: necrotrophy, extracellular biotrophy, or endocellular biotrophy (Leveau and Preston, 2008). These strategies demonstrate that bacteria feeding on a fungus does not mean that they are killing that organism, which also has biocontrol implications. A pathobiome study has not been done with the primary inoculum of P. omnivora, the sclerotia. Furthermore, the microbial ecology of fungal sclerotia generally is an understudied field. As previously mentioned, there is evidence to suggest that there is a microbial aspect in the success of P. omnivora to cause CRR.

In this ecological study, soil microorganisms were identified using metabarcoding to better understand the microbial community associated with P. omnivora sclerotia. The core hypothesis of this study is that live sclerotia will deterministically recruit a functional microbial community. With this hypothesis in mind, the objectives of this study were to identify microbial communities associated with P. omnivora sclerotia in fields that differ in their of support CRR during the cotton-growing and off seasons, as well as determine if these communities change between seasons. To investigate these objectives, metabarcoding was used to sequence soil in contact with lab-grown sclerotia. One cycle of seasonal change was evaluated at two locations with contrasting histories of CRR. Additionally, changes in microbial communities were assessed over three seasons in a soil that is CRR-conducive. Finally, potential determinism in the sclerotia-associated communities was assessed using linear discriminant analysis effect size (LEfSe) and Beta-Nearest Taxon Index (βNTI) to identify biomarkers in microbial communities associated with particular niches and assess deterministic selection within those niches.

2 Materials and methods

2.1 P. omnivora isolates and test sites

A single P. omnivora isolate was used in each of the burial seasons. For the 2023 and 2024 cotton-growing seasons, an isolate obtained from Willacy County, TX in 2022 was used. For the 2023–2024 off-season, an isolate obtained from Williamson County, TX in 2023 was used. P. omnivora isolates used in this study were collected from infected upper root tissue of cotton plants (Gossypium hirsutum) by thoroughly washing with water, followed by copious spraying with 70% ethanol and repeated whittling and peeling of outer tissue, until a lesion was identified. From this lesion, small pieces of tissue were excised and plated on half-strength potato dextrose agar amended with 10 mg of streptomycin per 100 mL (½ PDAs). The advancing margins of developing growth of P. omnivora were then transferred to a new ½ PDAs plate to obtain a pure culture. All isolates were stored at ambient room temperature (22°C) and sub-cultured monthly to maintain viability. These isolates were used to generate sclerotia as described in Section 3.2.

Lab-generated sclerotia were buried in one location during the 2023 cotton-growing season, as well as two locations during the 2023–2024 off-season and the 2024 cotton-growing season. The first location was the Stiles Farm in Williamson County, TX, and is considered the CRR-conducive location because there is widespread CRR in that field. The soil type at the location of the Stiles Farm where the sclerotia were buried is a Burleson clay (USDA NRCS). Its characteristics were 30% sand, 30% silt, 40% clay, pH 7.7, 1.7% organic matter, and a cation exchange capacity (CEC) of 33. Sclerotia were buried at this location during all three seasons. The second location was the Texas A&M Research Farm (Bottom Farm) in Burleson County, TX, and this location is considered to be non-conducive to CRR because the disease does not occur in that soil type in that area. The soil type at the location of the Bottom Farm where the sclerotia were buried is a Weswood silty clay loam (USDA NRCS). Its characteristics were 19% sand, 55% silt, 26% clay, pH 8.0, 1.2% organic matter, and a CEC of 30. Sclerotia were buried in this location during the 2023–2024 off-season and the 2024 cotton-growing season. Sclerotia were buried in mesh bags from June 2023 to September 2023 for the 2023 cotton-growing season, from December 2023 to March 2024 for the off-season burial period, and from June 2024 to September 2024 for the 2024 cotton-growing season burial period.

2.2 Sclerotia preparation in laboratory microcosms

Sclerotia were produced in vitro in a sorghum seed-soil substrate following a modification of the protocol of Dunlap (1941). Each microcosm was prepared in 250 mL Erlenmeyer flasks containing 10g of autoclaved sorghum seed and 100g of air-dried soil that was wetted with 30 mL reverse-osmosis (RO) water and inoculated with an agar plug of P. omnivora. The sorghum seed layer, above the soil, served as a growth medium for P. omnivora, from which it produced sclerotia in soil from rhizomorphs. The seed, initially in glass Petri dishes, along with 5 mL RO water, was autoclaved on a gravity cycle (121°C, 24 PSI) for 20 min. After autoclaving, the sorghum seed was placed on top of the soil within the Erlenmeyer flask that had been moistened with RO water. This flask was then autoclaved on a gravity cycle for one hour, allowed to cool, then inoculated with an agar plug of P. omnivora. These inoculated flasks were placed in plastic bags and incubated at 32°C for five weeks. At that time, the colonized sorghum was removed from the flasks and discarded, while the soil was wet sieved over a number 18 sieve (1 millimeter opening). The sclerotia were collected from the sieve, surface sterilized in a 10% bleach solution for 30 seconds, then rinsed in autoclaved RO water for 1 min. The sclerotia were quickly blotted dry on sterile filter paper then transferred to a glass Petri dish containing autoclaved soil for storage. This Petri dish was sealed with Parafilm and stored at ambient room temperature.

2.3 Field inoculation of P. omnivora sclerotia

To assess the microbial communities associated with P. omnivora sclerotia, we deployed laboratory-generated sclerotia using retrievable mesh bags. The mesh bag setup consisted of a firm plastic 1-mm2 opening mesh, 9.5 x 6 mm in size, with an opening at the top, which contained 10–15 sclerotia. The sclerotia bags were deployed across two geographically distinct sites in Texas: (1) the Stiles Farm in Williamson County, a site with widespread CRR and thus considered CRR-conducive, where sclerotia were buried during the 2023 cotton-growing season, the 2023–2024 off-season, and the 2024 cotton-growing season; and (2) the Texas A&M Research Farm (Bottom Farm) in Burleson County, a CRR-nonconducive site based on the absence of disease in the local soil type, where sclerotia were buried during the 2023–2024 off-season and 2024 growing season. There were a total of nine bags buried about 15 cm deep in three rows. The heat-killed sclerotia were autoclaved prior to burial. The burial locations of the bags were marked with stakes. Viability of sub-samples of sclerotia used in the burials was tested on ½ PDAs and unamended nutrient agar prior to burial, and germination of the recovered sclerotia was tested on ½ PDAs.

2.4 Soil collection

Following the three-month field incubation periods, the bags were recovered, and soil in contact with the bags was collected. Bulk soil samples were collected from two locations approximately 15 cm deep and at least 6 m away from any sclerotia bag, to serve as controls. One soil sample from each bag burial and bulk soil location was collected in a 50 mL centrifuge tube using plastic spoons for a total of 11 soil samples (six live sclerotia, three heat-killed sclerotia, and two bulk soil). These samples were transported back to the laboratory in a cooler with dry ice and then stored at 2 to 8°C prior to DNA extraction.

2.5 DNA extraction and metabarcoding sequencing

For DNA extraction, two preparations were taken from each soil sample providing 22 soil DNA samples (12 live sclerotia, six heat-killed sclerotia, and four bulk soil). DNA extraction was done using the DNeasy® PowerSoil® Pro Kit (Qiagen, Valencia, CA, USA) following the protocol provided by the manufacturer. Extracted DNA quality was evaluated using a Quickdrop Micro-volume spectrophotometer (Molecular Devices, San Jose, CA, USA). DNA was quantified using a Qubit Double-Stranded DNA High-Sensitivity Assay Kit (Thermo Fisher Scientific, MA, USA) in a Qubit 2.0 fluorometer (Invitrogen, CA, USA). Library preparation and sequencing was done through Novogene (Sacramento, CA, USA). Amplicon libraries were prepared using the primers 341F – CCT AYG GGR BGC ASC AG and 806R – GGA CTA CNN GGG TAT CTA AT targeting the V3-V4 region of 16S rRNA. For ITS region-based library preparation, the primers ITS5-1737-F – GGA AGT AAA AGT CGT AAC AAG G and ITS2-2043- R – GCT GCG TTC TTC ATC GAT GC were used. Twenty-two separate samples were sequenced for both bacterial and fungal identification, totaling 44 samples per burial location for each of the seasons.

2.6 Metabarcoding sequence analysis pipeline

Raw reads were processed using Mothur v.1.48 (Schloss et al., 2009). Mothur was run utilizing computing resources from the Texas A&M High Performance Research Computing Department. The protocols for Mothur were followed based on the MiSeq standard operating procedure (https://mothur.org/wiki/miseq_sop/). The total number of reads for the 2023 cotton-growing season was 1,036,501 for 16S V3-V4 amplicon sequences and 510,923 for ITS region amplicon sequences after quality filtering. For ITS region analysis during the 2023 cotton-growing season, sequence reads exceeding 400 base pairs (bp) were removed. The total number of reads for the 2023–2024 off-season was 2,336,959 for 16S V3-V4 amplicon sequences and 876,704 for ITS region amplicon sequences after quality filtering. The total number of reads for the 2024 cotton-growing season was 2,318,350 for 16S V3-V4 amplicon sequences and 1,369,654 for ITS amplicon sequences after quality filtering. Additionally, any ambiguous bases and maximum repeats for eight or more nucleotide sequences were removed using “maxambig” and “maxhomop” in Mothur. Mothur functions were applied to make contigs, filter out bad reads, remove chimeras, and assign OTUs. A 97% cutoff was applied to bacterial and fungal taxa. For taxonomic assignment of 16S rRNA reads, the Ribosomal Database project classifier (Wang et al., 2007) with the Silva database v138 (Quast et al., 2013) was used. For taxonomic assignment of ITS region reads, a Mothur release of UNITE database v6 (Abarenkov et al., 2021) was used. Using “remove.lineage” in Mothur, OTUs assigned to chloroplast, mitochondria, Archaea, Eukaryota, and unknown were removed for 16S rRNA reads, and OTUs assigned to chloroplast, mitochondria, Archaea, and unknown were removed for ITS region reads.

2.7 Data analysis and statistical evaluation

Mothur was used to perform an analysis of molecular variance (AMOVA) to compare sclerotia treatments to each other and to bulk soil. Files created in Mothur were input into RStudio utilizing multiple R versions due to the extended time frame of data analysis. In RStudio, the packages “tidyverse” and “broom” were used for statistical analysis and data visualization. Soil microbial diversity was assessed using the Shannon and inverse Simpson diversity indices, observed diversity, and evenness, and statistical comparisons were made using a t-test. Comparison of diversity between locations and seasons, or beta-diversity, was visualized using non-metric multidimensional scaling (NMDS) constructed using the Bray-Curtis dissimilarity matrix, with significant differences determined using the AMOVA results from Mothur. Differences in relative abundance of taxa within a location or season, or alpha-diversity, were assessed using a pairwise Wilcoxon test. To assess which OTUs were enriched when comparing sclerotia treatments, locations, and seasons, LEfSe analyses were performed to identify biomarkers within microbial communities (Segata et al., 2011). To evaluate for deterministic selection in microbial communities, βNTI analyses were performed utilizing the “microeco” package in RStudio (Liu et al., 2021). βNTI analyses reveal whether the phylogenetic composition of communities are more similar or dissimilar than expected under stochastic assembly models. Phylogenetic trees used in the βNTI analyses were created with FASTA outputs from “get.oturep” in mothur to generate a list of OTUs and representative sequences. For all analyses, differences were considered significant at an alpha level of 0.05, unless otherwise noted.

3 Results

3.1 Comparison of communities between locations: 2023–2024 off-season

Comparing the two soils, based on the Shannon Index, bacterial diversity was significantly (p<0.001) higher at the CRR-nonconducive Bottom Farm (Figure 1A), while fungal diversity was numerically higher at the CRR-conducive Stiles Farm (Figure 1B). When comparing the diversity of the communities between the soils, both bacterial (Fs=8.8, p<0.001) and fungal (Fs=6.3, p<0.001) communities significantly differed from one another (Figure 2). For each location, sclerotia and bulk soil treatments were significantly different. At the Bottom Farm, bacterial communities associated with live sclerotia differed significantly from those in bulk soil (p<0.001), as did communities associated with heat-killed sclerotia (p=0.049). Similarly, at the Stiles Farm, both live sclerotia (p<0.001) and heat-killed sclerotia (p=0.005) supported bacterial communities that were significantly different from the bulk soil. However, no significant differences were observed between bacterial communities associated with live and heat-killed sclerotia at either site. The fungal communities followed a similar pattern except for the Bottom Farm, where no significant differences were detected among treatments. At the Stiles Farm, fungal communities associated with both live sclerotia (p=0.007) and heat-killed sclerotia (p=0.043) differed significantly from the bulk soil, while no significant differences were observed between live and heat-killed sclerotia at either site.

Figure 1
Box plots comparing 2023-2024 off-season microbial diversity on two farms. Panel A shows bacterial Shannon diversity with higher values at Bottom Farm (non-conducive) than Stiles Farm (conducive). Panel B shows fungal Shannon diversity with marginally higher values at the Stiles Farm.

Figure 1. Microbial diversity during the 2023–2024 off-season. (A) Bacterial Shannon diversity was significantly (p<0.001) higher at the Bottom Farm. (B) Fungal Shannon diversity was numerically higher at the Stiles Farm, but not significantly. “*” represents a significant difference.

Figure 2
Two NMDS plots compare microbial communities. Plot A shows bacterial communities at Bottom and Stiles Farms with ellipses for live, heat-killed sclerotia, and bulk soil. Plot B displays fungal communities with similar groupings. Different colors represent live sclerotia (blue), heat-killed sclerotia (red), and bulk soil (black) for farms. Axes are labeled NMDS Axis 1 and 2.

Figure 2. Comparison of microbial communities between locations during the 2023–2024 off-season separated by sclerotia treatment. Bacterial (A) and fungal (B) communities were significantly (p<0.001) different by location.

To assess compositional differences, we identified the 10 most abundant bacterial orders averaged across samples in each of the sclerotia treatments and bulk soil (Supplementary Table S1). At the Bottom Farm, bacteria affiliated with the orders Hyphomicrobiales, Rhodospirillales, and Propionibacteriales were found at a significantly higher relative abundance than at the Stiles Farm (Figure 3A). At the Stiles Farm, bacteria in the orders Gaiellales, Unclassified Bacteria, Solirubrobacterales, and Rubrobacterales were found at a significantly higher relative abundance than at the Bottom Farm (Figure 3A). With fungal communities, there were significant differences among the seven most abundant fungal orders averaged across samples in each of the sclerotia treatments and bulk soil (Supplementary Table S2). At the Bottom Farm, fungal orders Hypocreales and Unclassified Ascomycota were found at a significantly higher relative abundance than at the Stiles Farm (Figure 3B). However, at the Stiles Farm, fungi in the orders Eurotiales and Sordariales were found at a significantly higher relative abundance than at the Bottom Farm (Figure 3B). The full breadth of bacterial and fungal alpha diversity during the 2023–2024 off-season, at the order level, are presented in Supplementary Figures S5, S6, respectively.

Figure 3
Two heatmaps compare the relative abundance of microbial orders during the 2023-2024 off-season. Panel A shows the top ten bacterial orders, with colors indicating abundance from light to dark red. Panel B displays the top seven fungal orders similarly. Each heatmap includes categories BF Live Sclerotia, BF Heat-killed Sclerotia, BF Bulk Soil, SF Live Sclerotia, SF Heat-killed Sclerotia, and SF Bulk Soil, varying in shading based on abundance percentages.

Figure 3. Heatmaps displaying diversity within location during the 2023–2024 off-season. Bolded orders are significantly (p<0.05) different between the Bottom Farm (BF) and Stiles Farm (SF). “(BF)” or “(SF)” after a bolded order indicates which location had a significantly higher relative abundance of that order. (A) Comparison of bacterial communities. (B) Comparison of fungal communities.

In the Bottom Farm communities, the genus Pseudomonas made up 0.06% of the community, while members of the class Actinobacteria made up 17.86%. In the Stiles Farm communities, the genus Pseudomonas made up 0.18% of the community, while members of the class Actinobacteria made up 13%.

Based on the results of three LEfSe analyses, genera that were enriched in live sclerotia treatments when compared to bulk soil, but not enriched in heat-killed sclerotia, were selected. At the Bottom Farm, seven bacterial genera met these criteria (with the percentage that genus represents in the live sclerotia community in parentheses): Virgisporangium (0.417%), Stenotrophobacter (0.159%), Skermanella (1.234%), Mesorhizobium (0.086%), Massilia (0.255%), Marmoricola (0.594%), and Dactylosporangium (0.106%). Of these seven genera, three were enriched in Bottom Farm communities as a whole: Virgisporangium, Skermanella, and Marmoricola. At the Bottom Farm, two fungal genera met these criteria: Paecilomyces (0.825%) and Colletotrichum (0.151%), both of which were enriched in Bottom Farm communities as a whole. At the Stiles Farm, one bacterial genus met the aforementioned criteria – Stenotrophobacter (0.151%). Also at the Stiles Farm, three fungal genera met the criteria: Preussia (0.619%), Hyponectriacea species (0.873%), and Alternaria (12.8%). Two of those fungal genera, Hyponectriacea species and Alternaria, were enriched at the Stiles Farm as a whole.

The results of the βNTI analyses did not indicate deterministic selection for live sclerotia when compared to the other treatments for bacterial and fungal communities at both locations. At the Bottom Farm, the average βNTI values for bacterial communities were -5.18, -5.04, and -5.15 for live sclerotia, heat-killed sclerotia, and bulk soil, respectively. For fungal communities at the Bottom Farm, the average βNTI values were -1.44, -1.44, and -1.29 for live sclerotia, heat-killed sclerotia, and bulk soil, respectively. At the Stiles Farm, the average βNTI values for bacterial communities were -4.88, -4.72, and -5.05 for live sclerotia, heat-killed sclerotia, and bulk soil, respectively. For fungal communities at the Stiles Farm, the average βNTI values were -1.71, -1.5, and -1.59 for live sclerotia, heat-killed sclerotia, and bulk soil, respectively. The βNTI values at both locations for bacterial communities indicated that there was more phylogenetically similarity in those communities than what is expected under stochastic assembly models. On the other hand, the βNTI values at both locations for fungal communities indicated stochastic selection.

3.2 Comparison of communities between locations: 2024 cotton-growing season

Bacterial and fungal diversity was significantly (p<0.001) higher at the Bottom Farm than the Stiles Farm (Figure 4). When comparing the diversity of communities between locations, both bacterial (Fs=13.2, p<0.001) and fungal (Fs=6.7, p<0.001) communities significantly differed from one another (Figure 5). When looking within a location, sclerotia and bulk soil treatments significantly differed from one another. In bacterial communities at the Bottom Farm, the following treatments were significantly different from one another: live sclerotia – bulk soil (p=0.007) and heat-killed sclerotia – bulk soil (p=0.003). In sclerotia-associated bacterial communities at the Stiles Farm, only two treatments were significantly different from one another: live sclerotia – heat-killed sclerotia (p=0.003). In fungal communities at the Bottom Farm, the following treatments were significantly different from each other: live sclerotia – bulk soil (p=0.028), heat-killed sclerotia – bulk soil (p=0.031), and live sclerotia – heat-killed sclerotia (p=0.008). In fungal communities at the Stiles Farm, the following treatments were significantly different: live sclerotia – bulk soil (p<0.001), heat-killed – bulk soil (p=0.007), and live sclerotia – heat-killed sclerotia (p=0.015).

Figure 4
Two box plots comparing Shannon Diversity. Plot A shows bacterial diversity, with higher values at Bottom Farm (non-conducive) than Stiles Farm (conducive). Plot B shows fungal diversity, also higher at Bottom Farm than Stiles Farm. Both plots indicate more diversity at the non-conducive site.

Figure 4. Microbial diversity during the 2024 cotton-growing season. Bacterial (A) and fungal (B) Shannon diversity was significantly (p<0.001) higher at the Bottom Farm. “*” represents a significant difference.

Figure 5
NMDS projections compare bacterial and fungal communities at the Bottom and Stiles farms during the 2024 cotton-growing season. Plot A displays bacterial communities using colored ellipses for different treatments: live sclerotia (blue), heat-killed sclerotia (red), and bulk soil (black). Plot B presents fungal communities with similar color coding but includes overlaps. Data is plotted on NMDS axes for both plots, showing significant community distribution differences between the two locations.

Figure 5. Comparison of microbial communities between locations during the 2024 cotton-growing season separated by sclerotia treatment. Bacterial (A) and fungal (B) communities were significantly (p<0.001) different by location.

Comparing relative abundance within a location, there were significant differences among the 10 most abundant bacterial orders averaged across samples in each of the sclerotia treatments and bulk soil (Supplementary Table S1). At the Bottom Farm, bacteria in the orders Rhodospirillales and Acidobacteria Gp6 incertae sedis were found at a significantly higher relative abundance than at the Stiles Farm (Figure 6A). At the Stiles Farm, bacteria in the orders Unclassified Bacteria, Caryophanales, Rubrobacterales, Gaiellales, and Unclassified Actinomycetota were found at a significantly higher relative abundance than at the Bottom Farm (Figure 6A). With fungal communities, there were significant differences among the eight most abundant fungal orders averaged across samples in each of the sclerotia treatments and bulk soil (Supplementary Table S2). At the Bottom Farm, fungi in the orders Hypocreales, Pleosporales, Unclassified Ascomycota, and Ascomycota order Incertae sedis were found at a significantly higher relative abundance than at the Stiles Farm (Figure 6B). At the Stiles Farm, fungi in only one order were found at a significantly higher relative abundance than at the Bottom Farm – Eurotiales (Figure 6B). The full breadth of bacterial and fungal alpha diversity during the 2024 cotton-growing season, at the order level, is shown in Supplementary Figures S7, S8, respectively.

Figure 6
Heat map displaying the relative abundance of top bacterial and fungal orders during the 2024 cotton-growing season. Panel A shows bacterial orders with varying abundance levels, highlighted by shades of red. Panel B presents fungal orders, also color-coded by abundance. The legend indicates average relative abundance percentages using a gradient from light to dark red. Categories include live and heat-killed sclerotia, and bulk soil for both bacterial and fungal orders.

Figure 6. Heatmaps displaying diversity within location during the 2024 cotton-growing season. Bolded orders are significantly (p<0.05) different between the Bottom Farm (BF) and Stiles Farm (SF). “(BF)” or “(SF)” after a bolded order indicates which location had a significantly higher relative abundance of that order. (A) Comparison of bacterial communities. (B) Comparison of fungal communities.

In the Bottom Farm communities, the genus Pseudomonas made up 0.12% of the community, while members of the class Actinobacteria made up 17.9%. In the Stiles Farm communities, the genus Pseudomonas made up 0.02% of the community, while members of the class Actinobacteria made up 15.44%.

Based on the results of three LEfSe analyses, genera that were enriched in live sclerotia treatments when compared to bulk soil, but not enriched in heat-killed sclerotia, were selected. At the Bottom Farm, there were three bacterial genera that met these criteria (with the percentage that genus represents in the live sclerotia community in parentheses): Robertmurraya (0.275%), Gp10 (0.373%), and Cellulomonas (0.159%). Of these three genera, one was enriched in Bottom Farm communities as a whole – Cellulomonas. At the Bottom Farm, three fungal genera met these criteria: Paecilomyces (4.06%), Mycoleptodiscus (4.833%), and Coniocessia (0.043%). Of these three genera, two were enriched in Bottom Farm communities as a whole: Paecilomyces and Mycoleptodiscus. At the Stiles Farm, two bacterial genera met the aforementioned criteria: Metabacillus (0.28%) and Domibacillus (0.651%), both of which were enriched at the Stiles Farm as a whole. Also at the Stiles Farm, one fungal genus met the criteria – Coniocessia (0.038%).

The results of the βNTI analyses did not indicate deterministic selection for live sclerotia when compared to the other treatments for bacterial and fungal communities at both locations. At the Bottom Farm, the average βNTI values for bacterial communities were -4.49, -4.52, and -4.91 for live sclerotia, heat-killed sclerotia, and bulk soil, respectively. For fungal communities at the Bottom Farm, the average βNTI values were -1.31, -1.36, and -1.13 for live sclerotia, heat-killed sclerotia, and bulk soil, respectively. At the Stiles Farm, the average βNTI values for bacterial communities were -4.49, -4.39, and -4.51 for live sclerotia, heat-killed sclerotia, and bulk soil, respectively. For fungal communities at the Stiles Farm, the average βNTI values were -1.03, -1.02, and -1.39 for live sclerotia, heat-killed sclerotia, and bulk soil, respectively. The βNTI values at both locations for bacterial communities indicated that there was more phylogenetically similarity in those communities than what is expected under stochastic assembly models. On the other hand, the βNTI values at both locations for fungal communities indicated stochastic selection.

3.3 Comparison of communities between seasons: off versus cotton-growing season

When bacterial and fungal diversity during the off-season and cotton-growing seasons was compared at both locations, two significant differences were observed. Off-season bacterial diversity at the Bottom Farm was significantly (p<0.001) higher than the cotton-growing season at that location (Figure 7), and off-season fungal diversity at the Stiles Farm was significantly (p<0.001) higher than the cotton-growing season at that location (Figure 8). When comparing the diversity of the communities between seasons as a whole, or beta-diversity, both bacterial and fungal communities significantly (p<0.001) differed from one another. Between the cotton-growing and off seasons, sclerotia and bulk soil treatments differed significantly. In bacterial communities at the Bottom Farm, live sclerotia (p<0.001), heat-killed sclerotia (p=0.003), and bulk soil (p=0.023) were all significantly different between the seasons. In bacterial communities at the Stiles Farm, live sclerotia (p<0.001) and heat-killed sclerotia (p<0.001) were significantly different, but not the bulk soil communities. In fungal communities at the Bottom Farm, live sclerotia (p<0.001), heat-killed sclerotia (p=0.004), and bulk soil (p=0.023) were all significantly different by season. In fungal communities at the Stiles Farm, live sclerotia (p<0.001) were significantly different by season, however, heat-killed sclerotia and bulk soil were not.

Figure 7
Box plots show bacterial Shannon diversity during cotton-growing and off seasons. Panel A (Bottom Farm, Non-conducive) shows higher diversity in the cotton-growing season. Panel B (Stiles Farm, Conducive) shows similar diversity between the two seasons.

Figure 7. Comparison of bacterial diversity at the Bottom Farm (A) and Stiles Farm (B) between the off-season and 2024 cotton-growing season. Off-season bacterial Shannon diversity was significantly (p<0.001) higher at the Bottom Farm. “*” represents a significant difference.

Figure 8
Box plots compare fungal Shannon diversity in cotton-growing and off seasons. Panel A shows Bottom Farm, labeled non-conducive, with similar diversity in both seasons. Panel B displays Stiles Farm, labeled conducive, where diversity is higher in the off-season.

Figure 8. Comparison of fungal diversity at the Bottom Farm (A) and Stiles Farm (B) between the off-season and 2024 cotton-growing season. Off-season fungal Shannon diversity was significantly (p<0.001) higher at the Stiles Farm. “*” represents a significant difference.

There were significant differences between the cotton-growing and off season among the 11 most abundant bacterial orders averaged across samples in each of the sclerotia treatments and bulk soil (Supplementary Table S1). At the Bottom Farm, bacteria in the orders Hyphomicrobiales and Acidobacteria Gp6 incertae sedis had a significantly higher relative abundance during the off-season than in the cotton-growing season (Figure 9A). On the other hand, bacteria in the orders Solirubrobacterales, Rubrobacterales, and Unclassified Actinomycetota had a significantly higher relative abundance during the cotton-growing season than in the off-season at the Bottom Farm (Figure 9A). At the Stiles Farm, bacteria in the orders Gaiellales, Hyphomicrobiales, and Acidobacteria Gp6 incertae sedis were found in a significantly higher relative abundance in the off-season than in the cotton-growing season (Figure 9B). Conversely, at the Stiles Farm, bacteria in the orders Unclassified Bacteria, Caryophanales, Unclassified Actinomycetota, and Gemmatimonadales had a significantly higher relative abundance during the cotton-growing season than the off-season (Figure 9B).

Figure 9
Heatmaps comparing the relative abundance of the top eleven bacterial orders at two farms across seasons. Panel A shows the Bottom Farm (non-conducive), while Panel B shows the Stiles Farm (conducive). Both maps use a gradient from light to dark red, indicating increasing relative abundance percentages, across conditions such as In-season and Off-season for Live Sclerotia, Heat-killed Sclerotia, and Bulk Soil.

Figure 9. Heatmaps displaying diversity within location and season. Bolded orders are significantly (p<0.05) different between the cotton-growing and off season. “(Off)” or “(In)” after a bolded order indicates which season had a significantly higher relative abundance of that order. Comparison of bacterial communities at the Bottom Farm (A) and Stiles Farm (B).

With fungal communities, there were significant differences between the cotton-growing and off season among the five most abundant fungal orders averaged across samples in each of the sclerotia treatments and bulk soil (Supplementary Table S2). At the Bottom Farm, fungi in the orders Hypocreales and Pleosporales had a significantly higher relative abundance during the off-season when compared to the cotton-growing season (Figure 10A). Also at the Bottom Farm, fungi in the orders Eurotiales, Sordariales, and Ascomycota order Incertae sedis had a significantly higher relative abundance during the cotton-growing season when compared to the off-season (Figure 10A). At the Stiles Farm, fungi in the orders Hypocreales, Pleosporales, and Capnodiales had a significantly higher relative abundance during the off-season when compared to the cotton-growing season (Figure 10B). Conversely, at the Stiles Farm, fungi in the order Eurotiales were found in a significantly higher relative abundance during the cotton-growing season when compared to the off-season (Figure 10B). The full breadth of alpha diversity compared between the 2023–2024 off-season and 2024 cotton-growing season, at the order level, is shown in Supplementary Figure S9 for bacterial communities and Supplementary Figure S10 for fungal communities.

Figure 10
Two heat maps compare the relative abundance of the top five fungal orders at Bottom Farm and Stiles Farm. Panel A shows data for Bottom Farm (Non-conducive) and Panel B for Stiles Farm (Conducive). Both maps use a gradient from light to dark red, indicating increasing relative abundance percentages, across conditions such as In-season and Off-season for Live Sclerotia, Heat-killed Sclerotia, and Bulk Soil.

Figure 10. Heatmaps displaying diversity within location and season. Bolded orders are significantly (p<0.05) different between the cotton-growing and off season. “(Off)” or “(In)” after a bolded order indicates which season had a significantly higher relative abundance of that order. Comparison of fungal communities at the Bottom Farm (A) and Stiles Farm (B).

Taxa exclusively enriched in live sclerotia communities (both in the growing season and off-season) and not enriched in bulk soil communities were identified, based on the LEfSe analyses. At the Bottom Farm, five genera met these criteria: Virgisporangium, Rubrobacter, Robertmurraya, Neobacillus, and Arboricoccus. At the Stiles Farm, 10 genera met the criteria: Oxalophagus, Oscillochloris, Neobacillus, Microlunatus, Metabacillus, Gp4, Ectobacillus, Archangium, Arboricoccus, and Amycolatopsis. For fungal communities, no genera met these criteria at either location.

3.4 Comparison of communities over three seasons at the Stiles Farm

Evaluation of bacterial and fungal communities at the Stiles Farm for approximately nine months facilitated observation of changes in P. omnivora sclerotia-associated communities over time. A microbial order was considered differentially abundant between the cotton-growing seasons and the off-season if average relative abundance decreased from the 2023 cotton-growing season to the off-season, then increased from the off-season to the 2024 cotton-growing season, or vice versa. Change over time in the top 10 most abundant bacterial orders, associated with live sclerotia, can be seen in Supplementary Table S3. Of these 10 orders, two were differentially abundant between the cotton-growing seasons and the off-season: Acidobacteria Gp6 incertae sedis and Gaiellales. For both orders, average relative abundance increased from the 2023 cotton-growing season to the off-season, then decreased from the off-season to the 2024 cotton-growing season. In both cases, the average relative abundance of bacteria in the orders was significantly higher in the off-season than in both cotton-growing seasons. Change over time in the top 10 most abundant bacterial orders, associated with heat-killed sclerotia, can be seen in Supplementary Table S3. Of these 10 orders, five were differentially abundant between the cotton-growing seasons and the off-season: Acidimicrobiales, Acidobacteria Gp6 incertae sedis, Gaiellales, Micromonosporales, and Rubrobacterales. In bacteria classified in Acidimicrobiales, Micromonosporales, and Rubrobacterales, the average relative abundance decreased from the 2023 cotton-growing season to the off-season, then increased from the off-season to the 2024 cotton-growing season. In bacteria classified in Acidobacteria Gp6 incertae sedis and Gaiellales, average relative abundance increased from the 2023 cotton-growing season to the off-season, then decreased from the off-season to the 2024 cotton-growing season. Change over time in the top 10 most abundant bacterial orders, associated with bulk soil, can be seen in Supplementary Table S3. Of these 10 orders, seven were differentially abundant between the cotton-growing seasons and the off-season: Acidimicrobiales, Caryophanales, Gaiellales, Micromonosporales, Rhodospirillales, Rubrobacterales, and Solirubrobacterales. In bacteria classified in Acidimicrobiales, Rhodospirillales, and Rubrobacterales, average relative abundance decreased from the 2023 cotton-growing season to the off-season, then increased from the off-season to the 2024 cotton-growing season. In bacteria classified in Caryophanales, Gaiellales, Micromonosporales, and Solirubrobacterales, average relative abundance increased from the 2023 cotton-growing season to the off-season, then decreased from the off-season to the 2024 cotton-growing season. The differences in the relative abundance of bacterial communities associated with bulk soil were numerically different over time, but not statistically.

Change over time in the top six most abundant fungal orders, associated with live sclerotia, can be seen in Supplementary Table S4. Of the six orders, only one was differentially abundant between the cotton-growing seasons and the off-season: Sordariales. Fungi in the order Sordariales increased in average relative abundance from the 2023 cotton-growing season to the off-season, then decreased from the off-season to the 2024 cotton-growing season, but the change was not significantly different. Change over time in the top six most abundant fungal orders, associated with heat-killed sclerotia, can be seen in Supplementary Table S4. Of the six orders, two were differentially abundant between the cotton-growing seasons and the off-season: Hypocreales and Sordariales. Fungi in both of these orders increased from the 2023 cotton-growing season to the off-season, and then decreased from the off-season to the 2024 cotton-growing season, but these changes were not statistically significant. Change over time in the top six most abundant fungal orders, associated with bulk soil, can be seen in Supplementary Table S4. Of the six orders, three were differentially abundant between the cotton-growing seasons and the off-season: Capnodiales, Hypocreales, and Pleosporales. Fungi in Capnodiales and Pleosporales increased from the 2023 cotton-growing season to the off-season, then decreased from the off-season to the 2024 cotton-growing season. Conversely, fungi in the order Hypocreales decreased from the 2023 cotton-growing season to the off-season, then increased from the off-season to the 2024 cotton-growing season. These differences in relative abundance over time were not statistically significant.

4 Discussion

This study provides the first comprehensive look at P. omnivora sclerotia-associated microorganisms in soils with contrasting histories of support for CRR, as well as documents how these communities change over time. The findings demonstrate that microbial communities differ in both diversity and composition across locations, seasons, and treatments. Specifically, microbial diversity was consistently higher at the Bottom Farm compared to the Stiles Farm. This was particularly evident in bacterial communities during the off-season and in both bacterial and fungal communities during the 2024 cotton-growing season. Given the absence of CRR at the Bottom Farm, this observation aligns with previous findings that associate increased microbial diversity with reduced CRR incidence (Chavez et al., 1976; Streets and Bloss, 1973). These findings suggest that part of the Bottom Farm’s lack of CRR could be due to its microbial diversity. This hypothesis could be tested by incorporating green manure at varying rates into a CRR-infested field, followed by observing CRR progression in that field subsequently planted with cotton, as was done by Chavez et al. (1976), and then evaluating soil microflora using metabarcoding. Such an experiment could clarify the link between microbial diversity and CRR incidence, providing non-microbial soil properties are not substantially changed by treatments. This study provides insight beyond community diversity metrics that show how microbial communities associated with P. omnivora sclerotia are qualitatively different between location and season, as well as quantitatively different when it comes to the relative abundance of microbial taxa found in both locations and seasons.

A core hypothesis of this study was that live sclerotia of P. omnivora selectively recruit particular microbial taxa. To investigate this, we used LEfSe analysis to identify microbial biomarkers enriched in live sclerotia relative to bulk soil and heat-killed sclerotia, and used βNTI to assess the nature of the community assembly processes. The LEfSe results show several bacterial and fungal genera are significantly enriched in live sclerotia across both seasons and test locations. During the off-season at the CRR non-conducive Bottom Farm, OTUs that belong to the bacterial genera such as Virgisporangium, Skermanella, Marmoricola, and fungal genera like Paecilomyces and Colletotrichum were enriched in live sclerotia. However, at the conducive Stiles Farm, Stenotrophobacter, Alternaria, and Preussia were among the enriched taxa. Many of these genera, particularly Paecilomyces, are known producers of secondary metabolites including antibiotics, antifungals, and nematocidal compounds (Hirota et al., 1991; Dai et al., 2020; Shi et al., 2025). The presence of actinobacteria such as Marmoricola and Virgisporangium aligns with broader patterns seen in sclerotia-forming pathogens like Sclerotinia sclerotiorum, where actinobacteria often act as early colonizers or antagonists. In the 2024 cotton-growing season, live sclerotia continued to enrich distinct taxa. At the Bottom Farm, bacterial genera Cellulomonas and Robertmurraya, along with fungal genera Paecilomyces and Mycoleptodiscus, were dominant. At the Stiles Farm, Metabacillus, Domibacillus, and Coniocessia were enriched. Notably, many of these genera are culturable, facilitating future mechanistic studies.

During both the 2023–2024 off-season and the 2024 cotton-growing season, representation of the genus Pseudomonas and members of the class Actinobacteria was evaluated because of findings by Zuberer et al. (1988) in which fluorescent pseudomonads and actinomycetes were found in association with P. omnivora sclerotia. The present study also found those groups of bacteria in association with live P. omnivora sclerotia, but as a low percentage of the community. This illustrates the ability of sequencing methods to more comprehensively identify the makeup of microbial communities, as compared to methods relying on selective media alone.

At the Stiles Farm, the three-season comparison (2023 cotton-growing season, 2023–2024 off-season, 2024 cotton-growing season) noted a snapshot of temporal dynamics. Some bacterial orders, such as Acidobacteria Gp6 incertae sedis and Gaiellales, showed consistent seasonal shifts, increasing in the off-season and decreasing during the growing season. However, not all patterns were conserved across niches. For instance, Rubrobacterales OTUs increased in abundance in bulk soil and heat-killed sclerotia communities during cotton seasons, but not in live sclerotia communities. Such differences suggest that live sclerotia may represent a distinct ecological niche with unique seasonal dynamics. Fungal communities also shifted seasonally but less consistently across treatments. Orders such as Sordariales were enriched in off-season sclerotia treatments but not in bulk soil. In contrast, fungi in Capnodiales and Pleosporales were more abundant in off-season bulk soils but not in sclerotia. These observations further suggest that fungal community dynamics are more stochastic and niche-specific compared to bacterial counterparts.

βNTI metrics are more recent indices used to evaluate deterministic selection in microbiome communities. This test helps evaluate whether a community structure is random or has been guided by a specific recruitment strategy. Specifically, it helps compare the observed phylogenetic dissimilarity between communities to a null distribution generated through randomizations, thereby allowing inference about the relative influence of deterministic versus stochastic assembly mechanisms. A βNTI value greater than +2.0 indicates that the phylogenetic composition of communities is more dissimilar than expected by chance, whereas value less than −2.0 reflects more phylogenetically similarity than expected under stochastic assembly models. Across all bacterial communities (live and heat-killed sclerotia and bulk soil), βNTI values were strongly negative ranging from -4.3 to -5.2, suggesting deterministic assembly driven by environmental filtering or host selection. In contrast, fungal βNTI values hovered between -1.0 and -1.7, indicating stochastic assembly dominated by random colonization or dispersal. While deterministic selection is expected in structured niches such as live and dead sclerotia, the observation of strongly negative βNTI values in bulk soil was unexpected. This pattern suggests that even bulk soil exerts a consistent selection pressure on bacterial communities. Such homogeneity may be driven by uniform soil physicochemical conditions, recurring plant-derived inputs (e.g., root exudates), or the residual effects of crop-associated organic matter. Although these factors likely contribute to the observed pattern, their specific roles remain unresolved within the scope of this study.

Microbial community comparisons between the 2023–2024 off-season and the 2024 cotton-growing season demonstrated the set of taxa that may be responsible for differences in CRR occurrence at the locations of interest. The comparison across communities allowed for the selection of genera that were enriched in live sclerotia, specifically in live sclerotia during the cotton-growing season. If the absence of CRR in some soils is microbially mediated, those microorganisms would be expected to be most active during the months when CRR manifests in the field. At the Bottom Farm, five bacterial genera met the enrichment criteria, including Rubrobacter, a member of the thermophilic order Rubrobacterales, that showed significantly higher relative abundance during the cotton-growing season. Given their thermotolerance (Albuquerque and da Costa, 2014), the higher relative abundance during the summer months is not unexpected. Although not associated with orders differing in relative abundance between the seasons, the selected genera Virgisporangium and Neobacillus may show functional relevance for competition with fungal pathogens. Characteristics of Virgisporangium are not well known, and the possibility of antibiotic production should be evaluated, as other members of the Actinomycetes produce such compounds. The genus Neobacillus was recently reclassified from the genus Bacillus, a genera noted for their secondary metabolic potential along with effects on plant growth (Kloepper et al., 2007), fungal modulation (Anckaert et al., 2024), and overall microbiome alterations (Stein, 2005; Adesemoye et al., 2025). Neobacillus was also enriched in live sclerotia communities during the cotton-growing season at the Stiles Farm, which is conducive to CRR. At the Stiles Farm, ten bacterial genera met the enrichment criteria, though none belonged to orders with seasonally differential abundance. Notably, all enriched bacterial genera from both locations are described in the literature as culturable.

The comparison of microbial communities at the Stiles Farm over three seasons allowed for the investigation of microorganisms that are differentially abundant between the cotton-growing and off seasons for each of the niches evaluated in this study. There were some bacterial orders that exhibited different seasonal shifts between the niches. Acidobacteria Gp6 incertae sedis was found at a higher relative abundance during the off-season for the sclerotia treatments, but this was not the case in bulk soil. Acidobacteria are well-known oligotrophs and perhaps their higher presence in off-season sclerotia is due to the low nutrient environment, outcompeting copiotrophs. However, Acidimicrobiales and Rubrobacterales as also oligotrophs but were found at a higher relative abundance during the cotton-growing seasons in the heat-killed sclerotia and bulk soil communities, but not the live sclerotia communities. Micromonosporales was found at a higher relative abundance during the cotton-growing seasons for heat-killed sclerotia communities, but was more abundant during the off-season in bulk soil. However, this could be due to their high stress-tolerance and, as mentioned earlier, might enable actinobacterial orders such as these to thrive. Caryophanales and Solirubrobacterales were found at a higher relative abundance during the off-season in bulk soil communities, but not in the sclerotia treatments. Among the aforementioned differences in seasonal shifts by niche, Gaiellales was the only order that was differentially abundant in the same way across the sclerotia treatments and bulk soil.

5 Conclusions

Overall, this study presents the first detailed characterization of microorganisms associated with P. omnivora sclerotia in different cotton-producing soils. Microbial diversity was higher at the non-conducive Bottom Farm, especially during the off-season and 2024 cotton-growing season, aligning with the hypothesis that greater microbial diversity contributes to disease suppression. LEfSe analyses revealed site- and season-specific microbial taxa enriched in live sclerotia. At the Bottom Farm, genera such as Paecilomyces, Marmoricola, and Virgisporangium were abundant. At the Stiles Farm, taxa like Stenotrophobacter and Alternaria dominated. These genera, including culturable ones like Neobacillus and Metabacillus, are known for antimicrobial potential. Further investigation of the culturable bacteria and fungi identified in this study should be evaluated in vitro for the ability to either suppress or encourage the growth of P. omnivora. βNTI values showed deterministic bacterial assembly across treatments, even in bulk soil, while fungal communities appeared stochastically assembled. This suggests a conditional selective recruitment where bacteria are selectively enriched on active sclerotia, while fungal recruitment is less structured. The seasonal shifts in specific bacterial orders (e.g., Rubrobacterales, Acidobacteria Gp6) and fungal taxa (e.g., Sordariales) highlighted niche- and time-dependent dynamics. These patterns parallel those observed in sclerotia communities of other pathogens like Sclerotinia and Rhizoctonia. Our findings support the view that P. omnivora sclerotia serve as ecological hubs, shaping microbial communities with possible implications for disease suppression. Several enriched taxa are culturable, offering candidates for future biocontrol studies.

Data availability statement

The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found below: https://www.ncbi.nlm.nih.gov/, BioProject PRJNA1289165.

Author contributions

MS: Conceptualization, Data curation, Formal Analysis, Investigation, Visualization, Writing – original draft. SA: Conceptualization, Methodology, Resources, Validation, Writing – review & editing. EP: Conceptualization, Writing – review & editing. TC: Conceptualization, Writing – review & editing. TI: Conceptualization, Funding acquisition, Methodology, Writing – review & editing.

Funding

The author(s) declare financial support was received for the research and/or publication of this article. Cotton Incorporated (Texas State Support Committee) grant 20-575TX and USDA National Institute of Food and Agriculture Hatch project 1025739.

Acknowledgments

We thank Texas A&M University farm managers Ryan Collett and Stephen Labar for helping to coordinate the sclerotia burial locations, as well as Vanessa Thomas for her consultation on analysis methods.

Conflict of interest

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.

The author(s) declared that they were an editorial board member of Frontiers, at the time of submission. This had no impact on the peer review process and the final decision.

Generative AI statement

The author(s) declare that no Generative AI was used in the creation of this manuscript.

Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.

Publisher’s note

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.

Supplementary material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/frmbi.2025.1666691/full#supplementary-material

References

Abarenkov K., Zirk A., Piirmann T., Pöhönen R., Ivanov F., Nilsson R. H., et al. (2021). Full mothur UNITE+INSD dataset 1. Version 10.05.2021 ( University of Tartu, Estonia: UNITE Community). doi: 10.15156/BIO/1279042

Crossref Full Text | Google Scholar

Adesemoye A. O., Antony-Babu S., Nagy E. M., Kafle B. D., Gregory T. A., Xiong C., et al. (2025). Bacteria-based artificial diets modulate larval development, survival and gut microbiota of two insect pests. Biol. Control 205, 105769. doi: 10.1016/j.biocontrol.2025.105769

Crossref Full Text | Google Scholar

Albuquerque L. and da Costa M. S. (2014). “The family Rubrobacteraceae,” in The Prokaryotes (Berlin: Springer-Verlag Berlin Heidelberg), 861–866.

Google Scholar

Anckaert A., Declerck S., Poussart L.-A., Lambert S., Helmus C., Boubsi F., et al. (2024). The biology and chemistry of a mutualism between a soil bacterium and a mycorrhizal fungus. Curr. Biol. 34, 4934–4950. doi: 10.1016/j.cub.2024.09.019

PubMed Abstract | Crossref Full Text | Google Scholar

Antony-Babu S., Abeysinghe G., Thomas V. E., Hockenbury C., Parunandi S. S., Dasgupta A., et al. (2025). Integrated metabarcoding and culture-dependent assessments reveal Pseudomonas as dominant hyphosphere-pathobiont in Race 4 Fusarium wilt pathogen of cotton. Front. Microbiol. 16. doi: 10.3389/fmicb.2025.1661556

PubMed Abstract | Crossref Full Text | Google Scholar

Chavez H. B., Bloss H. E., Boyle A. M., and Gries G. A. (1976). Effects of crop residues in soil on Phymatotrichum root rot of cotton. Mycopathologia 58, 1–7. doi: 10.1007/BF00493585

Crossref Full Text | Google Scholar

Dai Z.-B., Wang X., and Li G.-H. (2020). Secondary metabolites and their bioactivities produced by Paecilomyces. Molecules 25, 5077. doi: 10.3390/molecules25215077

PubMed Abstract | Crossref Full Text | Google Scholar

de Boer W., Folman L. B., Summerbell R. C., and Boddy L. (2005). Living in a fungal world: impact of fungi on soil bacterial niche development. FEMS Microbiol. Rev. 29, 795–811. doi: 10.1016/j.femsre.2004.11.005

PubMed Abstract | Crossref Full Text | Google Scholar

Dunlap A. A. (1941). A convenient soil-culture method for obtaining sclerotia of the cotton root rot fungus. Am. J. Bot. 28, 945–957. doi: 10.1002/j.1537-2197.1941.tb11027.x

Crossref Full Text | Google Scholar

Faske T. and Sisson A. (2025). Cotton disease loss estimates from the United States – 2024 (Ames, IA: Crop Protection Network). doi: 10.31274/cpn-20250310-0

Crossref Full Text | Google Scholar

Fritsche K., Leveau J. H. J., Gerards S., Ogawa S., de Boer W., and van Veen J. A. (2006). Collimonas fungivorans and bacterial mycophagy. Bull. OILB/SROP 29, 27–29.

Google Scholar

Hirota A., Nakagawa M., and Hirota H. (1991). Structure of Paecilospirone, a new antibiotic from Paecilomyces. Agric. Biol. Chem. 55, 1187–1188. doi: 10.1080/00021369.1991.10870698

Crossref Full Text | Google Scholar

Isakeit T. (2021). Cotton root rot (Phymatotrichopsis root rot) and its management. Texas A&M Agrilife Extension. Available online at: https://agrilifelearn.tamu.edu/s/product/cotton-root-rot-phymatotrichopsis-root-rot-and-its-management/01t4x000002dByhAAE (accessed November 18, 2025).

Google Scholar

Jakuschkin B., Fievet V., Schwaller L., Fort T., Robin C., and Vacher C. (2016). Deciphering the pathobiome: intro- and interkingdom interactions involving the pathogen Erysiphe alphitoides. Microbial Ecol. 72, 870–880. doi: 10.1007/s00248-016-0777-x

PubMed Abstract | Crossref Full Text | Google Scholar

Jamil F. N., Hashim A. M., Yusof M. T., and Saidi N. B. (2023). Association of soil fungal community composition with incidence of Fusarium wilt of banana in Malaysia. Mycologia 115, 178–186. doi: 10.1080/00275514.2023.2180975

PubMed Abstract | Crossref Full Text | Google Scholar

Jochum L. and Stecher B. (2020). Label or concept – what is a pathobiont? Trends Microbiol. 28, 789–792. doi: 10.1016/j.tim.2020.04.011

PubMed Abstract | Crossref Full Text | Google Scholar

Kloepper J. W., Ryu C.-M., and Zhang S. (2007). Induced systemic resistance and promotion of plant growth by Bacillus spp. Phytopathology 94, 1259–1266. doi: 10.1094/PHYTO.2004.94.11.1259

PubMed Abstract | Crossref Full Text | Google Scholar

Lee S.-M., Kong H. G., Song G. C., and Ryu C.-M. (2021). Disruption of Firmicutes and Actinobacteria abundance in tomato rhizosphere causes the incidence of bacterial wilt disease. ISME J. 15, 330–347. doi: 10.1038/s41396-020-00785-x

PubMed Abstract | Crossref Full Text | Google Scholar

Leveau J. H. J. and Preston G. M. (2008). Bacterial mycophagy: definition and diagnosis of a unique bacterial-fungal interaction. New Phytol. 177, 859–876. doi: 10.1111/j.1469-8137.2007.02325.x

PubMed Abstract | Crossref Full Text | Google Scholar

Liu C., Cui Y., Li X., and Yao M. (2021). microeco: an R package for data mining in microbial community ecology. FEMS Microbiol. Ecol. 97, fiaa255. doi: 10.1093/femsec/fiaa255

PubMed Abstract | Crossref Full Text | Google Scholar

Moses D. and Carter M. (2025). A plant health view on endohyphal bacteria and their fungal hosts. Phytobiomes first look. 9, 354–358. doi: 10.1094/PBIOMES-12-24-0117-MRVW

Crossref Full Text | Google Scholar

Obasa K., Adesemoye A., Obasa R., Moraga-Amador D., Shinogle H., Alvarez S., et al. (2019). Endohyphal bacteria associated with virulence, increased expression of fumonisin biosynthetic genes, and production of fumonisin and macroconidia in Fusarium fujikuroi W343. Plant Pathol. 69, 87–100. doi: 10.1111/ppa.13107

Crossref Full Text | Google Scholar

Percy R.G. (1983). Potential range of Phymatotrichum omnivorum as determined by edaphic factors. Plant Dis. 67, 981–983.

Google Scholar

Quast C., Pruesse E., Yilmaz P., Gerken J., Schweer T., Yarza P., et al. (2013). The SILVA ribosomal RNA gene database project: improved data processing and web-based tools. Nucleic Acids Res. 41, D590–D596. doi: 10.1093/nar/gks1219

PubMed Abstract | Crossref Full Text | Google Scholar

Schloss P. D., Westcott S. L., Ryabin T., Hall J. R., Hartmann M., Hollister E. B., et al. (2009). Introducing mothur: open-source, platform-independent, community-supported software for describing and comparing microbial communities. Appl. Environ. Microbiol. 75, 7537–7541. doi: 10.1128/AEM.01541-09

PubMed Abstract | Crossref Full Text | Google Scholar

Segata N., Izard J., Waldron L., Gevers D., Miropolsky L., Garrett W. S., et al. (2011). Metagenomic biomarker discovery and explanation. Genome Biol. 12, R60. doi: 10.1186/gb-2011-12-6-r60

PubMed Abstract | Crossref Full Text | Google Scholar

Shi W., Li M., Wei G., Tian R., Li C., Wang B., et al. (2019). The occurrence of potato common scab correlates with the community composition and function of the geocaulosphere soil microbiome. Microbiome 7, 14. doi: 10.1186/s40168-019-0629-2

PubMed Abstract | Crossref Full Text | Google Scholar

Shi X.-C., Zhou Y.-X., Yang J.-B., Mei D.-Z., Xu L.-Y., Wang S.-Y., et al. (2025). Biocontrol mechanisms of Paecilomyces spp. for the management of fungal plant diseases: a review. Pest Manage. Sci. 81, 4200–4219. doi: 10.1002/ps.8872

PubMed Abstract | Crossref Full Text | Google Scholar

Stein T. (2005). Bacillus subtilis antibiotics: structures, syntheses and specific functions. Mol. Microbiol. 56, 845–857. doi: 10.1111/j.1365-2958.2005.04587.x

PubMed Abstract | Crossref Full Text | Google Scholar

Streets R. B. and Bloss H. E. (1973). Phymatotrichum root rot (St. Paul, MN: American Phytopathological Society Monograph No. 8).

Google Scholar

Thomas V. E., Abeysinghe G., Goetze P. K., Jo Y.-K., and Antony-Babu S. (2025). The distinguished microbiome: differentiating microbial dysbiosis and the pathobiome of banana Fusarium tropical Race 4. Phytobiomes first look. doi: 10.1094/PBIOMES-10-24-0097-R

Crossref Full Text | Google Scholar

Thomas V. E. and Antony-Babu S. (2024). Core hyphosphere microbiota of Fusarium oxysporum f. sp. niveum. Environ. Microbiome 19, 14. doi: 10.1186/s40793-024-00558-5

PubMed Abstract | Crossref Full Text | Google Scholar

USDA NRCS Web soil survey. Available online at: https://websoilsurvey.nrcs.usda.gov/app/ (accessed November 18, 2025).

Google Scholar

Vayssier-Taussat M., Albina E., Citti C., Cosson J.-F., Jacques M.-A., Lebrun M.-H., et al. (2014). Shifting the paradigm from pathogens to pathobiome: new concepts in the light of meta-omics. Front. Cell. Infection Microbiol. 4. doi: 10.3389/fcimb.2014.00029

PubMed Abstract | Crossref Full Text | Google Scholar

Wang Q., Garrity G. M., Tiedje J. M., and Cole J. R. (2007). Naïve Bayesian classifier for rapid assignment of rRNA sequences into the new bacterial taxonomy. Appl. Environ. Microbiol. 73, 5261–5267. doi: 10.1128/AEM.00062-07

PubMed Abstract | Crossref Full Text | Google Scholar

Xiong W., Li R., Ren Y., Liu C., Zhao Q., Wu H., et al. (2017). Distinct roles for soil fungal and bacterial communities associated with the suppression of vanilla Fusarium wilt disease. Soil Biol. Biochem. 107, 198–207. doi: 10.1016/j.soilbio.2017.01.010

Crossref Full Text | Google Scholar

Yin C., Casa Vargas J. M., Schlatter D. C., Hagerty C. H., Hulbert S. H., and Paulitz T. C. (2021). Rhizosphere community selection reveals bacteria associated with reduced root disease. Microbiome 9, 86. doi: 10.1186/s40168-020-00997-5

PubMed Abstract | Crossref Full Text | Google Scholar

Zuberer D. A., Kenerley C. M., and Jeger M. J. (1988). Populations of bacteria and actinomycetes associated with sclerotia of Phymatotrichum omnivorum buried in Houston black clay. Plant Soil 112, 69–76. doi: 10.1007/BF02181754

Crossref Full Text | Google Scholar

Keywords: Phymatotrichopsis omnivora, sclerotia-associated microorganisms, cotton, Gossypium hirsutum, cotton root rot

Citation: Sturdivant M, Antony-Babu S, Pierson E, Chappell TM and Isakeit T (2025) Identification of microbial communities associated with Phymatotrichopsis omnivora sclerotia in two Texas fields. Front. Microbiomes 4:1666691. doi: 10.3389/frmbi.2025.1666691

Received: 15 July 2025; Accepted: 05 November 2025; Revised: 29 September 2025;
Published: 28 November 2025.

Edited by:

Sharareh Harirchi, Iranian Research Organization for Science and Technology, Iran

Reviewed by:

Venkateswara Rao Sripathi, Alabama Agricultural and Mechanical University, United States
Sowndarya Karapareddy, Alabama Agricultural and Mechanical University, United States

Copyright © 2025 Sturdivant, Antony-Babu, Pierson, Chappell and Isakeit. 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.

*Correspondence: Thomas Isakeit, VGhvbWFzLklzYWtlaXRAYWcudGFtdS5lZHU=

ORCID: Thomas M. Chappell, orcid.org/0000-0003-1399-5468

Disclaimer: 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.