Abstract
Drought stress has a significant impact on agricultural productivity, affecting key crops such as
soybeans, the second most widely cultivated crop in the United States. We conducted endophytic
and rhizospheric microbial diversity analyses in soybean plants cultivated during the 2023
growing season, amid extreme weather conditions of prolonged high temperatures and drought in
Louisiana. Specifically, we collected surviving and non-surviving soybean plants from two plots
of a Louisiana soybean field severely damaged from the extreme heat and drought condition in
2023. We did not observe any significant difference in the microbial diversity of rhizosphere
between surviving and non-surviving plants. However, we found obvious differences in the
structure of endophytic microbial community in root tissues between the two plant conditions.
Especially, the bacterial genera of Proteobacteria, Pseudomonas and Pantoea, were predominant
in the surviving root tissues, while the bacterial genus Streptomyces was conspicuously dominant
in the non-surviving (dead) root tissues. Co-occurrence patterns and network centrality analyses
enabled us to discern the intricate characteristics of operational taxonomic units (OTUs) within
endophytic and rhizospheric networks. Overall, this study advances our understanding of the
intricate relationship between bacteria and plants under drought stress, paving the way for future
research to investigate the importance of microbial diversity in drought affected regions such as
Louisiana.
Introduction
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Drought stress is one of the most important environmental factors that significantly impact
agricultural productivity, leading to a potential yield loss of 50% yield loss [1, 2]. This can have
severe implications for global feed security. The second most widely cultivated crop in the
United States is soybeans, representing 32% of the overall cultivated land. However, under
drought conditions, soybeans can experience a reduction in yield of up to 100% [1]. As the crisis
of global climate change continues to escalate, the frequency and severity of drought events are
intensifying, presenting a greater threat to crop yields and overall agricultural sustainability.
Consequently, understanding the mechanisms underlying plant responses to drought stress is
imperative for developing resilient soybean varieties and implementing effective management
strategies. Utilizing beneficial microbes has emerged as a promising approach to enhance crop
resilience against environmental stress, including drought [3].
Assessing the microbial diversity and population of both endophytes and the rhizosphere in crop
plants across various environments is crucial to harnessing their potential use in enhancing plant
growth and resilience against both biotic and abiotic stress [3]. The progress in high-throughput
sequencing and bioinformatics tools allows for the evaluation of operational taxonomic units
(OTU), amplicon sequence variants (ASV), or species, along with their respective abundances
[4]. Leveraging correlation-based and graphical models, among other methods, co-occurrence
network analysis is applied to illustrate microbial relationships within diverse spatiotemporal
niches [5]. Meanwhile, network topological features i.e. modularity and connectivity, and several
of such network parameters can serve as indicators of significant nodes in the network [6]. These
encompass degree, indicating the number of connections a node possesses; betweenness,
representing the fraction of the shortest paths passing through a node, among other centrality
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measures [7]. Recently, weight k-shell decomposition network analysis was shown to be more
effective in discovering fast information-spreading nodes [8].
During the 2023 growing season, most regions of Louisiana experienced extreme weather
conditions of high temperature and drought for an unprecedentedly extended period. From these
abnormally hot and dry weather conditions, some of the soybean fields at the Dean Lee Research
Station of the LSU AgCenter in Alexandria, Louisiana, exhibited devastating damages and most
of the plants could not survive, causing a more than 90% yield loss (Fig. 1). The primary
Objective
of this study is to investigate the microbiome structure of soybean roots under natural
drought and heat stresses in the field, particularly during this year's severe environmental
growing season. As there were no healthy plants at a similar growth stage cultivated in nearby
well-irrigated plots, soybean plants were collected from two damaged plots only. However, both
surviving and non-surviving plants were sampled from each plot for comparative analysis.
This report describes the prokaryotic microbiome structures associated with the soybean roots
that survived the natural heat and drought stresses in the field condition of central Louisiana
during the 2023 growing season, compared with those from non-surviving plants in the same plot.
We present here the alpha and beta diversity and the co-occurrence network of the microbiome
structures based on the 16S ribosomal DNA (16S rDNA) sequence data. We also discuss here the
main characteristics of the microbiome associated with the hot and dry field conditions.
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Figure 1. The drought-damaged soybean field where the plant samples were collected
(Alexandria, Louisiana). Plot A and Plot B were neighboring each other.
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Materials and methods
Plant Sample Collection and Preservation
Soybean plant samples were collected from two neighboring plots (Plot A and Plot B) at the
Dean Lee Research Station, Alexandria, Louisiana (31.11oN, 92.24 oW), which were severely
damaged from the extended period of high temperatures and dry weather conditions during
the 2023 growing season (Figures 1 and 2). Five surviving and five dead plants were collected
at the R6-R7 stage (~ 4 months after planting) from both Plot A and Plot B, totaling ten plant
samples per plot. Plot A experienced severe drought stress, resulting in the survival of only a few
green plants, while Plot B exhibited less severe drought stress with more green plants than Plot A
(Figure 1). Soil types in both plots included Latanier silty clay loam at the front and Moreland
clay at the back. Tillage was conducted in March, and the planting was done on May 4, 2023, for
both plots. Different crop varieties were cultivated in each plot: AG49XF3 (Bayer CropScience)
for Plot A and P5554RX (Progeny Ag) for Plot B. The collected plant and soil samples were
carefully encased in large plastic bags and transported to the laboratory, where they were
temporarily stored in a cold room at 4
0C before processing.
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Figure 2. The records of the rainfalls (A) and temperatures (B) in Alexandria, Louisiana, during
the 2023 growing season. These graphs were obtained from Weather Spark
(https://weatherspark.com).
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Field Management
Insecticide and herbicide applications In both plots, insecticides were applied on two dates:
Moccasin MTZ (United Phosphorous, PA, USA) on July 17, 2023, at a rate of 0.41 ml/m2, and
Endigo (Syngenta, DE, USA) on July 24, 2023, at a rate of 0.033 ml/m2. Herbicide applications
were administered on May 8, 2023, with Varsity (Innvictis Crop Care, Idaho, USA) at a rate of
0.015 ml/m2, Derive (Innvictis Crop Care, Idaho, USA) at a rate of 0.045 ml/m2, Zidua (BASF
Agricultural Solutions, LA, USA) at a rate of 0.018 ml/m2, and Fever (Innvictis Crop Care, Idaho,
USA) at a rate of 0.234 ml/m2. Charger Max (WinField United, MN, USA) was applied at a rate
of 0.146 ml/m2 on May 9, 2023, and on June 15, 2023, Sentris (BASF Agricultural Solutions, LA,
USA) at a rate of 0.06 ml/m2, Engenia (BASF Agricultural Solutions, LA, USA) at a rate of 0.09
ml/m2, and Roundup Powermax (Bayer Crop Science, MO, USA) at a rate of 0.23 ml/m2 were
administered.
Fungicide and fertilizer applications On June 30, 2023, a fungicide, Stratego Yield (Bayer
CropScience, MO, USA), was applied at a rate of 0.034 ml/m2 grams in both fields,
supplemented with a 0.25% nonionic surfactant. The fertilizer used in both fields was a
composition of N-P-K at 0-18-36.
DNA sample preparation
For DNA extraction from the rhizospheric soil, the soil closely attached to the plant roots was
collected in 50 ml falcon tubes using a sterile spatula and gloves to prevent contamination. Each
sample was labeled appropriately according to the status of each plant sample. 0.25 g of the
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collected soil sample was used for DNA extraction. The DNA extraction was performed using
DNeasy PowerSoil Pro Kit (Qiagen GmbH, Hilden, Germany) following the manufacturer’s
instructions. After DNA extraction, the quantity and quality of each DNA sample were assessed
using a NanoDrop 1000 Spectrophotometer (Thermo Scientific, Wilmington, DE, USA). For
DNA extraction from the inner part of plant roots (endosphere), the plant root samples that
remained after collection of the rhizospheric soil were surface sterilized by immersing them in 70%
ethanol and subsequently rinsing with double-distilled water to ensure the removal of microbes
on the surface of root tissue. Under aseptic conditions and using sterile scissors the surface-
sterilized roots were cut into pieces (~ 1 to 2 mm thick) to access the inner endospheric part.
DNA extraction of the plant tissue samples for the endosphere was conducted utilizing a DNeasy
Plant Mini Kit (Qiagen GmbH, Hilden, Germany) following the manufacturer’s instructions.
Subsequently, the DNA samples extracted from the endosphere samples were quantified using a
NanoDrop 1000 Spectrophotometer (Thermo Scientific, Wilmington, DE, USA). Extracted DNA
was then sequenced for 16S rDNA sequencing.
Library Construction and high-throughput DNA sequencing of 16S rDNA
The V4 regions of bacterial 16S rDNA were amplified using the primers 515F (5’-
GTGYCAGCMGCCGCGGTAA-3’) and 806R (5’-GGACTACNVGGGTWTCTAAT-3’)
designed in published protocols [9, 10]. Thirty nanograms of isolated DNA were used as the
template for the PCR amplification reaction and subsequent library construction. The resultant
products were purified using Agencourt AMPure XP beads and subsequently measured using an
Aligent 2100 bioanalyzer to determine their size and concentration. Samples that passed the
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quality control were sequenced on DNBSEQ-G99 platform (MGI Tech, ShenZhen, China) using
a 300bp paired-end strategy.
Raw Data Import, Quality checking, and ASV feature table Construction
Raw paired-end reads (FASTQ) from the original DNA fragments were imported in Qiime2 v
2023.2 software [11]. Paired-end reads for all 20 samples for the dataset Endosphere (root) and
20 samples for Rhizosphere (soil) were imported using the manifest file method. Quality filtering,
denoising, and chimeric sequence removal were done using the DADA2 denoising method. To
remove low-quality regions of the sequences --p-trunc-len parameter was used to truncate each
sequence at position 253 in forward and reverse reads. This DADA2 pipeline generated
a FeatureTable [Frequency], which contains counts (frequencies) of each unique sequence in
each sample in the dataset, and a FeatureData[Sequence], which maps feature identifiers in
the Feature Table to these sequences.
Taxonomy Assignment
To explore the taxonomic composition of the samples, a pre-trained Naïve Bayes classifier and
q2-feature classifier plugin were used to assign likely taxonomies to the sequences. This
classifier, downloaded from the qiime2 data resources page, was trained on the SILV A OTUs [12]
from the V4 (515F/806R) region of sequences. Taxa bar plots were generated using an R package
microViz (V . 0.12.0) [13] to visualize the taxonomic composition of each sample and group at
Phylum, Family, and Genus classification levels. Bar plots are used to visualize OTUs' relative
abundance. All nonbacterial OTUs’ sequences are filtered out using the feature-table-filtering
Method
in Qiime2.
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Diversity Analysis
To assess the alpha diversity, three different metrics are calculated: “Evenness” estimates the
species abundance; “Observed OTU” estimates the number of unique OTUs found in each
sample, and “Shannon index” accounts for both richness and evenness. Shannon index value
ranges from 0 to 1. Lower values indicate high diversity and higher index values do lower
diversity. These alpha diversity metrics were calculated using
the phyloseq function ‘estimate_richness’ [14] and to visualize diversity results, Boxplots are
generated using “qiime2R” [15] and “ggplot2” [16] libraries in R. For beta diversity analysis,
Principal Co-ordinates Analysis (PCoA) was performed. PCoA is an unconstrained method, but it
does require a distance matrix. In an ecological context, a distance (or more generally a
“dissimilarity”) measure indicates how different a pair of (microbial) ecosystems are. This can be
calculated in many ways. For this study, Weighted Unifrac distance, Unweighted Unifrac
distance, and Generalized UniFrac, "gunifrac were selected to generate PCoA curve to measure
the dissimilarity coefficient between pairwise samples, which are phylogenetic measures used
extensively in recent microbial community sequencing projects. An R package microViz (V .
0.12.0) [13] was used to generate these plots. The UniFrac family
of methods was employed to
determine dissimilarities. The approach considers the phylogenetic relatedness of taxa/sequences
in samples. Conversely, un-weighted UniFrac, dist_calc(dist = "unifrac") disregards the relative
abundance of taxa, and highlights solely on their presence (detection) or absence. This renders it
particularly sensitive to rare taxa, sequencing artifacts, and abundance filtering choices. For
assessing dissimilarities, on the other hand, weighted UniFrac, denoted as "wunifrac," places
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(potentially excessive) emphasis on highly abundant taxa. The Generalized UniFrac, labeled as
"gunifrac," achieves a balance between the extremes of unweighted and weighted UniFrac.
Co-occurrence microbial network analysis
An R package called ggClusterNet [17] was used to make networks for Endosphere (root) and
Rhizosphere (soil) datasets. An integrated function network.2() of ggClusterNet was used for
microbial network data mining and visualization. Briefly, to calculate network correlation the
Spearman method was used, 0.9 correlation and 0.05 P-value thresholds were used to filter the
microorganism table. The model_maptree2 layout has been used for the microbial network. Two
types of networks were calculated:1) Global network, including all OTU from all samples; 2)
Individual network for each of four groups from Endosphere (root) and Rhizosphere (soil)
datasets.
Results
and Discussion
Alpha and beta diversities
We analyzed the alpha and beta diversities of both rhizospheric and endospheric bacterial
communities. As we did not find any significant differences in beta diversity among the
rhizosphere samples regardless of their surviving status and plot condition (data not shown), our
analysis of bacterial community shifted to the root endosphere. Here, we observed significant
differences in beta diversity between drought-surviving and non-surviving soybean root tissues
in both Plot A and Plot B (p-value = 0.001, permanova, pseudo-F test statistic). Pairwise
permanova results further confirmed these distinctions. Notably, alpha diversity analysis revealed
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evenness within the groups. A closer scrutinizing of taxa bar plots identified seven genera—
Pseudomonas, Pantoea, Streptomyces, Micrococcaceae, Luteimonas, Variovorax, and Bacillus—
as being permanently abundant in either surviving or dry/dead plants from both fields (Figures 3
and 4). These findings led us to hypothesize that these bacterial genera might play a crucial role
in enhancing soybean tolerance to severe drought stress. A comprehensive bar graph visually
illustrates the abundance of these bacterial genera in surviving plants except for Streptomyces,
which is abundant in dry/dead plants in both fields (Figure 4).
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Figure 3. Taxa bar plot showing seven abundant bacterial genera either in surviving or dry/dead
soybean root tissues (root endosphere).
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Figure 4. Relative abundance of bacterial genera dominant in the root endosphere of drought-
damaged soybean plants.
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Among the seven major bacterial genera, Gram-negative bacteria Pseudomonas and Pantoea
were conspicuously predominant in surviving roots, although Pantoea showed reduced presence
in Plot B, which has less stress damage (Figure 4). In contrast, Streptomyces was the genus that
was most conspicuously dominant over other bacterial genera (Figure 4).
The predominance of Pseudomonas strains in our microbiome analysis is noteworthy given their
potential contributions to enhancing soybean tolerance to severe drought stress. Extensive studies
have highlighted the ability of Pseudomonas strains to produce V olatile Organic Compounds
(VOCs) that directly assist plants in withstanding drought and high salinity [18]. Furthermore,
Pseudomonas strains, such as P. si m i a e AU, have been associated with induced systemic
tolerance (IST) in plants against multiple abiotic stresses, aiding in the accumulation of proline
and reducing sodium content in roots to cope with osmotic and ionic stress [19]. The formation
of biofilms by plant-beneficial Pseudomonas spp. has also been identified as a mechanism that
improves tolerance to various stresses, including osmotic and oxidative stress, while enabling the
production of beneficial secondary metabolites [20, 21]. Additionally, Pseudomonas fluorescens
DR397, isolated from drought-prone rhizospheric soil, exhibited high metabolic activity under
drought conditions and upregulated the expression of genes related to plant growth promotion,
resulting in increased shoot and root growth in legume cultivars under drought conditions [22].
Moreover, the application of Pseudomonas putida H-2-3 reprogrammed chlorophyll, stress
hormones, and antioxidants in abiotic stress-affected soybean plants, improving their growth
under saline and drought conditions [23]. Collectively, these findings underlie the crucial role of
Pseudomonas strains in mitigating drought stress in soybean through various mechanisms,
including VOC production, biofilm formation, and plant physiological modulation.
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The other predominant bacterial genus Pantoea in the surviving root samples of Plot A is also
reminiscent of previous studies showing the biological roles of Pantoea spp. in protecting plants
from abiotic stresses. The colonization of wheat plants by Pantoea agglomerans, known for its
exopolysaccharide (EPS) production, positively influenced rhizosphere soil aggregation by
increasing the RAS/RT ratio and enhancing the water stability of adhering soil aggregates [24].
In a separate study, Pantoea strain LTYR-11ZT, isolated from the leaves of the drought-tolerant
plant Alhagi sparsifolia, exhibited multiple plant growth-promoting (PGP) traits, improving
wheat performance under drought conditions. This strain enhanced soluble sugar accumulation,
reduced proline and malondialdehyde levels, and decreased chlorophyll degradation in leaves
[25]. Moreover, EPS derived from Pantoea alhagi NX-11 demonstrated significant
improvements in drought resistance in rice seedlings, increasing fresh weight, and relative water
content, and enhancing various physiological parameters, including total chlorophyll, proline,
and soluble sugar content [26]. Additionally, Pantoea sp. YSD J2, isolated from the leaves of
Cyperus esculentus L. var. sativus, exhibited notable plant growth-promoting characteristics,
including indole acetic acid production, siderophores generation, and the ability to solubilize
phosphate and potassium [27]. These collective findings highlight the diverse roles of Pantoea
species in promoting plant growth, enhancing drought tolerance, and contributing to sustainable
agriculture through various mechanisms, including EPS production and PGP traits.
Our observation that the genus Streptomyces was solely prevailing over other major bacterial
genera is not surprising, regarding that this bacterial genus is one of the most abundant
microorganisms in soil [28, 29]. In dead root tissues, all the bacterial organisms that are
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dependent on the interactions with living plant tissues would be rapidly replaced with the
dominant soil saprophytes, such as Streptomyces spp. Our results suggest a preference for the
saprophytic lifestyle of Streptomyces in colonizing dead or dry plants, contributing to the
intriguing dynamics of microbial interactions in stressed plant environments. Further
investigations into the specific mechanisms underlying Streptomyces preferences and its
potential impact on plant health in stressed conditions would be valuable for a comprehensive
understanding of its ecological role.
Regarding the other 4 major bacterial genera identified in this study, several previous studies
reported their relatedness with plant drought stress, supporting the idea that these bacterial
organisms can be good candidate biological materials to augment the resilience of crops to
drought stress. Arun et al. [30] reported the isolation of Micrococcus spp. from various
environmental sources, including soil and plant samples, and highlighted the plant growth-
promoting properties of Micrococcus luteus. Notably, the strain K39 of Micrococcus luteus,
isolated from the roots of Cyperus conglomeratus in a desert environment, exhibited
characteristics relevant to drought stress survival [31]. This finding aligns with our results,
where Plot A, experiencing severe drought stress, showed a higher abundance of bacteria from
the Micrococcaceae family compared to Plot B. Related to another major genus Lutemonas, L.
deserti sp. nov. is an intriguing species isolated from the desert soil of northern PR China,
providing evidence for the presence of Luteimonas in the endosphere of drought-stressed plants
[32]. This discovery aligns with our observations, suggesting a potential association between
Luteimonas and plants experiencing drought stress.
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Variovorax paradoxus strain 5 C-2, characterized by the presence of the enzyme 1-
aminocyclopropane-1-carboxylate (ACC) Deaminase, has been associated with notable benefits
for plant growth under drought conditions. Belimov et al. [33] reported that this strain
contributes to a reduction in ethylene (ET) production, leading to increased nodulation, elevated
seed nitrogen content, enhanced xylem abscisic acid (ABA) concentration, improved water
content, and ultimately a higher pea yield. The findings suggest that the enzymatic activity of
ACC Deaminase in Variovorax paradoxus plays a crucial role in modulating hormone signaling
both locally in the rhizosphere and systemically within the plant. These observations underscore
the potential of Variovorax paradoxus as a beneficial rhizobacterium in promoting plant growth
and yield, particularly in conditions of soil moisture limitation.
Bacillus, particularly Bacillus thuringiensis (UFGS2), has demonstrated its ability to mitigate the
impacts of drought stress in plants. In soybean, UFGS2-treated plants exhibited higher stomatal
conductance and transpiration compared to the control group following drought stress [34]. This
suggests a positive influence of Bacillus thuringiensis on plant water regulation under water
scarcity conditions. Similarly, the combined application of Pseudomonas putida and Bacillus
amyloliquefaciens alleviated drought stress in chickpeas by exhibiting multiple plant growth-
promoting traits, including ACC deaminase activity, mineral solubilization, hormone production,
biofilm formation, and siderophore production [35]. Moreover, Bacillus paralicheniformis strain
FMCH001 demonstrated the potential to enhance water use efficiency, nutrient uptake, root
growth, photosynthesis rate, C:N ratio, and overall plant-water relations in soybean, making it a
promising candidate for sustaining plant growth in water-limited conditions [36]. Additionally,
Bacillus pumilus strain SH-9, identified as a drought-tolerant variant, positively influenced
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soybean growth under drought stress by modulating the expression of phytohormone genes and
antioxidant profiles [37]. Furthermore, Bacillus subtilis emerged as a beneficial bacterium
promoting the growth of common beans and maize while increasing water use efficiency. This
bacterium enhanced leaf water content, regulated stomatal activity, and decreased antioxidant
activities without compromising photosynthetic rates [38]. In summary, Bacillus species,
including Bacillus thuringiensis, Bacillus amyloliquefaciens, Bacillus paralicheniformis,
Bacillus pumilus, and Bacillus subtilis, exhibit promising capabilities in alleviating drought
stress and enhancing plant growth under challenging environmental conditions. These findings
emphasize the potential of Bacillus-based strategies for sustainable agriculture in water-limited
regions.
Co-occurrence networks analyses
Network analyses play crucial roles in deciphering co-occurrence patterns across microbial taxa
within complex communities. They also facilitate determining positive and negative interactions
among diverse taxa [17]. Here, we constructed two sets of co-occurrence networks: endophytic
and rhizospheric networks (Figure 5). Within each category, four networks were developed,
namely, surviving plot A, non-surviving plot A, surviving plot B, and non-surviving plot B. In
total, eight co-occurrence networks were constructed using the significant correlations among
phyla (Spearman’s correlation coefficient r/i1>/i10.9, p/i1</i10.05). Each network exhibited varied
network features (Figure 5, Table 1). In general, rhizospheric networks consist of a greater
number of nodes, edges, and clusters compared to all endophytic networks, with the highest
numbers observed in surviving plot A. Conversely, among endophytic networks, non-surviving
plot A displayed the highest number of nodes, edges, and clusters (Figure 5). These findings
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suggest the existence of varied levels of OTU complexity in endophytic and rhizospheric
networks in plot A. These network features are consistent with the average degree of each
network. Intriguingly, non-surviving plot A of endophytic networks showed the highest numbers
of negative edges, indicating the existence of both synergistic and antagonistic relations among
diverse OTUs. The edge density, a network characteristic that represents the proportion of
possible relationships in the network, signifies the intricacy of the network and the presence of
robust interactions among diverse OTUs. Among the eight networks studied, surviving plot B of
endophytic networks exhibited the highest edge density of 0.07, while the lowest value of 0.04
was observed in non-surviving plot A of endophytic networks. The highest modularity, a
network feature assessing the network's structure, was identified in surviving plot A (12.04) of
rhizospheric networks. Conversely, the lowest modularity was observed in surviving plot B of
endophytic networks (Figure 5 and Table 1). In summary, the examination of co-occurrence
patterns and network centrality analyses allowed us to recognize the intricate nature of
operational taxonomic units (OTUs) within each network category.
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Figure 5. The co-occurrence networks analyses. Four groups each for endophytic (A) and
rhizospheric networks (B) are illustrated. Individual types of networks within each category are
indicated. Nodes, edges, and clusters for each network are specified. The color of nodes signifies
OTUs from the same module in each network, while line color indicates positive (orange) and
negative (blue) correlation coefficients. Network construction employed Spearman’s correlation
coefficient, with R
/i1>/i10.9 and p/i1</i10.05 as criteria.
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Table 1. Network features of diverse co-occurrence networks
Endophytic networks Rhizospheric networks
Centrality Features Surviving
(Plot A)
Non-
surviving
(Plot A)
Surviving
(Plot B)
Non-
surviving
(Plot B)
Surviving
(Plot A)
Non-
surviving
(Plot A)
Surviving
(Plot B)
Non-
surviving
(Plot B)
Nodes 476 648 327 406 1094 1011 872 861
Edges 6449 10208 3840 5474 38632 32640 21395 20119
Positive Edges 6320 10050 3765 5426 38590 32543 21352 19992
Negative Edges 129 158 75 48 42 97 43 127
Number of Clusters 73 92 52 61 90 92 73 93
Connectance (Edge
Density) 0.05704556 0.048695785 0.07204368 0.06658152 0.06461595 0.063930429 0.0563388 0.054341896
Average degree
(Average K) 27.0966387 31.50617284 23.4862385 26.9655172 70.6252285 64.56973294 49.071101 46.7340302
Average Path Length 1 1 1 1 1 1 1 1
Diameter 1 1 1 1 1 1 1 1
Mean Clustering
Coefficient (Average
CC) 1 1 1 1 1 1 1 1
Centralization Degree 0.06927023 0.064132654 0.1334778 0.06181354 0.08817454 0.095475512 0.0791377 0.0712395
RM (Relative
Modularity) 5.2693558 6.040679146 3.17505499 4.79215729 12.0494888 10.78020977 8.7625972 8.561277694
Conclusion
This study contributes to a deeper understanding of the intricate interactions between bacteria
and plants in the context of drought stress. Specifically, our metagenomic analyses in the fields
of Louisiana under drought conditions have provided insights into microbial diversity and
primary bacterial components of the rhizosphere under such arid circumstances. The findings
from our co-occurrence network analyses have corroborated and strengthened our understanding
of the microbial dynamics in response to drought stress. Our study establishes a foundation for
further research and highlights the importance of defining microbial diversity in the context of
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drought stress, particularly in regions like Louisiana facing challenges related to drought
conditions.
Funding
This work was supported by USDA NIFA (Hatch LAB# 94575), Louisiana Soybean and Grain
Research and Promotion Board (GR# 00010744 and GR# 00010803), United Soybean Board
(#2314-209-0201), and NSF (Award # IOS-2038872).
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