Skip to main content
Frontiers in Microbiology logoLink to Frontiers in Microbiology
. 2022 Dec 22;13:1042944. doi: 10.3389/fmicb.2022.1042944

Populus root exudates are associated with rhizosphere microbial communities and symbiotic patterns

Mengjie Li 1,, Zhen Song 2,, Zhanbiao Li 1, Rongye Qiao 1, Pingdong Zhang 1, Changjun Ding 3, Jianbo Xie 1, Yinglong Chen 4, Hui Guo 1,5,*
PMCID: PMC9812961  PMID: 36619999

Abstract

Introduction

Microbial communities in the plant rhizosphere are critical for nutrient cycling and ecosystem stability. However, how root exudates and soil physicochemical characteristics affect microbial community composition in Populus rhizosphere is not well understood.

Methods

This study measured soil physiochemistry properties and root exudates in a representative forest consists of four Populus species. The composition of rhizosphere bacterial and fungal communities was determined by metabolomics and high-throughput sequencing.

Results

Luvangetin, salicylic acid, gentisic acid, oleuropein, strigol, chrysin, and linoleic acid were the differential root exudates extracted in the rhizosphere of four Populus species, which explained 48.40, 82.80, 48.73, and 59.64% of the variance for the dominant and key bacterial or fungal communities, respectively. Data showed that differential root exudates were the main drivers of the changes in the rhizosphere microbial communities. Nitrosospira, Microvirga, Trichoderma, Cortinarius, and Beauveria were the keystone taxa in the rhizosphere microbial communities, and are thus important for maintaining a stable Populus microbial rhizosphere. The differential root exudates had strong impact on key bacteria than dominant bacteria, key fungi, and dominant fungi. Moreover, strigol had positively effects with bacteria, whereas phenolic compounds and chrysin were negatively correlated with rhizosphere microorganisms. The assembly process of the community structure (keystone taxa and bacterial dominant taxa) was mostly determined by stochastic processes.

Discussion

This study showed the association of rhizosphere microorganisms (dominant and keystone taxa) with differential root exudates in the rhizosphere of Populus plants, and revealed the assembly process of the dominant and keystone taxa. It provides a theoretical basis for the identification and utilization of beneficial microorganisms in Populus rhizosphere.

Keywords: dominant taxa, keystone taxa, differential root exudates, phenolic compounds, interactive effect

Introduction

Soil microorganisms play an important role in plant growth. Beneficial microbial population can effectively promote the nutrient utilization, growth, and development of plants, and improve plant stress resistance (Song et al., 2020; Gupta et al., 2021). Early studies revealed more abundant microbial density, species richness, and metabolic activity in the rhizosphere than in the bulk soil, which has been regarded as “rhizosphere effect” (Ma et al., 2021). Various rhizosphere microorganisms, such as Pseudomonas, Streptomyces, and Fusarium, are common in the plant habitat (Wu N. et al., 2021). Microbe-microbe interactions sustain ecological balance. Network comprises the various interactions, including complex positive (e.g., commensalism and mutualism) and negative (e.g., predation and competition) interactions (Jiang Y. et al., 2017). For example, reconstructing a consortium of Chitinophaga and Flavobacterium consistently suppresses root disease caused by Rhizoctonia solani (Carrión et al., 2019). Pseudomonas interacts with Lysobacter and Bacillus to colonize the plant rhizosphere, where they supply nutrients for plant growth (Jiang Y. et al., 2017). In-depth research of co-occurrence networks is essential to understand the underlying interactive effect of the microbial communities, and to identify possible keystone populations in the communities.

Microbial groups (dominant and key microorganisms) play essential roles in promoting the utilization of nutrient elements by plant. Rhizosphere microorganisms are affected by soil nutrients and pH, electrical conductivity (EC), and soil moisture (Jiang J. et al., 2017; Bahram et al., 2018; Bai et al., 2020; Zhou et al., 2020). The composition, diversity, and dominance of bacteria vary among soils with different pH and soil organic carbon content (Sui et al., 2021). Basal microbial respiration depends strongly on soil moisture because of the water’s crucial role in substrate diffusion (Kundel et al., 2020); in turn, this directly affects the cycling of nutrients to microbes in forest ecosystems, including carbon cycling and nitrogen transformation (Wagg et al., 2014).

In addition to soil physicochemical properties, root exudates also affect the composition of the rhizosphere microbial communities. Root exudates account for 5–21% of the total photosynthetically fixed carbon, including organic acids, fatty acids, phenolics, amino acids, polysaccharides, and other secondary metabolites. The microbes make use of root exudates as nitrogen and carbon sources, and as signal stimuli (Ma et al., 2021). Phenolics are the most abundant plant metabolites and have been used as a slow carbon pool in soil dynamics models (Min et al., 2015). In Populus, the phenol salicylic acid acts as an inducible defense chemical that varies with tree genotype (Veach et al., 2019). Several microbial groups interact with salicylic acid, including Chloroflexi and the Basidiomycete family Hymenogastraceae (Veach et al., 2019). Strigol stimulates spore germination and hyphal growth of arbuscular mycorrhizal fungi (AMF). A positive correlation was detected between the capacity of a microbe to utilize compounds exuded by roots and its relative abundance therein (Rozpądek et al., 2018). During plant evolution, rhizosphere microorganisms affected root exudation. Beneficial microorganisms promote the accumulation of organic and amino acids, or produce peroxidase, which improves Populus plant growth under stress (Veach et al., 2020). Auxin produced by plant rhizosphere microbiota modulates flowering time and further stimulates exudation via a positive feedback mechanism (Lu et al., 2018). Therefore, root exudates affect the microbial community structure and microbial interactions. However, compared to the well-studied effect of nutrients on microorganisms, the role of the interaction between root metabolites and rhizosphere microorganisms in maintaining the stability of the ecosystem is not understood.

Populus is a genus of the Northern Hemisphere willow family (Salicaceae), and is the model organism for the study of woody perennials that may serve as an ideal model for understanding plant-microbe interactions (Feng et al., 2013). The growth and development of Populus are partially dependent on the functional microbial communities in the rhizosphere, which is the critical root-soil interface for plant growth (Song et al., 2020). Research on Populus has focused on plant aboveground traits, such as photosynthetic characteristics, carbon and nitrogen storage, and circulation, or focused on single factor on the belowground traits (Hogan et al., 2021; Wu X. et al., 2021; Wang et al., 2022). While research on the belowground traits, including dominant combined keystone taxa in the rhizosphere of Populus and the regulatory effects of differential root exudates on dominant and keystone taxa is lacking. Thus, this study used multi-omics technique (genomic-metabolomics) to explore microbial communities (dominant and key microorganisms) and differential root exudates in rhizosphere microecology of Populus in this ecological niche. The objectives of this study were to (i) identify the major factors influencing microbial communities; (ii) identify the key rhizosphere microorganisms in Populus; and (iii) examine the relationships between the exudates and rhizosphere microorganisms in the Populus microecosystem. The findings will lay a theoretical foundation for the screening and identification of key rhizosphere growth promoting microorganisms and the development and application of growth promoting agents for Populus.

Materials and methods

Study site and sample collection

The soil was sampled at the Research Base of Beijing Forestry University in Guanxian, Shandong Province, China (115°22′10.5″E, 36°30′56″N). The main cultivars of the experimental forests are Populus tomentosa (LM), Populus nigra (HY), Populus alba var. pyramidalis Bge. (XJ), and Populus simonii Carr (XY). Therefore, four Populus species (14 years old) were selected for study. They are widely distributed and cultivated in China and has been widely used in the numerous labs for diverse studies (Song et al., 2016, 2021; Ma et al., 2018; Sun et al., 2021). In this study, soil samples were randomly collected using the five-point sampling method with three replicates, five-point sampling (1 m × 1 m) was carried out using the diagonal principle. Plant fine roots (< 2 mm) were collected from each point within the root zone at a depth of 10–30 cm. The root samples were divided into two parts. For one part, the root-attached soil was shake off as bulk soils, and the soils tightly adhering to the roots were collected with a hairbrush as rhizosphere soil (Edwards et al., 2015; Zhu et al., 2022). Then, the soil sample was stored at 4°C until the physicochemical parameters were measured. For the other part, the samples were washed in 10 mM PBS buffer for 10 min on a shaking platform (120 rpm) and then transferred to clean 50 ml plastic tubes. Sterile tweezers were used to remove roots from the 50 ml plastic tubes, the soil particles directly centrifuged (6,000 × g, 4°C, 20 min) from the remaining suspension represented the rhizosphere samples (Beckers et al., 2016, 2017; Qin et al., 2018). And then the samples were stored at −20°C for later DNA extraction.

Soil physicochemical parameters

The soil pH and the electric conductivity (EC) value were tested using a glass electrode meter in a suspension of 1 g of soil in 5 ml of distilled water by pH meter and conductivity meter. Moisture content was determined by the oven dry-weight method. Available phosphorus (AP), available potassium (AK), available nitrogen (AN), and organic matter (OM) were separately measured by the molybdenum blue, flame photometry, potassium persulfate oxidation, and dichromate oxidation method, respectively (Lu, 1999). Each measurement had three replicates. Furthermore, Tukey’s test was performed to evaluate the distribution of the soil physicochemical parameters. A p-value <0.05 was considered significant.

Liquid chromatography with tandem mass spectrometry untargeted metabolomic analysis

After homogenization, a 1 g soil sample was put in a 5 ml Eppendorf tube, to which 3 ml of methanol was then added. The mixture was sonicated for 30 min in an ultrasonic bath. The supernatant was collected by centrifugation. These steps were repeated twice. Freeze-dried samples from exudates were resuspended in 150 μl methanol and then sonicated for 5 min in an ultrasonic bath. An aliquot of the supernatant was passed through a 0.22-μm (micropore) organic filter membrane and transferred to vials for subsequent analysis. The supernatant underwent high-performance liquid chromatography/triple time-of-flight mass spectrometry (Sciex TripleTOF 5600+, Framingham, MA, United States) analysis; an electron spray ionization (ESI) source was equipped. Separation was achieved on an HSS T3 column (100 mm × 2.1 mm, 1.7 μm; Waters, Milford, MA, United States). A gradient elution conditions were presented in Supplementary Table S1. The mass spectrometer was operated in both negative and positive ionization modes, and full scan mass spectra were recorded across the range of m/z 50–1,200. The curtain gas, gas 1, and gas 2 of the mass spectrometer were set to 35, 60, and 60 psi, respectively. The ESI temperature and spray voltage were 550°C and 4,500 V (negative)/5,500 V (positive), respectively. The differential metabolites with significant differences between any two of the four Populus samples were screened and identified by plant exudates databases (KEGG, PlantCyc, GMD; Wanichthanarak et al., 2020; Hawkins et al., 2021; Duan et al., 2022).

DNA extraction and high-throughput sequencing

Total microbial genomic DNA was extracted from 0.1 g of soil sample using the DNeasy PowerSoil DNA Isolation kit (Qiagen, Hilden, Germany). The V3–V4 regions of the bacterial 16S rRNA genes for the entire bacterial communities were amplified using the 338F/806R primers and the following temperature cycling conditions described by literature (Song et al., 2020). Fungal internal transcribed spacer (ITS1) genes were amplified using the ITS1F and ITS2R barcode primers, with the amplification program according to the reference description (Zhou et al., 2021).

The purified PCR amplified products were paired-end sequenced (2 × 300) on the Illumina MiSeq platform (Illumina, San Diego, CA, United States). The raw data were first screened and sequences were removed from consideration if they were shorter than 120 bp, had a low quality score (≤20), contained ambiguous bases or did not exactly match to primer sequences and barcode tags, and separated using the sample-specific barcode sequences. Qualified reads were clustered into operational taxonomic units (OTUs) at a similarity level of 97% use Uparse algorithm of Vsearch (v2.7.1) software. The Ribosomal Database Project (RDP) Classifier tool was used to classify all sequences (16S rRNA genes) into different taxonomic groups against SILVA128 database. The BLAST tool was used to classify all sequences (ITS1 genes) into different taxonomic groups against Unite database. Sequences belonging to archaea, mitochondria, and chloroplasts were also removed. To avoid potential bias caused by differences in sequencing depth, the number of sequences in each sample was rarefied to 56,232 (16S rRNA genes) and 29,376 (ITS1 genes) sequences per sample (Zhou et al., 2022). The raw sequencing data were deposited in the Sequence Read Archive at NCBI with the accession number PRJNA888251.

Statistical analysis

SPSS software (var. 17.0) was used for the data analysis. One-way ANOVA was used to detect differences among samples. Tukey’s test was performed to evaluate the distribution of the data. A value of p < 0.05 was considered significant. Metabolites with value of p < 0.05 and fold change >1.20 were considered as differential root exudates by SIMCA software (14.1), the fold change was compared with any two of four Populus species in pairs. Redundancy analysis (RDA) was performed using Canoco (v.5.0). A variation partitioning analysis (VPA) was applied to quantify the contributions of the environmental variables to the microbial communities, and the correlations between the microbes and metabolites, using R software 3.6.3. Interactions between microbial composition were studied through network analysis. The Gephi software 9.2 was used to visualize the network. The high values of topological features (degree, betweenness, and closeness centrality) suggest a core position of a node in the network (Jiao et al., 2017, 2020), and the high values of the above three parameters can jointly reflect the importance of key microbial flora (nodes in the network; Xing et al., 2021). Therefore, we choose high values of the topological parameters (degree, betweenness, and closeness centrality) as keystone taxa in this study.

The normalized stochasticity ratio (NST) was quantitated with the “NST” R package, which is assembly with 50% as the boundary point between more deterministic (NST < 50%) and more stochastic (NST > 50%) assembly (Ning et al., 2019). Levin’s niche breadth values of the dominant and keystone taxa were performed to illustrate community sensitivity to the environment, using the beta diversity “niche width” function within the R package “spaa” (Levins, 1968).

Results

Soil physicochemical characteristics and composition of root exudates

Most soil properties, including pH, moisture, OM, AN, AP, and AK, differed among the four Populus species (Table 1). The pH and EC values among HY, LM, XJ, and XY were 8.03–8.13 and 117.10–124.57 μs/cm, respectively. The moisture values of HY, LM, XJ, and XY were 2.00, 4.00, 4.00, and 3.00%, respectively. The average OM content was in the following order: LM (11.19 g/kg) > HY (9.98 g/kg) > XJ (7.74 g/kg) > XY (7.43 g/kg). The average AP contents of HY, LM, XJ, and XY were 4.34, 32.83, 11.50, and 2.90 mg/kg, respectively. The mean AN value were LM (38.93 mg/kg) > XJ (35.33 mg/kg) > HY (33.92 mg/kg) > XY (28.09 mg/kg). The AK values among HY, LM, XJ, and XY were 9.67, 10.50, 26.48, and 10.87 mg/kg, respectively. OM and AN content were significantly higher in LM than in the others. XJ had the highest AK content among the four Populus cultivars.

Table 1.

Soil properties in the rhizosphere of four Populus species.

Soil properties LM XJ HY XY
pH 8.12 ± 0.04a 8.03 ± 0.03b 8.13 ± 0.02a 8.06 ± 0.03ab
Moisture 4.00% ± 0.00a 4.00% ± 0.00a 2.00% ± 0.00b 3.00% ± 0.00a
EC(μs/cm) 121.80 ± 0.70a 124.57 ± 0.74a 119.93 ± 0.32a 117.10 ± 6.90a
OM(g/kg) 11.19 ± 0.40a 7.74 ± 0.17c 9.98 ± 0.08b 7.43 ± 0.34c
AP(mg/kg) 32.83 ± 0.02a 11.50 ± 0.03b 4.34 ± 0.00c 2.90 ± 0.01c
AK(mg/kg) 10.50 ± 0.16c 26.48 ± 0.06a 9.67 ± 0.15d 10.87 ± 0.12b
AN(mg/kg) 38.93 ± 0.20a 35.33 ± 0.91b 33.92 ± 1.38b 28.09 ± 1.07c

Different lower letters mean significant differences (p < 0.05) between the properties of different samples. Populus species: LM (P. tomentosa), XJ (P. alba var. pyramidalis Bge.), HY (P. nigra), and XY (P. simonii Carr).

Thirty-nine differential metabolites with significant differences between any two of the four samples (LM, HY, XY, and XJ) were obtained (p < 0.05, fold change > 1.20). These metabolites predominantly consisted of fatty acyls, prenol lipids, carboxylic acids and derivatives, benzene and substituted derivatives, organooxygen compounds, and flavonoids. Seven plant root exudates were then identified from them, including coumarins (luvangetin), phenolic compounds (salicylic acid, gentisic acid, and oleuropein), a phytohormone (strigol), a flavonoid compound (chrysin), and fatty acids (linoleic acid; Table 2).

Table 2.

The peak area of differential root exudates in the rhizosphere of four Populus species.

Differential root exudates Mean value in each type of Populus Pair-wise test (P-value)
LM XJ HY XY LM vs. XJ LM vs. HY LM vs. XY XJ vs. HY XJ vs. XY HY vs. XY
Chrysin 0.000 ± 0.000 1.250 ± 0.170 29.348 ± 20.686 362.294 ± 176.755 0.041 0.028 0.001 0.045 0 0.001
Luvangetin 8463.262 ± 791.139 4171.554 ± 161.516 11513.344 ± 750.233 23666.135 ± 1231.016 0 0.001 0 0 0 0
Oleuropein 17.356 ± 5.709 435.355 ± 22.632 79.344 ± 5.573 104.369 ± 9.892 0 0 0 0 0 0.011
Salicylic acid 213.105 ± 11.562 275.985 ± 40.937 458.952 ± 38.372 336.125 ± 1.119 0.006 0 0 0 0.013 0.004
Strigol 261.810 ± 26.201 1.558 ± 0.404 7.565 ± 0.481 3.890 ± 0.782 0 0 0 0 0.01 0
Gentisic acid 59.848 ± 2.256 23.370 ± 3.041 155.988 ± 24.740 277.597 ± 77.996 0 0.001 0 0 0 0.02
Linoleic acid 77.894 ± 10.874 29.017 ± 0.545 21.263 ± 2.651 14.891 ± 2.451 0 0 0 0.004 0 0.019

p < 0.05, fold change > 1.20; Populus species: LM (P. tomentosa), XJ (P. alba var. pyramidalis Bge.), HY (P. nigra), and XY (P. simonii Carr).

XY had higher contents of chrysin, luvangetin, and gentisic acid compared to the other Populus cultivars, and the contents of luvangetin and gentisic acid in XY were 5.67 and 11.88 times higher than in XJ. Relatively high oleuropein content was detected in XJ. The salicylic acid content in HY was 1.37–2.15 times higher than that in LM, XJ, and XY. In this study, LM had the highest strigol content (approximately 168-fold change).

Microbial diversity analysis

The Chao1 and Shannon diversity indices were used to measure the microbial alpha-diversity of each soil sample; the highest bacterial Chao1 and Shannon indices were observed in the LM sample, followed by the HY and XJ samples; the XY sample had the lowest index values (Figure 1A), showing that the sum of bacterial species was the highest in the LM rhizosphere sample. Among the rhizosphere fungal community samples (Figure 1B), the HY cultivar harbored more diverse communities than the LM, XJ, and XY cultivars. Bray-Curtis analysis showed that bacterial and fungal diversity differed among the four Populus cultivars (Figures 1C,D).

Figure 1.

Figure 1

Chao1 index, Shannon index, and principal-coordinate analysis (PCoA) of bacteria and fungi from four Populus species. (A) The bacterial alpha diversity. (B) The fungal alpha diversity. (C) The bacterial principal component analysis. (D) The fungal principal component analysis. Different lower letters mean significant differences (p < 0.05). The same lowercase letters mean that the difference is not significant in four Populus species (p > 0.05).

Microbial community composition

At the bacterial level, the communities were composed of the top 15 phyla and genera (dominant taxa) in each sample (Figure 2). Proteobacteria was the dominant phylum (25–28%), followed by Actinobacteria (18–21%), Acidobacteria (14–21%), Gemmatimonadetes (7–11%), Bacteroidetes (4–7%), and Chloroflexi (6–8%). At the genus level, soil beneficial bacteria included RB41 and H16, with mean relative abundances of 2.9–4.9 and 1.3–1.9%, respectively, followed by Sphingomonas, Gaiella, Haliangium, and Bacillus.

Figure 2.

Figure 2

Rhizosphere microbial community compositions of four Populus species.

At the fungal level, the communities were composed of the top 15 phyla and 10 genera (dominant taxa) in each sample (Figure 2). Ascomycota, Basidiomycota, and Mortierellomycota were the dominant fungal phyla, accounting for 50–63, 16–34, and 4–16%, respectively. At the genus level, the fungal communities were primarily composed of Geopora, Chrysosporium, Mortierella, and Tomentella. Coprinopsis was the most abundant fungal genus in LM. Mortierella dominated, with an abundance of 30–40% in HY and XY.

Co-occurrence network of rhizosphere microorganisms

The bacterial co-occurrence network composed of 132 nodes (genus) and 103 edges (links) was shown in Figure 3, which included 82 (79.61%) positive and 21 (20.39%) negative interactions. Positive relationships between microbial populations show the occurrence of a mutualistic interaction, while negative relationships indicate competition for hosts or a predacious relationship between microorganisms (Chow et al., 2014; Jiang J. et al., 2017). These interactions are strongly associated with important soil processes. The network had a modularity index of 0.94, the modularity index exceeded 0.4, suggesting a modular structure of the micro-network (Liu et al., 2020; Ye et al., 2020). Keystone taxa are the taxa which have major influence on microbiome composition and function at a particular space or time (Banerjee et al., 2018). The high values of the topological parameters (degree, betweenness, and closeness centrality) in the network were considered the keystone taxa (Jiao et al., 2017, 2020; Xing et al., 2021). The key bacteria were Flavihumibacter, Blastocatella, Adhaeribacter, Microvirga, Agromyces, and Nitrosospira. Flavihumibacter was positively correlated with Microvirga, indicating commensalism or a mutualistic relationship. The changes directly linked with the nodes (Nitrosospira) were all positive interactions.

Figure 3.

Figure 3

Co-occurrence networks of bacterial and fungal communities based on Spearman correlation.

The fungal co-occurrence network composed of 182 genera and 232 links was shown in Figure 3, which included 215 (92.67%) positive and 17 (7.33%) negative interactions. The network had a diameter of 13, average clustering coefficient of 0.33, average path length of 4.32, and modularity index of 0.88. The key microorganisms were mainly Myrmecridium, Trichomerium, Absidia, Neopaxillus, Trichoderma, Pluteus, Periconia, Cortinarius, Beauveria, Talaromyces, and Arnium. All of these taxa positively interacted with the Beauveria nodes. Eight genera, including Apodus, Laetisaria, Racocetra, Funneliformis, Erysiphe, Dentiscutata, Colacogloea, and Papiliotrema, were positively correlated with the keystone taxa Cortinarius, indicating their similarity or cooperation in ecological functions. There were two positive edges and one negative edge directly associated with Trichoderma hubs, including Lophiotrema, Hebeloma, and Phakopsora. Trichoderma was negatively correlated with Fusarium indirectly. Furthermore, key microorganisms generally have lower relative abundances than dominant microorganisms (Supplementary Table S1).

Relationship between the microbial communities, soil properties, and differential root exudates

Redundancy analysis and VPA were performed to study the relationships between the environmental factors and abundance of microbes (dominant taxa and keystone taxa). The RDA results shown in Figure 4A (dominant bacteria) indicated that OM, AN, AP, and moisture were positively correlated with the abundance of Sphingomonas, Streptomyces, Bacillus, and Pseudomonas, suggesting that bacteria were favored in rich nutritional conditions where they play important roles in soil C-, N- and P-cycling. AK and the differential root exudates negatively affected bacterial community composition. AP and AK had contrasting effects on the rhizosphere microbial population, indicating that they play a crucial role in the distribution of the microbial communities. The contribution of environmental factors was further quantified by VPA, which showed that differential root exudates explained 48.40%, soil nutrients explained 1.15%, pH and EC explained 1.00%, and moisture explained 16.61% of the dominant bacterial variance. The RDA results for dominant fungi (Figure 4B) showed that Hebeloma and Mortierella were positively correlated with AK, while the most dominant fungi had a negative association with soil nutrients (AP, AN, and OM) and differential root exudates, suggesting that fungi may be more suitable for oligotrophic environments. Differential root exudates had negatively correlation with most of the fungi (Figure 4B). VPA revealed that the differential root exudates explained 48.73% of the variance, soil nutrients explained 0.49%, pH and EC explained 1.15%, and moisture explained 0.66%.

Figure 4.

Figure 4

Redundancy analysis and variation partitioning analysis of microorganisms and soil properties. (A) Dominant bacteria and soil properties. (B) Dominant fungi and soil properties. (C) Key bacteria and soil properties. (D) Key fungi and soil properties. Red arrow: soil properties, blue triangle: microorganisms (In RDA).

The RDA results shown in Figures 4C,D indicated that OM and pH were positively correlated with the great majority of key microorganisms mainly include Microvirga, Agromyces, Blastocatella, Apodus, Pluteus, and Trichomerium, while the most key microorganisms had a negative association with AK and differential root exudates. VPA revealed that the differential root exudates explained 82.80% of the variance for key bacteria and 59.64% of the variance for key fungi, soil nutrients explained 0.54% (key bacteria) and 1.88% (key fungi), pH and EC explained 0.72% (key bacteria) and 0.66% (key fungi), and moisture explained 1.84% (key bacteria) and 3.67% (key fungi). Differential root exudates explained more of the variance in the bacterial and fungal communities than environmental factors, such as pH, EC, moisture, and soil nutrients. This finding indicates that the differential root exudates played the dominant role in shaping the Populus rhizosphere microbial communities and the differential root exudates had more effect on keystone taxa than dominant taxa.

Correlations between the differential root exudates and microbial communities and microbial community assembly processes

Variation partitioning analysis showed that differential root exudates had largest contributions to the changes in the rhizosphere microbial communities (Figure 4), we further focused on analyzing the relationships between differential root exudates and microbes (dominant and key microorganisms) in the rhizosphere by Spearman’s correlation analysis. The correlation analysis revealed that strigol was positively correlated with the dominant bacteria Bacillus (Figure 5). Phenolic compounds (oleuropein, gentisic acid, and salicylic acid) were negatively correlated with two dominant taxa (Bacillus and Hebeloma) and positively associated with two genera (Ossicaulis and Ramicandelaber). Luvangetin showed negatively relationship with Hebeloma. The abundances of dominant fungi (Pachyphloeus and Coprinopsis) had negatively relationship with chrysin and positively relationship with linoleic acid.

Figure 5.

Figure 5

Diagram of microbial assembly process. Significance of each exudate: *p ≤ 0.05. **p ≤ 0.01.

The correlation analysis indicated that strigol positively correlated with the abundances of the key bacteria Microviga, Pseudenhygromyxa, Flavihumibacter, and Actinocorallia. Oleuropein and other phenolic compounds had significantly negative correlation with the key microorganisms. Negative correlations were detected between the phenolics and abundances of bacteria (Flavihumibacter, Pseudenhygromyxa, Actinocorallia, Microviga, Kallotenue, and Thermomonas) and fungi (Trichoderma). Gentisic acid (a phenolic compound) was negatively correlated with Trichoderma. Chrysin (flavonoid compounds) was negatively correlated with three keystone taxa (Kallotenue, Thermomonas, and Rhizophlyctis). Kallotenue was positively associated with linoleic acid. In general, strigol was positively correlated with key bacteria, whereas phenolic compounds showed a negative correlation, which indicated the response of keystone taxa and dominant taxa were different to the same variables.

To study more in depth the differences in community structure, we further calculated the community-level habitat niche breadths (Bcom). Bacterial keystone taxa exhibited higher Bcom value than dominant taxa, fungal dominant taxa showed higher Bcom value than keystone taxa. Subsequently, we further employed NST to elucidate the assembly processes. The NST value was above the 50% boundary point accounted for both dominant taxa and keystone taxa (for 90.91%), suggesting that stochastic process played a more important role than deterministic process during the bacterial assembly. Additionally, NST value was observed in bacterial keystone communities with an average of 81.69% than that in bacterial dominant communities with an average of 79.43%. The dominant fungi accounted for 42.43% and key fungi accounted for 68.18% in the NST values above 50%, implying that fungal dominant taxa were dominated by deterministic process.

Discussion

Rhizosphere characteristics of Populus

Many studies have suggested that soil properties are the basic factors affecting the soil microbial communities (Li X. et al., 2021). The basic metabolism of microorganisms depends strongly on soil moisture (Kundel et al., 2020; Su et al., 2020). Soil OM is the main substrate and energy source for soil microbes (Wang J. et al., 2021). A previous report showed that AK alters the microbial communities and improves soil metabolic activities and functional diversity (Li H. et al., 2021). In the present study, we found that LM and XJ had high trophic level soils (Table 1).

Moreover, root exudates also affect the formation and structure of rhizosphere microbiome (Czarnota et al., 2003; Vives-Peris et al., 2020). Here we found seven differential root exudates. Oleuropein and gentisic acid are phenolic compounds, and gentisic acid is one of the most common aromatic acids in plants (Zhang et al., 2017; Catinella et al., 2022). Salicylic acid content can vary with genotype and the developmental stage of the plants (Veach et al., 2019). Salicylic acid regulates plant growth and development that as a common plant phenolic compound in Salicaceae, and acts as an inducible defense chemical expressed in response to a pathogen. However, some researches have showed that salicylic acid reduces soil microbial diversity and significantly affects the carbon metabolism capacity and genetic structure of microbial communities. Strigol is a carotenoid-derived signaling molecule that communicates with parasites in the rhizosphere, and regulates plant growth and development by crosstalk with other hormones (Wakabayashi et al., 2021). Strigol is chemically unstable and decomposes rapidly in the soil, but exudates can protect strigol from rapid degradation (Yoneyama, 2020). The linoleic acid level was higher in LM than in the others significantly. Linoleic acid is a major component of biomembranes; it functions as a signaling molecule and directly participates in development (Huang et al., 2021). The changes of some specific compounds in root exudates can affect the dynamics of soil microbial communities (Zhao et al., 2021).

Dominant and keystone taxa on Populus rhizosphere

We revealed that the dominant phyla such as Proteobacteria, Actinobacteria, Acidobacteria, Ascomycota, and Basidiomycota. The ratio of Proteobacteria to Acidobacteria can be used to measure the level of soil nutrition, favoring Proteobacteria in rich soils and Acidobacteria in poor soils (Castro et al., 2010; Gottel et al., 2011). In our research, LM and XJ had higher ratios than HY and XY. Bacteroidetes is usually not a dominant bacterial phylum in soil (Song et al., 2020), but was highly abundant in the rhizosphere. Sphingomonas, a Gram-negative bacterium and rhizosphere biomarker that grows under aerobic conditions. The biomarker results indicated that the Populus rhizosphere environment can provide sufficient air and organic nutrient conditions for these bacteria (Li J. et al., 2020). Mortierella is a plant growth-promoting fungi that enhances plant phosphate nutrition (Li F. et al., 2020). Geopora species are common and important ectomycorrhizal fungi that often seen in woody plants rhizosphere, where they can increase the utilization of water and nutrients by hosts. These taxa constituted a high proportion of the microbial communities in the different Populus cultivars, and play a notable role in promoting plant growth and degrading refractory pollutants, and protect plants from harmful pathogens (Patterson et al., 2019).

Dominant and key populations affect the composition and structure of the entire microbial communities (Berry and Widder, 2014). The entire communities will crumble without key species (Floc’H et al., 2020); thus, apart from those dominant taxa, identifying the keystone taxa of the plant rhizosphere is essential to optimize plant growth. Modularity, which represents microbial interactions, is vital for microbial community stability and resilience due to the resource allocation, habitat heterogeneity, phylogeny, or niche overlap (Tya et al., 2021). In this research, the modularity index exceeded 0.4, suggesting a modular structure of the real-world network (Liu et al., 2020; Ye et al., 2020). The co-occurrence network composed of 22 bacterial keystone taxa and 26 fungal keystone taxa. The genus Microvirga is very common in nature. Microvirga sp. participates in the soil nitrogen cycle and provides nitrogen for plants and other microorganisms (Amin et al., 2016; Veyisoglu et al., 2016; Longa et al., 2017). The key genus Adhaeribacter exhibits urease and alkaline phosphomonoesterase activities, which help maintain available N and P content in the soil and regulate growth in environments polluted with heavy metals (Lin et al., 2020). Nitrosospira are ammonia- and nitrite-oxidizing bacteria, related to the nitrogen metabolic processes that make nutrients available to other community members. Numerous studies have revealed that nitrogen cycling taxa play a key role in a variety of ecosystems (Rädecker et al., 2015; Che et al., 2018; Dai et al., 2020; Ramond et al., 2022). Therefore, the ecological role and mechanism of nitrogen cycling-related microorganisms in plant growth merit further systematic study.

Beauveria bassiana is widely used as an effective strain for biological control of plant diseases. The BbAFP1 chitinase secreted by B. bassiana has good antifungal activity in plants, and its gene expression in Chinese white poplar can well reduce the incidence of diseases caused by Cytospora chrysosperma (Tong et al., 2021). Members of the ectomycorrhizal genus Cortinarius are often dominant in fungal communities from boreal soils. Some members of this genus may be directly involved in the degradation of soil OM in the humus layers of northern forest ecosystems. This is an active mycorrhizal community with high mycelial turnover rates that successively depletes N humus and minimizes the long-term accumulation of humus layers, which were very important in maintaining the balance of the ecosystem (Bödeker et al., 2014; Clemmensen et al., 2015). The genus Trichoderma, a well-known plant growth-promoting microorganism and biological control agent (Fernández-González et al., 2020), activates the plant immune system through induced systemic resistance, which is a priming defense mechanism against pathogens (Gupta et al., 2021). Xylanase secreted by Trichoderma promotes systemic resistance of host plants against pathogens, suggesting that Trichoderma may have biocontrol abilities in the Populus rhizosphere (Guo et al., 2021). Furthermore, key microorganisms generally have lower relative abundances than dominant microorganisms, indicating that species interactions may played a more important role in Populus growth than that of species abundance.

Effects of differential root exudates on rhizosphere microbial communities

As shown in RDA, environmental factors such as AN, OM, and pH influence microbial communities. Here, we found by VPA that the differential root exudates explained more of the variability in shaping the Populus rhizosphere microbiome than other environmental factors. This result was in agreement with previous reports that root exudates significantly regulate the soil microbial community structure (Gu et al., 2020). We further revealed that the correlations of the differential root exudates and microbiome (dominant taxa and keystone taxa). Our results showed that strigol and phenolic compounds were key factors for rhizosphere microbial communities. Strigol was reported to regulate root architecture and hyphal branching of AMF (Liu et al., 2018). Bacillus plays an important mediating role in mycorrhizal symbiosis, which improves the growth and nutrient uptake of plants (Wang Y. et al., 2021; Zhang et al., 2021). Therefore, the positive correlation between strigol and Bacillus may have combined action on the development of mycorrhiza, which could promote the growth of Populus. Phenolic compounds showed a negative correlation with microbiome, probably because these chemicals are relatively resistant to decomposition by microorganisms and inhibit microbial activity (Gu et al., 2020). Furthermore, phenolic compounds can impair membrane structure and function, or increase the permeability of cell membrane to cause the leakage of cell contents (Mattos et al., 2017). It is reported that salicylic acid modulates root colonization by Trichoderma, as exogenous inoculation decreases the multiplication of the fungus on roots. Phenolic compounds extracted from rice straw were also reported to have significant inhibition on the growth of T. reesei (Zheng et al., 2017; Macías-Rodríguez et al., 2020). Moreover, the differential root exudates affected the key bacteria more than fungi and the dominant bacteria, and that the keystone taxa maintained the microbial ecology critically. Therefore, the further study on the relationship between specific microorganisms and rhizosphere exudates will provide a theoretical basis for reducing the adverse effects and promoting plant growth.

Differences in community assembly between keystone and dominant taxa

In the present study, we demonstrated that the niche-based stochastic processes determine the assembly of bacterial communities and fungal keystone taxa. Keystone taxa showed higher stochasticity comared dominant taxa, thus demonstrating keystone taxa make more contributions to the stable of community structure under environmental disturbances. In addition, a finding is that the NST value of bacteria was higher than that of fungi, suggesting that stochastic processes contribute more to bacterial communities than to fungal communities. This observation could be due to the size-plasticity hypothesis that smaller organisms (bacteria) are less environment filtered than larger organisms (Liu et al., 2015). Subsequently, we quantified the Bcom value. Bacterial keystone taxa had a higher Bcom value than dominant, which was consistent with previous studies, a previous study reported that organisms with Bcom value might have greater metabolic plasticity and be less influenced by deterministic processes (Pandit et al., 2009). The Bcom value of fungal keystone taxa was lower than that of dominant.

In a word, VPA indicated that the differential root exudates explained a larger proportion of keystone taxa (82.8 and 59.64%) than dominant taxa (48.4 and 48.73%), while NST demonstrated keystone taxa showed higher stochasticity compared dominant taxa. These contrasting results may be due to the unmeasured environmental variables as mentioned above. Thus, more comprehensive data (taxonomic, phylogenetic, environmental, and spatial) and more dimensions should be considered when relating the relative influence of ecological processes to microbial community assembly.

Conclusion

In this study, differential root exudates from four Populus cultivars, including luvangetin, salicylic acid, gentisic acid, oleuropein, strigol, chrysin, and linoleic acid, were the major interfering factor of microbial communities’ variation. Network analysis revealed that keystone taxa interactions were very important in maintaining the stability of the Populus rhizosphere microorganisms than species abundance. Furthermore, correlation analysis revealed that strigol had positively effects with bacteria, the phenolic compounds and chrysin were negatively correlated with the rhizosphere microorganisms. In general, differential root exudates showed significant relationship with the key bacterial taxa. Community structure (keystone taxa and bacterial dominant taxa) was mostly determined by stochastic processes, keystone taxa showed higher stochasticity compared dominant taxa, thus demonstrating keystone taxa make more contributions to the stable of community structure under environmental disturbances. The results provided a basis for further identification and utilization of important microbes in Populus rhizosphere.

Data availability statement

The data presented in the study are deposited in the Sequence Read Archive repository, accession number PRJNA888251, https://www.ncbi.nlm.nih.gov/bioproject/PRJNA888251.

Author contributions

ML and ZS: conceptualization, methodology, investigation, writing—original draft, and writing—review and editing. ZL, PZ, and JX: software and formal analysis. RQ: validation and resources. CD: validation and data curation. HG: conceptualization, methodology, writing—review and editing, supervision, and funding acquisition. All authors contributed to the article and approved the submitted version.

Funding

This work was funded by National Key Research and Development Program of China (2021YFD2201205), National Natural Science Foundation of China (41601513 and 41977203), and Beijing Forestry University Municipal Training Program of Innovation and Entrepreneurship for Undergraduates (202110022017).

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.

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/fmicb.2022.1042944/full#supplementary-material

References

  1. Amin A., Ahmed I., Habib N., Abbas S., Hasan F., Xiao M., et al. (2016). Microvirga pakistanensis sp. nov., a novel bacterium isolated from desert soil of Cholistan. Pak. Arch. Microbiol. 198, 933–939. doi: 10.1007/s00203-016-1251-3, PMID: [DOI] [PubMed] [Google Scholar]
  2. Bahram M., Hildebrand F., Forslund S. K., Anderson J. L., Soudzilovskaia N. A., Bodegom P. M., et al. (2018). Structure and function of the global topsoil microbiome. Nature 560, 233–237. doi: 10.1038/s41586-018-0386-6, PMID: [DOI] [PubMed] [Google Scholar]
  3. Bai Y., Ren P., Feng P., Yan H., Li W. (2020). Shift in rhizospheric and endophytic bacterial communities of tomato caused by salinity and grafting. Sci. Total Environ. 734:139388. doi: 10.1016/j.scitotenv.2020.139388, PMID: [DOI] [PubMed] [Google Scholar]
  4. Banerjee S., Schlaeppi K., Van D. (2018). Keystone taxa as drivers of microbiome structure and functioning. Nat. Rev. Microbiol. 16, 567–576. doi: 10.1038/s41579-018-0024-1 [DOI] [PubMed] [Google Scholar]
  5. Beckers B., Op De Beeck M., Weyens N., Boerjan W., Vangronsveld J. (2017). Structural variability and niche differentiation in the rhizosphere and endosphere bacterial microbiome of field-grown poplar trees. Microbiome 5:25. doi: 10.1186/s40168-017-0241-2, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  6. Beckers B., Op De Beeck M., Weyens N., Van Acker R., Van Montagu M., Boerjan W., et al. (2016). Lignin engineering in field-grown poplar trees affects the endosphere bacterial microbiome. Proc. Natl. Acad. Sci. 113, 2312–2317. doi: 10.1073/pnas.1523264113, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  7. Berry D., Widder S. (2014). Deciphering microbial interactions and detecting keystone species with co-occurrence networks. Front. Microbiol. 5:219. doi: 10.3389/fmicb.2014.00219 [DOI] [PMC free article] [PubMed] [Google Scholar]
  8. Bödeker I. T. M., Clemmensen K. E., Boer W., Martin F., Olson Å., Lindahl B. D. (2014). Ectomycorrhizal Cortinarius species participate in enzymatic oxidation of humus in northern forest ecosystems. New Phytol. 203, 245–256. doi: 10.1111/nph.12791, PMID: [DOI] [PubMed] [Google Scholar]
  9. Carrión V. J., Perez-Jaramillo J., Cordovez V., Tracanna V., de Hollander M., Ruiz-Buck D., et al. (2019). Pathogen-induced activation of disease-suppressive functions in the endophytic root microbiome. Science 366, 606–612. doi: 10.1126/science.aaw9285, PMID: [DOI] [PubMed] [Google Scholar]
  10. Castro H. F., Classen A. T., Austin E. E., Norby R. J., Schadt C. W. (2010). Soil microbial community responses to multiple experimental climate change drivers. Appl. Environ. Microbiol. 76, 999–1007. doi: 10.1128/AEM.02874-09, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  11. Catinella G., Donzella S., Borgonovo G., Dallavalle S., Contente M. L., Pinto A. (2022). Efficient 2-step enzymatic cascade for the bioconversion of oleuropein into hydroxytyrosol. Antioxidants 11:260. doi: 10.3390/antiox11020260, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  12. Che R., Qin J., Tahmasbian I., Wang F., Zhou S., Xu Z., et al. (2018). Litter amendment rather than phosphorus can dramatically change inorganic nitrogen pools in a degraded grassland soil by affecting nitrogen-cycling microbes. Soil Biol. Biochem. 120, 145–152. doi: 10.1016/j.soilbio.2018.02.006 [DOI] [Google Scholar]
  13. Chow C.-E. T., Kim D. Y., Sachdeva R., Caron D. A., Fuhrman J. A. (2014). Top-down controls on bacterial community structure: microbial network analysis of bacteria, T4-like viruses and protists. ISME J. 8, 816–829. doi: 10.1038/ismej.2013.199, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  14. Clemmensen K. E., Finlay R. D., Dahlberg A., Stenlid J., Wardle D. A., Lindahl B. D. (2015). Carbon sequestration is related to mycorrhizal fungal community shifts during long‐term succession in boreal forests. New Phytol. 205, 1525–1536. doi: 10.1111/nph.13208, PMID: [DOI] [PubMed] [Google Scholar]
  15. Czarnota M. A., Rimando A. M., Weston L. A. (2003). Evaluation of root exudates of seven sorghum accessions. J. Chem. Ecol. 29, 2073–2083. doi: 10.1023/A:1025634402071 [DOI] [PubMed] [Google Scholar]
  16. Dai Z., Yu M., Chen H., Zhao H., Huang Y., Su W., et al. (2020). Elevated temperature shifts soil N cycling from microbial immobilization to enhanced mineralization, nitrification and denitrification across global terrestrial ecosystems. Glob. Chang. Biol. 26, 5267–5276. doi: 10.1111/gcb.15211, PMID: [DOI] [PubMed] [Google Scholar]
  17. Duan M., Lu J., Yang W., Lu M., Wang J., Li S., et al. (2022). Metabarcoding and metabolome analyses reveal mechanisms of Leymus chinensis growth promotion by fairy ring of Leucocalocybe mongolica. J. Fungi. 8:944. doi: 10.3390/jof8090944, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  18. Edwards J., Johnson C., Santos-Medellín C., Lurie E., Podishetty N. K., Bhatnagar S., et al. (2015). Structure, variation, and assembly of the root-associated microbiomes of rice. Proc. Natl. Acad. Sci. 112, E911–E920. doi: 10.1073/pnas.1414592112, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  19. Feng J., Jiang D., Shang H., Dong M., Wang G., He X., et al. (2013). Barcoding poplars (Populus L.) from Western China. PLoS One 8:e71710. doi: 10.1371/journal.pone.0071710, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  20. Fernández-González A. J., Cardoni M., Gómez-Lama Cabanás C., Valverde-Corredor A., Villadas P. J., Fernández-López M., et al. (2020). Linking belowground microbial network changes to different tolerance level towards Verticillium wilt of olive. Microbiome 8:11. doi: 10.1186/s40168-020-0787-2, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  21. Floc’H J. B., Hamel C., Harker K. N., St-Arnaud M. (2020). Fungal communities of the canola rhizosphere: keystone species and substantial between-year variation of the rhizosphere microbiome. Microb. Ecol. 80, 762–777. doi: 10.1007/s00248-019-01475-8 [DOI] [PubMed] [Google Scholar]
  22. Gottel N. R., Castro H. F., Kerley M., Yang Z., Pelletier D. A., Podar M., et al. (2011). Distinct microbial communities within the endosphere and rhizosphere of Populus deltoides roots across contrasting soil types. Appl. Environ. Microbiol. 77, 5934–5944. doi: 10.1128/AEM.05255-11, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  23. Gu Y., Wang X., Yang T., Friman V., Geisen S., Wei Z., et al. (2020). Chemical structure predicts the effect of plant-derived low-molecular weight compounds on soil microbiome structure and pathogen suppression. Funct. Ecol. 34, 2158–2169. doi: 10.1111/1365-2435.13624 [DOI] [Google Scholar]
  24. Guo R., Ji S., Wang Z., Zhang H., Wang Y., Liu Z. (2021). Trichoderma asperellum xylanases promote growth and induce resistance in poplar. Microbiol. Res. 248:126767. doi: 10.1016/j.micres.2021.126767, PMID: [DOI] [PubMed] [Google Scholar]
  25. Gupta R., Keppanan R., Leibman-Markus M., Rav David D., Elad Y., Ment D., et al. (2021). The entomopathogenic fungi Metarhizium brunneum and Beauveria bassiana promote systemic immunity and confer resistance to a broad range of pests and pathogens in tomato. Phytopathology 112, 784–793. doi: 10.1094/PHYTO-08-21-0343-R, PMID: [DOI] [PubMed] [Google Scholar]
  26. Hawkins C., Ginzburg D., Zhao K., Dwyer W., Xue B., Xu A., et al. (2021). Plant metabolic network 15: a resource of genome-wide metabolism databases for 126 plants and algae. J. Integr. Plant Biol. 63, 1888–1905. doi: 10.1111/jipb.13163, PMID: [DOI] [PubMed] [Google Scholar]
  27. Hogan J. A., Baraloto C., Ficken C., Clark M. D., Weston D. J., Warren J. M. (2021). The physiological acclimation and growth response of POPULUS TRICHOCARPA to warming. Physiol. Plant. 173, 1008–1029. doi: 10.1111/ppl.13498, PMID: [DOI] [PubMed] [Google Scholar]
  28. Huang K. L., Tian J., Wang H., Fu Y.-F., Li Y., Zheng Y., et al. (2021). Fatty acid export protein BnFAX6 functions in lipid synthesis and axillary bud growth in Brassica napus. Plant Physiol. 186, 2064–2077. doi: 10.1093/plphys/kiab229, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  29. Jiang Y., Li S., Li R., Zhang J., Liu Y., Lv L., et al. (2017). Plant cultivars imprint the rhizosphere bacterial community composition and association networks. Soil Biol. Biochem. 109, 145–155. doi: 10.1016/j.soilbio.2017.02.010 [DOI] [Google Scholar]
  30. Jiang J., Song Z., Yang X., Mao Z., Nie X., Guo H., et al. (2017). Microbial community analysis of apple rhizosphere around Bohai gulf. Sci. Rep. 7:8918. doi: 10.1038/s41598-017-08398-9, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  31. Jiao S., Chen W., Wei G. (2017). Biogeography and ecological diversity patterns of rare and abundant bacteria in oil-contaminated soils. Mol. Ecol. 26, 5305–5317. doi: 10.1111/mec.14218, PMID: [DOI] [PubMed] [Google Scholar]
  32. Jiao S., Yang Y., Xu Y., Zhang J., Lu Y. (2020). Balance between community assembly processes mediates species coexistence in agricultural soil microbiomes across eastern China. ISME J. 14, 202–216. doi: 10.1038/s41396-019-0522-9, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  33. Kundel D., Bodenhausen N., Jørgensen H. B., Truu J., Birkhofer K., Hedlund K., et al. (2020). Effects of simulated drought on biological soil quality, microbial diversity and yields under long-term conventional and organic agriculture. FEMS Microbiol. Ecol. 96:fiaa205. doi: 10.1093/femsec/fiaa205, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  34. Levins R. (1968). Evolution in Changing Environments: Some Theoretical Explorations. Princeton, NJ: Princeton University Press. [Google Scholar]
  35. Li X., Chen J., Zhang Q., Li X. F., Zhou X., Tao Y. (2021). Microbial community responses to multiple soil disinfestation change drivers. Appl. Microbiol. Biotechnol. 105, 6993–7007. doi: 10.1007/s00253-021-11528-z, PMID: [DOI] [PubMed] [Google Scholar]
  36. Li J., Luo Z., Zhang C., Qu X., Chen M., Song T., et al. (2020). Seasonal variation in the rhizosphere and non-rhizosphere microbial community structures and functions of camellia yuhsienensis Hu. Microorganisms 8:1385. doi: 10.3390/microorganisms8091385, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  37. Li H., Qiu Y., Yao T., Han D., Gao Y., Zhang J., et al. (2021). Nutrients available in the soil regulate the changes of soil microbial community alongside degradation of alpine meadows in the northeast of the Qinghai-Tibet plateau. Sci. Total Environ. 792:148363. doi: 10.1016/j.scitotenv.2021.148363, PMID: [DOI] [PubMed] [Google Scholar]
  38. Li F., Zhang S., Wang Y., Li Y., Li P., Chen L., et al. (2020). Rare fungus, Mortierella capitata, promotes crop growth by stimulating primary metabolisms related genes and reshaping rhizosphere bacterial community. Soil Biol. Biochem. 151:108017. doi: 10.1016/j.soilbio.2020.108017 [DOI] [Google Scholar]
  39. Lin H., Liu C., Li B., Dong Y. (2020). Trifolium repens L. regulated phytoremediation of heavy metal contaminated soil by promoting soil enzyme activities and beneficial rhizosphere associated microorganisms. J. Hazard. Mater. 402:123829. doi: 10.1016/j.jhazmat.2020.123829, PMID: [DOI] [PubMed] [Google Scholar]
  40. Liu K., Ding X., Wang J. (2020). Soil metabolome correlates with bacterial diversity and co-occurrence patterns in root-associated soils on the Tibetan plateau. Sci. Total Environ. 735:139572. doi: 10.1016/j.scitotenv.2020.139572, PMID: [DOI] [PubMed] [Google Scholar]
  41. Liu G., Pfeifer J., de Brito Francisco R., Emonet A., Stirnemann M., Gübeli C., et al. (2018). Changes in the allocation of endogenous strigolactone improve plant biomass production on phosphate-poor soils. New Phytol. 217, 784–798. doi: 10.1111/nph.14847, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  42. Liu J., Sui Y., Yu Z., Shi Y., Chu H., Jin J., et al. (2015). Soil carbon content drives the biogeographical distribution of fungal communities in the black soil zone of Northeast China. Soil Biol. Biochem. 83, 29–39. doi: 10.1016/j.soilbio.2015.01.009 [DOI] [Google Scholar]
  43. Longa C., Nicola L., Antonielli L., Mescalchin E., Zanzotti R., Turco E., et al. (2017). Soil microbiota respond to green manure in organic vineyards. J. Appl. Microbiol. 123, 1547–1560. doi: 10.1111/jam.13606, PMID: [DOI] [PubMed] [Google Scholar]
  44. Lu R.K. (1999). Soil and Agro-Chemistry Analytical Methods. Beijing: China Agricultural Science & Technology Press. [Google Scholar]
  45. Lu T., Ke M., Lavoie M., Jin Y., Fan X., Zhang Z., et al. (2018). Rhizosphere microorganisms can influence the timing of plant flowering. Microbiome 6:231. doi: 10.1186/s40168-018-0615-0, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  46. Ma J., Wan D., Duan B., Bai X., Bai Q., Chen N., et al. (2018). Genome sequence and genetic transformation of a widely distributed and cultivated poplar. Plant Biotechnol. J. 17, 451–460. doi: 10.1111/pbi.12989, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  47. Ma L., Yang L., Liu W., Zhang Y., Zhou Q., Wu Z., et al. (2021). Effects of root exudates on rhizosphere bacteria and nutrient removal in pond-ditch circulation systems (PDCSs) for rural wastewater treatment. Sci. Total Environ. 785:147282. doi: 10.1016/j.scitotenv.2021.147282, PMID: [DOI] [PubMed] [Google Scholar]
  48. Macías-Rodríguez L., Contreras-Cornejo H. A., Adame-Garnica S. G., Del-Val E., Larsen J. (2020). The interactions of Trichoderma at multiple trophic levels: inter-kingdom communication. Microbiol. Res. 240:126552. doi: 10.1016/j.micres.2020.126552, PMID: [DOI] [PubMed] [Google Scholar]
  49. Mattos G. N., Tonon R. V., Furtado A. A., Cabral L. M. (2017). Grape by-product extracts against microbial proliferation and lipid oxidation: a review: grape by-products with antimicrobial and antioxidant potential. J. Sci. Food Agric. 97, 1055–1064. doi: 10.1002/jsfa.8062, PMID: [DOI] [PubMed] [Google Scholar]
  50. Min K., Freeman C., Kang H., Choi S.-U. (2015). The regulation by phenolic compounds of soil organic matter dynamics under a changing environment. Biomed. Res. Int. 2015, 1–11. doi: 10.1155/2015/825098, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  51. Ning D., Deng Y., Tiedje J. M., Zhou J. (2019). A general framework for quantitatively assessing ecological stochasticity. Proc. Natl. Acad. Sci. 116, 16892–16898. doi: 10.1073/pnas.1904623116, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  52. Pandit S. N., Kolasa J., Cottenie K. (2009). Contrasts between habitat generalists and specialists: an empirical extension to the basic metacommunity framework. Ecology 90, 2253–2262. doi: 10.1890/08-0851.1, PMID: [DOI] [PubMed] [Google Scholar]
  53. Patterson A., Flores-Rentería L., Whipple A., Whitham T., Gehring C. (2019). Common garden experiments disentangle plant genetic and environmental contributions to ectomycorrhizal fungal community structure. New Phytol. 221, 493–502. doi: 10.1111/nph.15352, PMID: [DOI] [PubMed] [Google Scholar]
  54. Qin Y., Pan X. Y., Jin W., Chen L. Q., Yuan Z. L. (2018). Comparison of four extraction methods of soil microbiome in poplar plantation. Sci. Silvae Sin. 9, 169–176. doi: 10.11707/j.1001-7488.20180919 [DOI] [Google Scholar]
  55. Rädecker N., Pogoreutz C., Voolstra C. R., Wiedenmann J., Wild C. (2015). Nitrogen cycling in corals: the key to understanding holobiont functioning. Trends Microbiol. 23, 490–497. doi: 10.1016/j.tim.2015.03.008, PMID: [DOI] [PubMed] [Google Scholar]
  56. Ramond J. B., Jordaan K., Díez B., Heinzelmann S. M., Cowan D. A. (2022). Microbial biogeochemical cycling of nitrogen in arid ecosystems. Microbiol. Mol. Biol. Rev. 86:e0010921. doi: 10.1128/mmbr.00109-21, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  57. Rozpądek P., Domka A. M., Nosek M., Ważny R., Jędrzejczyk R. J., Wiciarz M., et al. (2018). The role of strigolactone in the cross-talk between Arabidopsis thaliana and the endophytic fungus Mucor sp. Front. Microbiol. 9:441. doi: 10.3389/fmicb.2018.00441, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  58. Song Y., Chen P., Xuan A., Bu C., Liu P., Ingvarsson P. K., et al. (2021). Integration of genome wide association studies and co-expression networks reveal roles of PtoWRKY 42-PtoUGT76C1-1 in trans-zeatin metabolism and cytokinin sensitivity in poplar. New Phytol. 231, 1462–1477. doi: 10.1111/nph.17469, PMID: [DOI] [PubMed] [Google Scholar]
  59. Song Y., Ci D., Tian M., Zhang D. (2016). Stable methylation of a non-coding RNA gene regulates gene expression in response to abiotic stress in Populus simonii. J. Exp. Bot. 67, 1477–1492. doi: 10.1093/jxb/erv543, PMID: [DOI] [PubMed] [Google Scholar]
  60. Song Y., Li X., Yao S., Yang X., Jiang X. (2020). Correlations between soil metabolomics and bacterial community structures in the pepper rhizosphere under plastic greenhouse cultivation. Sci. Total Environ. 728:138439. doi: 10.1016/j.scitotenv.2020.138439, PMID: [DOI] [PubMed] [Google Scholar]
  61. Su X., Su X., Yang S., Zhou G., Ni M., Wang C., et al. (2020). Drought changed soil organic carbon composition and bacterial carbon metabolizing patterns in a subtropical evergreen forest. Sci. Total Environ. 736:139568. doi: 10.1016/j.scitotenv.2020.139568, PMID: [DOI] [PubMed] [Google Scholar]
  62. Sui X., Zhang R., Frey B., Yang L., Liu Y., Ni H., et al. (2021). Soil physicochemical properties drive the variation in soil microbial communities along a forest successional series in a degraded wetland in northeastern China. Ecol. Evol. 11, 2194–2208. doi: 10.1002/ece3.7184, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  63. Sun N., Bu Y., Pan C., Wu X., Cao Y., Jing Y. (2021). Analyses of microstructure and dynamic deposition of cell wall components in xylem provide insights into differences between two black poplar cultivars. Forests 12:972. doi: 10.3390/f12080972, PMID: 33717448 [DOI] [Google Scholar]
  64. Tong S., Yuan M., Liu Y., Li X., Jin D., Cheng X., et al. (2021). Ergosterol-targeting fusion antifungal peptide significantly increases the Verticillium wilt resistance of cotton. Plant Biotechnol. J. 19, 926–936. doi: 10.1111/pbi.13517, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  65. Tya B., Jxab C., Zzb C., Ywa B. (2021). Biochar-based fertilizer amendments improve the soil microbial community structure in a karst mountainous area. Sci. Total Environ. 794:148757. doi: 10.1016/j.scitotenv.2021.148757, PMID: [DOI] [PubMed] [Google Scholar]
  66. Veach A. M., Chen H., Yang Z. K., Labbe A. D., Engle N. L., Tschaplinski T. J., et al. (2020). Plant hosts modify belowground microbial community response to extreme drought. mSystems 5:5. doi: 10.1128/mSystems.00092-20, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  67. Veach A. M., Morris R., Yip D. Z., Yang Z. K., Engle N. L., Cregger M. A., et al. (2019). Rhizosphere microbiomes diverge among Populus trichocarpa plant-host genotypes and chemotypes, but it depends on soil origin. Microbiome 7:76. doi: 10.1186/s40168-019-0668-8, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  68. Veyisoglu A., Tatar D., Saygin H., Inan K., Cetin D., Guven K., et al. (2016). Microvirga makkahensis sp. nov., and microvirga arabica sp. nov., isolated from sandy arid soil. Antonie Van Leeuwenhoek 109, 287–296. doi: 10.1007/s10482-015-0631-z, PMID: [DOI] [PubMed] [Google Scholar]
  69. Vives-Peris V., de Ollas C., Gómez-Cadenas A., Pérez-Clemente R. M. (2020). Root exudates: from plant to rhizosphere and beyond. Plant Cell Rep. 39, 3–17. doi: 10.1007/s00299-019-02447-5, PMID: [DOI] [PubMed] [Google Scholar]
  70. Wagg C., Bender S. F., Widmer F., van der Heijden M. G. A. (2014). Soil biodiversity and soil community composition determine ecosystem multifunctionality. Proc. Natl. Acad. Sci. 111, 5266–5270. doi: 10.1073/pnas.1320054111, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  71. Wakabayashi T., Ishiwa S., Shida K., Motonami N., Suzuki H., Takikawa H., et al. (2021). Identification and characterization of sorgomol synthase in sorghum strigolactone biosynthesis. Plant Physiol. 185, 902–913. doi: 10.1093/plphys/kiaa113, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  72. Wang Y., Hou L., Wu X., Zhu M., Dai Y., Zhao Y. (2021). Mycorrhiza helper bacterium Bacillus pumilus HR10 the improves growth and nutritional status of Pinus thunbergii by promoting mycorrhizal proliferation. Tree Physiol. 42, 907–918. doi: 10.1093/treephys/tpab139, PMID: [DOI] [PubMed] [Google Scholar]
  73. Wang J., Liu L., Gao X., Hao J., Wang M. (2021). Elucidating the effect of biofertilizers on bacterial diversity in maize rhizosphere soil. PLoS One 16:e0249834. doi: 10.1371/journal.pone.0249834, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  74. Wang W., Talide L., Viljamaa S., Niittylä T. (2022). Aspen growth is not limited by starch reserves. Curr. Biol. 32, 3619–3627.e4. doi: 10.1016/j.cub.2022.06.056 [DOI] [PubMed] [Google Scholar]
  75. Wanichthanarak K., Boonchai C., Kojonna T., Chadchawan S., Sangwongchai W., Thitisaksakul M. (2020). Deciphering rice metabolic flux reprograming under salinity stress via in silico metabolic modeling. Comput. Struct. Biotechnol. J. 18, 3555–3566. doi: 10.1016/j.csbj.2020.11.023, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  76. Wu N., Li Z., Meng S., Wu F. (2021). Soil properties and microbial community in the rhizosphere of Populus alba var. pyramidalis along a chronosequence. Microbiol. Res. 250:126812. doi: 10.1016/j.micres.2021.126812, PMID: [DOI] [PubMed] [Google Scholar]
  77. Wu X., Liu J., Meng Q., Fang S., Kang J., Guo Q. (2021). Differences in carbon and nitrogen metabolism between male and female Populus cathayana in response to deficient nitrogen. Tree Physiol. 41, 119–133. doi: 10.1093/treephys/tpaa108, PMID: [DOI] [PubMed] [Google Scholar]
  78. Xing M., Wang Q., Li X., Li Y., Zhou X. (2021). Selection of keystone species based on stable carbon and nitrogen isotopes to construct a typical food web on the shore of Xingkai Lake, China. Ecol. Indic. 132:108263. doi: 10.1016/j.ecolind.2021.108263 [DOI] [Google Scholar]
  79. Ye X., Li Z., Luo X., Wang W., Li Y., Li R., et al. (2020). A predatory myxobacterium controls cucumber fusarium wilt by regulating the soil microbial community. Microbiome 8:49. doi: 10.1186/s40168-020-00824-x, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  80. Yoneyama K. (2020). Recent progress in the chemistry and biochemistry of strigolactones. J. Pestic. Sci. 45, 45–53. doi: 10.1584/jpestics.D19-084, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  81. Zhang Y., Zhao L., Zhao J., Li Y., Wang J., Guo R., et al. (2017). S5H/DMR6 encodes a salicylic acid 5-hydroxylase that fine-tunes salicylic acid homeostasis. Plant Physiol. 175, 1082–1093. doi: 10.1104/pp.17.00695, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  82. Zhang L., Zhou J., George T. S., Limpens E., Feng G. (2021). Arbuscular mycorrhizal fungi conducting the hyphosphere bacterial orchestra. Trends Plant Sci. 27, 402–411. doi: 10.1016/j.tplants.2021.10.008, PMID: [DOI] [PubMed] [Google Scholar]
  83. Zhao M., Zhao J., Yuan J., Hale L., Wen T., Huang Q., et al. (2021). Root exudates drive soil-microbe-nutrient feedbacks in response to plant growth. Plant Cell Environ. 44, 613–628. doi: 10.1111/pce.13928, PMID: [DOI] [PubMed] [Google Scholar]
  84. Zheng W., Zheng Q., Xue Y., Hu J., Gao M.-T. (2017). Influence of rice straw polyphenols on cellulase production by Trichoderma reesei. J. Biosci. Bioeng. 123, 731–738. doi: 10.1016/j.jbiosc.2017.01.009, PMID: [DOI] [PubMed] [Google Scholar]
  85. Zhou S., Geng B., Li M., Li Z., Liu X., Guo H. (2021). Comprehensive analysis of environmental factors mediated microbial community succession in nitrogen conversion and utilization of ex situ fermentation system. Sci. Total Environ. 769:145219. doi: 10.1016/j.scitotenv.2021.145219, PMID: [DOI] [PubMed] [Google Scholar]
  86. Zhou X., Wang J.-T., Zhang Z.-F., Li W., Chen W., Cai L. (2020). Microbiota in the rhizosphere and seed of rice from China, with reference to their transmission and biogeography. Front. Microbiol. 11:995. doi: 10.3389/fmicb.2020.00995, PMID: [DOI] [PMC free article] [PubMed] [Google Scholar]
  87. Zhou X., Zhang X., Ma C., Wu F., Jin X., Dini-Andreote F., et al. (2022). Biochar amendment reduces cadmium uptake by stimulating cadmium-resistant PGPR in tomato rhizosphere. Chemosphere 307:136138. doi: 10.1016/j.chemosphere.2022.136138, PMID: [DOI] [PubMed] [Google Scholar]
  88. Zhu Q., Yan K., Dong Y., Wang Y. (2022). Rhizosphere bacterial communities and soil nutrient conditions reveal sexual dimorphism of Populus deltoides. J. For. Res. 33, 1–11. doi: 10.1007/s11676-022-01517-x [DOI] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Data Availability Statement

The data presented in the study are deposited in the Sequence Read Archive repository, accession number PRJNA888251, https://www.ncbi.nlm.nih.gov/bioproject/PRJNA888251.


Articles from Frontiers in Microbiology are provided here courtesy of Frontiers Media SA

RESOURCES