Plant pot experiments
In this study, a pot experiment was conducted to investigate the impact of different concentrations of indole-3-acetic acid (IAA) on the rhizosphere and endosphere fungal communities associated with E. ulmoides. The experiment included three concentration levels of IAA: 10 µM, 100 µM, and 1000 µM, alongside a blank control group, with three replicates per treatment. In April 2023, 2 kg of pre-mixed soil was placed in plastic pots, and each pot was sown with 5 surface-sterilized seeds of E. ulmoides (Huazhong 8), which had undergone a germination promotion treatment following a 2-minute soak in 75% alcohol. A total of 48 pots were sown to ensure there were enough seedlings with consistent growth for hormone spraying. Once the E. ulmoides seedlings developed cotyledons, 3 healthy and well-growing seedlings were retained per pot, while 2 seedlings with poorer growth were removed. To protect the seedlings from rainwater, white plastic sheds were erected over them in an open field setting. Soil moisture levels were maintained by adjusting with sterile water to ensure optimal growth conditions for each pot of seedlings. Natural ambient temperature was maintained throughout the experiment, and no external carbon sources were introduced. By May 2023, when the E. ulmoides seedlings reached four weeks of age, 36 pots showing uniform growth were randomly assigned to four groups: a blank control (CK) and three treatment groups (10 µM IAA, 100 µM IAA, and 1000 µM IAA). Each group consisted of 3 pots for subsequent analysis. Referring to the described method (Gupta et al. 2022) for preparing the required hormone aqueous solution, first dissolve the plant hormone in a small amount of NaOH solution, and then dilute it to the desired concentration with water, and add Tween 20 (100 µl L− 1). The blank control plants were treated with a NaOH solution containing Tween 20. Using a sprayer, 15 mL of hormone solution was evenly sprayed onto the leaves of 3 E. ulmoides seedlings in each pot once a week for 8 weeks. At the conclusion of the experiment, rhizosphere and endosphere soil samples from each treatment replicate were collected, thoroughly mixed, and stored at -80°C for total DNA extraction.
Results and Analysis
Effects of IAA foliar sprays on fungal community diversity in the underground niche of E. ulmoides
Through ITS gene deep sequencing, a total of 6451 ASVs were identified across 12 rhizosphere soil samples of E. ulmoides, representing taxa from 13 phyla, 36 classes, 73 orders, 137 families, 210 genera, and 262 species. Similarly, 26280 ASVs were detected in 12 endosphere samples, encompassing taxa from 16 phyla, 47 classes, 106 orders, 217 families, 421 genera, and 582 species. The impact of foliar IAA spray on fungal community diversity in both rhizosphere and endosphere niches of E. ulmoides was analyzed using the ACE richness index (Fig. 1).
Results indicated that the influence of IAA treatment on fungal community diversity in both rhizosphere and endosphere niches was not statistically significant, although there was an increasing trend in fungal diversity with higher hormone concentrations (Fig. 1A). For instance, the ACE index for rhizosphere fungal communities of E. ulmoides in the 10 µM, 100 µM, and 1000 µM IAA treatment groups were 427.77, 502.26, and 560.70, respectively. In the endosphere samples of E. ulmoides, the ACE index in these treatment groups were 1969.04, 1913.90, and 2100.18, respectively, indicating a dose-dependent effect of IAA on fungal diversity.
Furthermore, the study revealed that fungal community diversity in the endosphere of E. ulmoides was significantly higher than that in the rhizosphere fungal communities across both control and IAA treatment groups (Fig. 1B).
Effect of IAA foliar sprays on fungal community composition in the underground niche of E. ulmoides
In the rhizosphere niche of E. ulmoides (Fig. 2A), the dominant fungal community in the control group was Galactomyces (15.60%). Foliar application of IAA would affect the composition of the rhizosphere fungal community of E. ulmoides, with greater changes observed at higher hormone concentrations. Specifically, in the 10 µM IAA treatment group, Galactomyces remains the dominant genus in the rhizosphere fungal community, but its relative abundance shifts to 18.26%. In the 100 µM IAA treatment group, the dominant genus in the rhizosphere fungal community shifts to an unclassified genus of Fungi, with a relative abundance of 26.58%. Similarly, in the 1000 µM IAA treatment group, the rhizosphere fungal community is dominated by unclassified of Fungi (15.35%), all of which were low-abundance genera in the control group.
In the endosphere niche (Fig. 2B), foliar application of IAA had minimal effect on fungal community composition. For instance, Fusarium exhibited a relative abundance of 3.28% in the control group, and with 10 µM IAA, 100 µM IAA, and 1000 µM IAA treatments, it showed relative abundances of 4.31%, 2.74%, and 3.47% respectively, with no significant changes observed. Overall, the foliar application of IAA had little impact on the fungal community composition in the endosphere niche.
Effects of IAA foliar sprays on fungal community function in the underground niche of E. ulmoides
Based on the FUNGuild platform, 67 and 77 ecological functional groups were identified by annotating fungal communities in the rhizosphere and endosphere niches of E. ulmoides, respectively. Both niches shared several functional groups, such as Arbuscular Mycorrhizal, Soil Saprotroph, Animal Pathogen, and Dung Saprotroph-Plant Saprotroph. Additionally, each niche harbored unique functional groups. Specifically, the rhizosphere niche had seven exclusive functional types, including Lichenized-Undefined Saprotroph, Endophyte-Plant Pathogen-Undefined Saprotroph, and Endophyte-Plant Pathogen. The endosphere niche similarly featured seven unique functional types, such as Dung Saprotroph-Endophyte, Dung Saprotroph-Endophyte-Undefined Saprotroph, and Ectomycorrhizal-Undefined Saprotroph (Fig. 3A).
Regardless of the rhizosphere or endosphere niche, the dominant functional type among fungal communities in the control treatment was Undefined Saprotroph. Results indicated that foliar application of IAA influenced fungal community functions in both rhizosphere and endosphere niches of E. ulmoides, with specific functional groups enriched across different IAA concentration treatments. For instance, under 100 µM IAA treatment, the rhizosphere niche showed enrichment in Animal Pathogen-Undefined Saprotroph (26.17%) and Soil Saprotroph (11.51%), while the endosphere niche was enriched in Arbuscular Mycorrhizal (18.81%) and Plant Pathogen (10.43%). Notably, under 1000 µM IAA treatment, differences in dominant functional groups like Plant Pathogen (7.69%) and Dung Saprotroph (5.55%) in the rhizosphere niche versus Arbuscular Mycorrhizal (28.98%) and Plant Pathogen (9.95%) in the endosphere niche were observed (Fig. 3B). The PCoA plot (Fig. 3C) illustrated distinctions in fungal community characteristics between rhizosphere and endosphere niches under 100 µM IAA treatment, while showing similar β diversity characteristics, suggesting functional similarity in fungal communities across both niches.
Comparison of the effects of IAA foliar sprays on the fungal communities in the rhizosphere and endosphere of E. ulmoides
Linear discriminant analysis (LDA) was employed to analyze the impact of different concentrations of IAA on fungal communities within the rhizosphere and endosphere of E. ulmoides. The study revealed higher specificity of fungal communities in the rhizosphere compared to the endosphere. Specifically, at the genus level, 13 fungal genera such as Aspergillus、Hemileucoglossum、unclassified of Helotiaceae、unclassified of Pseudeurotiaceae、Pseudaleuria、Teunomyces、Galactomyces、Pleiocarpon、Conlarium、Clavulina、Solicoccozyma、unclassified of Chytridiomycota、Entrophospora 13 fungal genera were significantly associated with the rhizosphere niche of E. ulmoides (Fig. 4A, C), whereas only Neofusicoccum, Tausonia, and one undefined genus correlated significantly with the endosphere niche (Fig. 4B, D). These findings indicate that foliar application of IAA had a more pronounced effect on rhizosphere fungal communities than on endosphere communities. The higher the LDA value, the greater the contribution to the differences between groups, indicating that this microbial group is a more important biomarker than other microorganisms. Under the control group and three different concentrations of IAA, the taxonomic compositions of fungal communities in the rhizosphere and endosphere niches of E. ulmoides showed significant differences. However, the number of taxa showing significant abundance differences was highest in the 1000 µM IAA concentration treatment group, regardless of whether in the rhizosphere or endosphere niches. Specifically, in the rhizosphere niche fungal community of the treatment group, there were 14 taxa with significant differences in abundance, includin 1 class (Pezizomycetes), 2 orders (Pezizales, Ohygenales), 3 families (Aspergillaceae, Mycosphaerellaceae, Piskurozymaceae), 4 genera (Aspergillus, Pseudaleuria, Solicoccozyma, unclassified of Helotiaceae) and three species (Aspergillus-versicolor, Candida-metapsilosis, unclassified of Helotiaceae, unidentified) (Fig. 4A, C). In the endosphere niche, the number of taxa with significant abundance differences in the fungal community was 8, including 1 class (Pucciniomycetes), 2 orders (Capnodiales, Septobasidiales), 1 family (Septobasidiaceae), 1 genus (Neofusicoccum) and 3 species (Setophoma-vemoniae, Neofusicoccum-italicum, Neosetophma-rosigene) (Fig. 4B, D).