Analysis of the sequencing data
A total of 1,434,573 effective tags of fungal samples were obtained after filtering low-quality and other unsuitable sequences. The number of effective tags per sample ranged from 72,677 to 84,744, and the average number of clean reads was 79,699 per sampled group. The sequence lengths of all samples are mainly concentrated in 200-300bp and 300-400bp, accounting for 89.9% and 10.0% respectively. The quality of the sequencing data was evaluated mainly through the statistics of sequence number, sequence length, GC content, Q20 and Q30 quality values, effective ratio, and other parameters in each sample (Table 1).
Table 1
The statistics and quality evaluation of the sequencing data.
Sample
|
Raw_Tags
|
Valid Tags
|
Q20(%)
|
Q30(%)
|
GC(%)
|
Valid(%)
|
CDR_1
|
87444
|
84744
|
99.31
|
97.35
|
52.54
|
96.91
|
CDR_2
|
85883
|
81799
|
99.10
|
96.50
|
53.74
|
95.24
|
CDR_3
|
80058
|
75929
|
99.31
|
97.21
|
53.11
|
94.84
|
CDS_1
|
85964
|
83838
|
99.44
|
97.65
|
52.09
|
97.53
|
CDS_2
|
82868
|
79893
|
99.51
|
97.88
|
54.59
|
96.41
|
CDS_3
|
82394
|
80274
|
99.47
|
97.80
|
55.60
|
97.43
|
CDY_1
|
81011
|
79162
|
99.52
|
97.90
|
54.67
|
97.72
|
CDY_2
|
83619
|
81254
|
99.71
|
98.58
|
55.33
|
97.17
|
CDY_3
|
85349
|
83548
|
99.49
|
97.75
|
53.94
|
97.89
|
QXR_1
|
80931
|
75692
|
99.17
|
96.78
|
55.47
|
93.53
|
QXR_2
|
82683
|
77556
|
99.67
|
98.31
|
54.46
|
93.80
|
QXR_3
|
81931
|
75342
|
99.48
|
97.72
|
52.79
|
91.96
|
QXS_1
|
85104
|
82224
|
99.59
|
98.09
|
55.67
|
96.62
|
QXS_2
|
83886
|
72677
|
99.60
|
98.25
|
53.26
|
86.64
|
QXS_3
|
81085
|
78158
|
98.82
|
95.87
|
56.20
|
96.39
|
QXY_1
|
84574
|
82311
|
99.54
|
97.98
|
56.57
|
97.32
|
QXY_2
|
84803
|
81718
|
99.57
|
98.06
|
55.37
|
96.36
|
QXY_3
|
80351
|
78454
|
99.11
|
96.66
|
54.11
|
97.64
|
The rarefaction curves, displaying the relationship between the number of reads and operational taxonomic units (OTUs) in each sample, exhibited a stable plateau with the increase of the sample size (Fig. 1A), indicating that the sequencing depth and the number of OTUs were sufficient for each sample to represent the fungal communities and continue with further analyses. The rarefaction curves also showed that leaf samples had the highest abundance of fungal species, while root samples had the lowest. The Good’s coverage values for the eighteen samples ranged from 98.2–100% (Fig. 1B), also indicating that the sequencing data confidently reflected the structure of the endophytic fungi community of the samples.
Taxonomic Analysis Of Endophytic Fungi
A total of 2,521 operational taxonomic units (OTUs) was yielded in six groups, and 1,829 and 1,288 OTUs were totally detected in ChengDu samples and Qixianhu samples, respectively. Moreover, a total of 140 OUTs and 102 OUTs were common to ChengDu samples and Qixianhu samples, respectively (Fig. 2A, Fig. 2B). As depicted in the petal diagram, 25 common OTUs were present in each sample’s, indicating that there may be great differences in endophytic fungi between the two areas due to different ecological conditions (Fig. 2C).
The taxonomic distribution of endophytic fungi in the roots, stems and leaves of H. serrata was displayed in Fig. 3. After screening out rare OTUs, the remaining OTUs represented 9 phyla, 40 classes, 102 orders, 228 families, and 430 genera, respectively. At the level of phyla, the operational taxonomic units (OTU) were assigned into 8 known fungal, which were Ascomycota, Basidiomycota, Zygomycota, Glomeromycota, Chytridiomycota, Olpidiomycota, Mucoromycota, Mortierellomycota. According to the results of multiple sequence alignment of features feature sequences of these phyla, the evolutionary tree of feature sequences is constructed (Fig. 3A). Among them, the predominant phylum was Ascomycota (54.34%, 41.14%-62.30%), followed by Basidiomycota (41.51%, 32.42%-57.17%), Fungi_unclassified (1.83%, 0.49%-3.34%), Zygomycota (0.58%, 0.15%-3.41%) and Glomeromycota (0.62%, 0%-3.52%). Basidiomycota, Ascomycota, Zygomycota and Olpidiomycota were found in all tested samples. Otherwise, all the Glomeromycota were found in the root samples and the stem samples, but not found in leaf samples from two sites. Chytridiomycota and Mucoromycota were only found in the roots samples from Chengdu (CD), but not found in Qixianhu (QX). In addition, Mucoromycota and Mortierellomycota were only found in the root samples and leaf samples from ChengDu (CD), respectively. At the genus level, a total of 430 distinct fungal genera were identified, and the compositions and proportions of the genera was significantly different among in different tissues and different ecological areas. The genus Ascomycota was the most abundant in leaf and stem samples (CDY, CDS, QXY, QXS), with relative abundances ranging from 21.45–28%. While, Ascomycota genus was relative low abundance in root samples, with the relative abundance were 0.77% and 1.67% in CDR and QXR, respectively. And Piskurozyma genus showed similar features. In contrast, Cladophialophora and Mycena genera were more abundant in root samples than in leaf and stem sample. It is remarkable to mention that Sebacina was the second dominant genus in ChengDu samples (CDR, CDS and CDY), which account for 18.54%, 15.74% and 11.76%, respectively, but it was hardly detected in Qixianhu samples (QXR, QXS and QXY). (Fig. 3B).
The top 9 classes were selected to make a heatmap clustering, which further indicated that species distributions differed greatly across the three tissue samples and different ecological areas. The heat-map representation of the results showed that the root samples, i.e., CDR and QXR clustered together, exhibiting a relatively similar community structure (Fig. 3D). The top 30 genera (i.e., those with relative abundance > 1%) were also selected to make a heatmap clustering (Figure. 3d). At the genus level, Auricularia and Mycena were the dominant genus in root sample (CDR and QXR), while Mortierella, Pestalotiopsis, Cladophialophora Agaricomycetes, and Herpotrichiellaceae were more abundant in the QXR samples than in CDR samples. The results of fungal communities showed that CDR and QXR samples clustered together, as did CDS and QXS, CDY and QXY, exhibiting a relatively similar community structure. The results hinted that the origin of endophytic fungi in roots is different from that in leaves and stems.
Alpha diversity analyses of the endophytic fungal communities in H. serrata. from different ecological areas
Alpha diversity analyses, including Shannon, Simpson, Chao1 and ACE indices, were conducted by Wilcoxon rank-sum test, characterize differences in fungal community abundances and diversities in different groups. The results of the alpha diversity analysis of the fungal communities indicated that the Simpson index of the six samples was no significant (Fig. 4A). Specifically, the Shannon index of CDS and CDY samples was significantly higher than CDR samples (P < 0.05) (Fig. 4B). The Chao1 index of the CDS samples were significantly higher than CDR and QXR, and QXR samples was significantly lower than except five samples (P < 0.05) (Fig. 4C). The ACE index of the CDR samples was significantly lower than CDS and CDY samples and the ACE index of QXR samples was significantly lower than QXS and QXY (P < 0.05) (Fig. 4D).
Beta diversity analyses of the endophytic fungal communities in H. serrata. from different ecological areas
To evaluate differences in endophytic fungal composition among different samples in H. serrata, beta diversity analysis was performed. A principal coordinate analysis (PCoA) based on the unweighted Unifrac distance matrix was conducted to show the relationship between the different H. serrata. samples (Fig. 5). In the PCoA result, the first axis explained 21.95% of the data’s variability and the second axis explained 16.8%. And the results revealed that the structures of the fungal communities of the stem and leaf samples (CDS and CDY, QXS and QXY) clustered near each other, while the endophytic fungal communities in roots (CDR and QXR) was distinctly separated from those of the stems and leaves (CDS and CDY, QXS and QXY) (Fig. 5A). Moreover, the endophytic fungal communities of two root samples (CDR and QXR) from different nature populations were distinctly separated. Similarly, the structures of the fungal communities of stem and leaf samples from two nature populations were also separated. Similar results were found for Non-metric multidimensional scaling (NMDS) analysis, hinting that the endophytic fungal communities from H. serrata displayed a strong separation based on the plant tissues and natural populations (Fig. 5B).
UPGMA tree was conducted by unweighted unifrac method based on the genus level. Important distinctions were found in the composition of fungal communities in two area’s root, stem, and leaf samples. Two different clusters were observed, the endophytic fungal communities from leaf and stem samples clustered together (CDS, CDY QXS and QXY), while the root sample clustered alone and distinctly separated from those of the stem and leaf samples (CDR and QXR). Otherwise, the endophytic fungal communities of the leaf samples and stem samples in same ecological areas (CDS to CDY, QXS to QXY) were more like than that of different ecological areas (CDS to QXS, CDY to QXY) (Fig. 5C). The results suggest that the endophytic fungal communities of the root sample might have specie-specific and those of the leaf and stem samples probably have ecological specificity.
Linear discriminant analysis effect size (LEfSe) analysis was employed to determine different taxon abundances of endophytic fungi among the six tissues from two ecological areas. Concerning the different tissues and ecological areas, a total of 53 biomarkers were employed to discern significant differences with an LDA score greater than 3.0. The LEfSe analysis showed more taxa with statistically significant abundance in CDs followed by CDR and CDY in Chengdu samples with an LDA score greater than 3.0 at the genus level. The CDY samples contain more Tremellales_unclassified and Tremellomycetes_unclassified CDS samples contain more Piskurozyma, Strelitziana, Pleosporales_unclassified, Spizellomycetaceae_unclassified, Rhinocladiella, Halosphaeriaceae_unclassified, Tremella and Veronaea. And Auricularia, Gliocladium, Ilyonectria, Cotylidia, Clavulinopsis, Olpidiaceae_unclassified and Chaetothyriaceae_unclassified are more abundant in CDR (Fig. 6A). On the other hand, more taxa with statistically significant abundance in QXR followed by QXY and QXS as well. At the genus level, Auricularia, Glomus, Rhizophagus and Glomeraceae_unclassified were significantly enriched in QXR samples, while Eurotiomycetes_unclassified, Tremellales_unclassified and Strelitziana were more abundant in QXY samples. And Septobasidium and Teichosporaceae_unclassified were significantly enriched in QXS samples (Fig. 6b).
Correlation Analysis Between Fungal Endophytes Diversity And Hup A Content
The content of Hup A in different samples was quantified by high performance
liquid chromatography (HPLC) (Fig. 7). The retention time of standard Hup A was 17.989 min and the HPLC spectrum of Hup A standard is shown in Fig. 7A. The results showed that the content of Hup A in roots (CDR and QXR) was significantly lower than that in stems and leaves. The Hup A content from Qixianhu samples was significantly higher than that from ChengDu samples, hinting that Hup A content might have variety specificity (Fig. 7B). The correlation between the top 30 OTUs of endophytic fungal community and Hup A content is depicted using Pearson heat map (Fig. 8). There were 7 genera ( Fungi_unclassified, Pestalotiopsis, Rhodotorula, Ascomycota_unclassified, Cyphellophora, Sporobolomyces and Trichomeriaceae_unclassified) were significantly and positively correlated to Hup A content of Chengdu samples(CI ≥ 0.95), while, there were 7 genera (Mortierella, Russula, Auricularia, Mycena, Tomentella, Chaetothyriales_unclassified and Cladophialophora) were significantly and negatively correlated to Hup A content of Chengdu samples(CI≤- 0.95) (Fig. 8A). On the other hand, there were 10 genera (Carlosrosaea, Ascomycota_unclassified, Sporobolomyces, Fungi_unclassified, Trichomeriaceae_unclassified, Basidiomycota_unclassified, Chaetothyriales_unclassified, Bionectria, Phialophora and Trechispora) were significantly and positively correlated to Hup A content of Qixianhu samples (CI ≥ 0.95), and there were 7 genera (Fungi_unclassified, Pestalotiopsis, Rhodotorula, Ascomycota_unclassified, Cyphellophora, Sporobolomyces and Trichomeriaceae_unclassified) were significantly and negatively correlated to Hup A content of Chengdu samples(CI≤-0.95) (Fig. 8B). In which, there are 6 genera (Ascomycota_unclassified, Cyphellophora, Fungi_unclassified, Sporobolomyces and Trichomeriaceae_unclassified) were significantly and correlated to Hup A content in all two areas, whereas, there are 6 genera (Auricularia, Cladophialophora, Cryptococcus, Mortierella and Mycena) were significantly and negatively correlated to Hup A content of in all two areas. These genera which showed positively or negatively correlated Hup A content of in all two areas may probably have species specific. However, those genera which showed positively or negatively correlated Hup A content of in only one area may probably have eco-environmental specificity.