Skip to main content
PMC home page
Frontiers in Microbiology logoLink to Frontiers in Microbiology
. 2022 May 24;13:874582. doi: 10.3389/fmicb.2022.874582

Altitudinal Distribution Patterns of Phyllosphere Microbial Communities and Their Contribution to Silage Fermentation of Kobresia pygmaea Along the Elevation Gradient on the Tibetan Plateau

Xin Yang 1,†, Yuhong Bao 2,3,†, Tao Shao 1, Wenkang Wang 1, Pengfei Ma 1, Wenbo Wang 1, Antonio Gallo 4, Xianjun Yuan 1,*
PMCID: PMC9173736  PMID: 35685941

Abstract

The study aimed to reveal altitudinal distribution patterns of phyllosphere microbial communities and silage fermentation of Kobresia pygmaea along the elevation gradient on the Tibetan Plateau. The K. pygmaea was individually collected from 2,500, 3,000, 4,000, 4,500, and 5,000 m above sea level (a.s.l.) on the Tibetan Plateau and ensiled for 60 days, respectively. The phyllosphere bacterial diversity increased while fungal diversity decreased along the elevation gradient, and bacterial and fungal richness showed a unimodal distribution with peak abundance at 4,000 and 3,000 m a.s.l., respectively. After 60 days of ensiling, the bacterial and fungal community composition changed but did not exhibit clear altitudinal distribution patterns. All K. pygmaea underwent a weak fermentation indicated by pH above 5.0 and low ratio of lactic/acetic acid (LA/AA). The S5000 and S3000 showed the highest and lowest pH, respectively. Although Lactobacillus dominated S4000 after 60 days of ensiling, S4000 still exhibited poor fermentation quality as well as silages from the other four regions. The higher ammonia N concentrations in S3000 and S4000 than the other silages were consistent with the detectable butyric acid in S3000 and S4000. The silage fermentation of K. pygmaea collected from five regions exhibited poor fermentation quality, thereby inoculating lactic acid bacteria to K. pygmaea before ensiling is highly recommended to improve fermentation quality on the Tibetan Plateau.

Keywords: elevational gradients, Kobresia pygmaea, fermentation quality, Tibetan Plateau, bacterial diversity, fungal diversity

Introduction

The Tibetan Plateau, known as the “roof of the world,” has a unique ecosystem, which is characterized by extreme environmental conditions, including low temperature, strong ultraviolet rays, and hypoxia. The Tibetan Plateau harbors vast areas of alpine meadow; however, the forage yields are too low to feed the domestic animals, resulting in feed deficiency during the long cold period of a year (Zhou et al., 2017). Therefore, ensiling is a preferred forage preservation strategy to alleviate the seasonal unbalance of feed supply on the Tibetan Plateau. Ensiling fermentation is a complex biological process driven by epiphytic lactic acid bacteria (LAB) under anaerobic conditions, thus, the phyllosphere microbial flora played a critical role during ensiling (McAllister et al., 2018). It is well known that environmental factors affected the microbial community that played a significant role in ecosystem functioning and primary production (Handley, 2019). The Tibetan Plateau harbors unique microorganisms because it is geographically and ecologically distinct. Microbial abundance and species diversity vary considerably along environmental gradients across the plateau (Dong et al., 2010); however, the distribution patterns of phyllosphere microbial communities in Kobresia pygmaea along the elevation gradient on the Tibetan Plateau are still unclear.

Unraveling the distribution pattern of phyllosphere microbial communities on the Tibetan Plateau has been attracting the growing scientific interests of ecologists. The phyllosphere microbiome has been shown to play an important role in the adaptation of the plant host to different environmental stressors by enhancing tolerance to heat, cold, drought, and salinity (Al Ashhab et al., 2021). Investigating the change in bacterial communities along the altitudinal gradient will shed light on the prediction of future climatic changes scenario (Yuan et al., 2014). Wei et al. (2022) characterized the microbial community composition and metabolic capacity in Qinghai-Tibet Plateau high-altitude areas (with an altitude of 4,555 m) and confirmed that Qinghai-Tibet Plateau is a huge and valuable resource bank in which more new non-resistant antibiotics and many other bioactive substances could be developed. Characterizing the microbial community composition is important for forage preservation because phyllosphere microbial flora play a critical role in ensiling fermentation and provide sufficient fodder for local livestock during winter and spring. Thus, surveys on phyllosphere microbial community composition will reveal the key and dominant microorganism in grass along altitudinal gradients, which might be useful as a potential application in silage fermentation in the different regions of the Tibetan Plateau.

Kobresia pygmaea is an important forage resource in the Qinghai-Tibet Plateau and is essential in maintaining the ecological balance of grasslands. K. pygmaea is widely distributed in temperate to cold zones of the Himalayas and Hengduan Mountains because they are tolerant to cold, radiation, drought, and strong wind (Can et al., 2020). Ding et al. (2020) proposed that the harsh and unique environment contributed to the unique epiphytic microbial community of forages on the Tibetan Plateau compared to other regions worldwide, which subsequently influenced silage fermentation quality of native grasses.

The study aimed to reveal the altitudinal distribution of phyllosphere microbial community and evaluate their contributions to silage fermentation of K. pygmaea harvested from five elevation gradients on the Tibetan Plateau. We hypothesized that (1) the epiphytic fungal and bacterial communities in K. pygmaea varied along the elevation gradient on the Tibetan Plateau and (2) the variation in microbial communities might affect the silage fermentation of K. pygmaea.

Materials and Methods

Sampling Area and Silage Preparation

Kobresia pygmaea was individually collected from 2,500, 3,000, 4,000, 4,500, and 5,000 m above sea level (a.s.l.) on the Tibetan Plateau. The exact coordinates and climatic characteristics of the sampling sites are shown in Supplementary Table S1. For each elevation gradient, five plots (100 × 50 m block) with vegetation coverage of K. pygmaea above 80% were chosen for parallel sampling, and the grass plots were open terrain and far away from residential areas. Five squares (50 × 50 cm) per plot were chosen for fresh K. pygmaea collecting. All collected fresh forage were mixed and chopped into lengths of 2–3 cm with a paper cutter. Then, about 500 g of chopped grasses were packed into polyethylene plastic bags (dimensions 270 × 300 mm) and vacuum-sealed tightly, and five bags for each elevation gradient were prepared. All bags were taken to the laboratory in Lhasa and stored at ambient temperature (20–25°C) for 60 days. At the same time, the fresh forages in quintuplicate per elevation gradient were taken for immediate microbial population analyses and DNA extraction, and a portion of fresh forages (80 g) was sampled for dry matter (DM) and chemical composition analyses.

Laboratory Analyses

Five bags per elevation gradient were opened after 60 days of ensiling, then all silages of each bag were poured into an ethanol-sterilized plastic container and mixed thoroughly. One subsample (80 g) of fresh K. pygmaea and silage was dried in a forced-air oven at 65°C for 48 h for the determination of DM. Then, dried samples were ground in a laboratory knife grinder (FW100, Taisite Instrument Co., Ltd, Tianjin, China) to pass a 1-mm sieve. Ground samples were used for total nitrogen (TN), crude protein (CP), water-soluble carbohydrate (WSC), neutral detergent fiber (NDF), and acid detergent fiber (ADF) analyses. The TN content was determined with a Kjeltec Analyzer (Kjeltec 8400 -Analyzer, FOSS Analytical AB, Höganäs, Sweden), and the CP content was calculated by multiplying the TN by 6.25 (Krishnamoorthy et al., 1982). The WSC content was analyzed by colorimetry after reacting with the Throne reagent (Thomas, 1977). An ANKOM 200 fiber analyzer (ANKOM Technologies, Macedon, NY, USA) was used to determine the NDF and ADF according to the Van Soest procedures, a thermostable α-amylase was used, and the results were expressed on a DM basis, including residual ash.

A subsample of silage (20 g wet basis) was diluted with 60 ml distilled water and stored at 4°C for 24 h. The silage extract was filtered through four layers of cheesecloth and Whatman filter paper (Hangzhou Xinhua Co., Ltd., China). The pH of the extract was measured immediately using a glass electrode pH meter (Hanna Instruments Italia Srl, Padua, Italy). Ammonia N was measured according to the phenol-hypochlorite method (Broderick and Kang, 1980). One subsample (5 ml) of silage extract was centrifuged at 12,000 × g for 10 min at 4°C, and the supernatant was filtered through a 0.45-μm membrane for organic acid analysis. Organic acids were quantified using a high-performance liquid chromatography system (Agilent HPLC 1260, Agilent Technologies, Inc., Waldbronn, Germany) equipped with a refractive index detector.

A subsample of fresh or silage (10 g) was mixed and homogenized with 90 ml of sterile sodium chloride solution (0.85%) for 1 min. The homogenate was filtered through four layers of cheesecloth, then 1 ml of the filtrate was serially diluted for microorganism counting, and the remaining solution was filtered through four layers of medical gauze for DNA extraction. The numbers of LAB were counted on deMan, Rogosa, and Sharp agar after 48 h of incubation at 37°C under anaerobic conditions. The Enterobacteriaceae were counted on purple-red bile glucose agar after 24 h of incubation at 37°C under aerobic conditions. The numbers of yeast and molds were counted on potato dextrose agar after culturing for 48–72 h under aerobic conditions at 28°C. The numbers of aerobic bacteria were counted on the nutrient agar medium (Qingdao Haibo Biotechnology Co., Ltd) after aerobic incubation for 2 days at 37°C. Microbial data was obtained in the form of colony-forming units (CFU) and converted to a logarithmic scale on a fresh weight (FW) basis.

Microbial Community Analyses

Three replicates of fresh or silage per elevation gradient were randomly chosen for microbial community analyses by sequencing the bacterial 16S rRNA V3–V4 region and the fungal internal transcribed spacer (ITS) region. The DNA extraction solution was centrifuged at 10,000 × g for 15 min, then the supernatant was discarded, and the pellet was resuspended by 100 μl of autoclaved Ringer's solution. Microbial DNA was extracted using the Fast DNA SPIN Kit for Soil (MP Biomedicals, Solon, OH, USA) following the protocol provided by the manufacturer. The quantity and quality of DNA were evaluated using NanoDrop 2000 ultraviolet-visible spectrophotometer (Thermo Scientific, Wilmington, DE, USA), and DNA quality was checked by 1% agarose gel electrophoresis. The bacterial 16S rRNA V3–V4 regions were amplified based on the specific primers 338F (ACTCCTACGGGAGGCAGCAG) and 806R (GGACTACHVGGGTWTCTAAT). The primers ITS1F (5′-CTTGGTCATTTAGAGGAAGTAA-3′) and ITS2aR (5′-GCTGCGTTCTTCATCGATGC-3′) were used to amplify fungal ITS. The purified PCR amplicons were paired-end sequenced using the Illumina MiSeq PE300 platform (Illumina Inc., San Diego, CA, USA). Sequences have been deposited in the NCBI Short Read Archive database under BioProject PRJNA742870.

The sequence was first quality-controlled to remove mismatches and ambiguous readings. Then, operational taxonomic units (OTUs) were clustered with a 97% similarity cutoff using UPARSE (version 7.1). Bacterial community structure was analyzed at the phylum and genus levels using the Silva database (release 138) with a confidence threshold of 70%, respectively. Fungal community structure was analyzed at the phylum and genus levels using the Unite 8.0 database (release 8.0) with a confidence threshold of 70%, respectively. Alpha-diversity estimates and beta-diversity evaluation, based on principal coordinate analysis (PCoA), were performed using the Phyloseq and Vegan packages on R. The distance-based redundancy analysis was used to examine the relationship between bacterial communities and environmental factors, whereas canonical correspondence analysis (CCA) was used to examine the relationship between fungal communities and environmental factors with Canoco for Windows 4.5 (Microcomputer Power, Ithaca, NY, USA).

Statistical Analysis

The chemical composition and microbial populations of fresh K. pygmaea and silages were analyzed as a completely randomized design using the GLM procedure of SAS (version 9.3; SAS Institute Inc., Cary, NC) with a model that included the elevation gradient effect. A polynomial contrast was used to test the linear or quadratic effects of elevation gradient on parameters measured. The data of bacterial and fungal diversity were analyzed as a completely randomized factorial design in a 2 (fresh and silage) × 5 (elevation gradients) factorial arrangement, with the main effect of elevation gradient, ensiling, and their interactions by the GLM procedure of SAS. If significance was detected for a specific effect or interaction (p ≤ 0.05), data were analyzed using Tukey's test.

Results

Chemical Composition and Microbial Populations in Fresh K. pygmaea

The chemical composition and microbial populations of fresh K. pygmaea along the elevation gradient on the Tibetan Plateau are shown in Table 1. The DM contents of fresh K. pygmaea ranged from 283 to 561 g kg−1, and the elevation gradient had a significant influence on DM contents with a linear and quadratic effect (p < 0.01). The NDF (p = 0.358) and ADF (p = 0.193) contents were similar for all fresh K. pygmaea. The elevation gradient significantly affected CP content with a linear and quadratic effect (p < 0.01). The elevation gradient significantly affected WSC content with a linear effect (p < 0.01). The numbers of LAB, yeast and molds were affected by elevation gradient with a quadratic effect (p = 0.011). The elevation gradient significantly affected the numbers of Enterobacteriaceae and aerobic bacteria with a linear and quadratic effect (p < 0.01).

Table 1.

The chemical composition (g kg−1 DM basis unless stated otherwise) and microbial populations (log 10 CFU g−1 FW) of fresh K. pygmaea along the elevation gradient on the Tibetan Plateau.

Item Altitude1 SEM2 P-value Contrast P-values
F2500 F3000 F4000 F4500 F5000 Linear Quadratic
Dry matter (g kg−1 FW) 295d 283d 315c 359b 561a 27.4 <0.01 <0.01 <0.01
Neutral detergent fiber 422 450 455 460 463 6.9 0.358 0.077 0.381
Acid detergent fiber 201 238 214 221 220 4.9 0.193 0.484 0.241
Crude protein 108c 128b 158a 128b 131b 4.4 <0.01 <0.01 <0.01
Water-soluble carbohydrate 16.3a 10.7b 14.3a 9.83b 9.02b 0.796 <0.01 <0.01 0.555
Lactic acid bacteria 3.00b 5.03a 3.40b 3.77ab 3.00b 0.232 <0.01 0.228 0.011
Yeast and Molds 2.30ab 3.31a 2.79ab 2.40ab 2.00b 0.149 0.019 0.065 0.011
Enterobacteriaceae 5.26b 6.66a 5.24b 5.26b 4.00c 0.229 <0.01 <0.01 <0.01
Aerobic bacteria 5.80b 6.66a 6.13ab 5.41b 4.00c 0.248 <0.01 <0.01 <0.01
Open in a new tab
a−d

Values within the same row with different letters are significantly different (p < 0.05).

1

F2500, F3000, F4000, F4500, and F5000 represent fresh K. pygmaea at corresponding altitude gradients.

2

SEM, standard error of the mean.

Chemical Composition, Microbial Populations, and Fermentation Quality of K. pygmaea Silages After 60 Days of Ensiling

The chemical composition, microbial population, and fermentation profiles of K. pygmaea silage along the elevation gradient are shown in Tables 2, 3. Quadratic effect (p < 0.01) of elevation gradient on DM and CP contents was detected. The elevation gradient significantly affected contents of ADF with linear (p < 0.01) effect. The WSC contents in silage linearly (p < 0.01) increased with increasing elevation gradient. There was a quadratic effect (p < 0.01) of elevation gradient on the numbers of Enterobacteriaceae and aerobic bacteria. The LAB numbers in silages linearly (p < 0.01) declined with the increasing elevation gradient. The silage pH linearly (p < 0.01) increased with the increasing elevation gradient. The elevation gradient affected (p < 0.01) the LA concentration with the highest LA values in S3000. The AA concentration exhibited the quadratic (p < 0.01) effect with the lowest AA concentration in S4500. A similar PA concentration was observed in S2500, S3000, and S4000 silage, and it was not detected in S4500 and S5000 silages. The BA was solely detected in S3000 and S4000 silages. Linear and quadratic effects (p < 0.01) of elevation gradient on ammonia N concentration were detected.

Table 2.

The chemical composition (g kg−1 DM basis unless stated otherwise) and microbial populations (log 10 CFU g−1 FW) of ensiled K. pygmaea along the elevation gradient on the Tibetan Plateau.

Item Altitude1 SEM2 P-value Contrast P-values
S2500 S3000 S4000 S4500 S5000 Linear Quadratic
Dry matter (g kg−1 FW) 280c 278c 261d 351b 567a 33.0 <0.01 <0.01 <0.01
Neutral detergent fiber 453ab 480a 389b 443ab 439ab 9.6 0.015 0.194 0.157
Acid detergent fiber 270a 261a 185b 209b 196b 9.8 <0.01 <0.01 0.016
Crude protein 107c 116c 143a 131b 142ab 3.9 <0.01 <0.01 <0.01
Water-soluble carbohydrate 5.56b 5.41b 5.53b 5.79b 7.13a 0.176 <0.01 <0.01 <0.01
Lactic acid bacteria 7.49a 5.00c 6.91b 5.39c 5.00c 0.282 <0.01 <0.01 0.105
Yeast and molds 2.26 3.09 2.55 2.42 3.55 0.202 0.234 0.174 0.530
Enterobacteriaceae 5.18ab 3.00c 3.50bc 5.21ab 5.41a 0.303 <0.01 0.046 <0.01
Aerobic bacteria 6.41ab 5.75bc 5.04c 6.27ab 7.00a 0.198 <0.01 0.047 <0.01
Open in a new tab
a−d

Values within the same row with different letters are significantly different (p < 0.05).

1

S2500, S3000, S4000, S4500, and S5000 represent K. pygmaea silage after 60 days of ensiling at corresponding altitude gradients.

2

SEM, standard error of the mean.

Table 3.

Fermentation profiles of K. pygmaea silage along the elevation gradient on the Tibetan Plateau.

Item Altitude1 SEM2 P-value Contrast P-values
S2500 S3000 S4000 S4500 S5000 Linear Quadratic
pH 5.25bc 5.24c 5.40bc 5.72ab 5.75a 0.055 <0.01 <0.01 0.070
Lactic acid (g kg−1 DM) 26.3bc 42.1a 18.9cd 30.6b 16.3d 2.57 <0.01 <0.01 <0.01
Acetic acid (g kg−1 DM) 24.8ab 20.0bc 19.7bc 14.0c 29.3a 1.55 <0.01 0.605 <0.01
Lactic/acetic acid 1.08bc 2.15ab 0.98c 2.29a 0.56c 0.204 <0.01 0.256 <0.01
Propionic acid (g kg−1 DM) 8.99 8.28 8.60 0.00 0.00 1.485 0.051 <0.01 0.449
Butyric acid (g kg−1 DM) 0.00b 14.3a 2.88b 0.00b 0.00b 1.563 <0.01 0.512 <0.01
Ammonia N (g kg−1 TN) 33.6c 78.9a 51.2b 26.4c 11.4d 6.25 <0.01 <0.01 <0.01
Open in a new tab
a−d

Values within the same row with different letters are significantly different (p < 0.05).

1

S2500, S3000, S4000, S4500, and S5000 represent K. pygmaea silage after 60 days of ensiling at corresponding altitude gradients.

2

SEM, standard error of the mean.

Bacterial and Fungal Communities of Fresh and Ensiled K. pygmaea Along the Elevation Gradient on the Tibetan Plateau

Sequencing bacterial 16S rRNA V3–V4 and fungal ITS regions resulted in 1,747,180 and 2,001,636 reads, respectively. The Good's coverage values were greater than 99% for all samples, indicating that the depth of sequencing was adequate for reliable analysis of the bacterial and fungal communities. Rarefaction curves plateaued in all samples, indicating that the number of reads used in the analysis was sufficient for identifying OTU. The α-diversity indexes of the bacterial and fungal communities of fresh and ensiled K. pygmaea are shown in Table 4. There was an interaction between elevation gradient and ensiling for bacterial Shannon (p < 0.01) and Chao 1 (p = 0.018) indexes. The bacterial Shannon index was similar among all fresh grasses, whereas S5000 showed the lowest bacterial Shannon index among all silages. The Chao 1 index in F4000 was the highest among all fresh grasses, whereas S5000 showed the lowest Chao 1 index among silages. There was an interaction (p < 0.01) between elevation gradient and ensiling for fungal Shannon (p < 0.01) and Chao 1 (p = 0.017) indexes. F5000 showed the lowest fungal Shannon index among fresh grasses, whereas there was no significant difference in Shannon index among all silages. The fungal Chao 1 index in F3000 was the highest among all fresh grasses, whereas in S4000 it was the highest among all silages.

Table 4.

The α-diversity indexes of the bacterial and fungal communities of K. pygmaea along the elevation gradient on the Tibetan Plateau.

Item Bacterial community Fungal community
Shannon Chao 1 Shannon Chao 1
Altitudes Fresh Silage Fresh Silage Fresh Silage Fresh Silage
2,500 2.75 2.89a 416b 223ab 3.36a 2.74 228bc 359ab
3,000 2.81 2.59a 482ab 262a 3.64a 1.45 460a 393ab
4,000 3.19 2.34ab 659a 245a 2.44ab 3.46 332ab 444a
4,500 3.56 2.33ab 561ab 199ab 2.89ab 2.01 130c 323b
5,000 3.33 1.64b 340b 157b 1.20b 2.58 180bc 294b
K. pygmaea
Fresh 3.13a 492a 2.71a 266b
Silage 2.35b 217b 2.45b 362a
Altitudes
2,500 2.82 319bc 3.05 294bc
3,000 2.70 372ab 2.55 426a
4,000 2.77 452a 2.95 388ab
4,500 2.94 380ab 2.45 226c
5,000 2.49 248c 1.89 237c
SEM1 0.110 31.4 0.193 29.3
Effects and interactions
Elevation gradient 0.206 <0.01 0.168 <0.01
Ensiling <0.01 <0.01 0.409 <0.01
Elevation gradient × Ensiling <0.01 0.018 <0.01 0.017
Open in a new tab
a−c

Values within the same column with different letters were significantly different (p < 0.05).

1

SEM, standard error of the mean.

The unweighted PCoA UniFrac plots revealed differences in the bacterial and fungal communities of fresh and ensiled K. pygmaea (Figure 1). For the bacterial community, principal component 1 (PC1) and principal component 2 (PC2) explained 30.75 and 18.08% of total variation, respectively (Figure 1A). The fresh grasses and silages were separated in the plot, and the fresh material harvested from low altitudes was separated from that of high altitudes. The PCoA plot revealed a clear separation and difference in the distribution and structure of the fungal communities between fresh and ensiled K. pygmaea, and the PC1 and PC2 explained 20.43 and 16.49% of total variation, respectively (Figure 1B). The fresh K. pygmaea were separated from silages. The fresh K. pygmaea and silages harvested from 5000 m were clustered far from samples harvested from other altitudes.

Figure 1.

Figure 1

Open in a new tab

The unweighted principal coordinate analysis (PCoA) of bacterial (A) and fungal (B) community of K. pygmaea along the elevation gradient on the Tibetan Plateau. F2500, F3000, F4000, F4500, and F5000 represent samples of fresh K. pygmaea at corresponding altitude gradients. S2500, S3000, S4000, S4500, and S5000 represent samples of K. pygmaea silages at corresponding altitude gradients. Percentage variation explained by each PCoA is indicated on the axis.

A total of 23 bacterial genera with relative abundance (RA) above 5% were detected in samples (Figure 2A). Enterobacter, Exiguobacterium, and Sphingomonas were the dominant genera in F2500. Enterobacter was the most dominant genus in F3000. Weissella and Sphingomonas were the dominant genera in F4000. Sphingomonas was the most dominant genus in F5000 and F4500. After 60 days of ensiling, Enterococcus, Lactococcus, and Lactobacillus accounted for 28, 16.5, and 6.4% of the total sequence in S2500, respectively. Hafnia-Obesumbacterium, unclassified_f_Enterobacteriaceae, Enterobacter, and Enterococcus accounted for 29, 23.8, 13.3, and 9.6% of all sequences in S3000, respectively. Lactobacillus and Enterococcus accounted for 64 and 9.4% of the total sequence in S4000, respectively. Weissella and Enterococcus accounted for 31 and 22% of the total sequence in S4500, respectively. Enterobacter, unclassified_f_Enterobacteriaceae, Weissella, and Lactobacillus accounted for 37, 22, 17, and 9.3% of the total sequence in S5000.

Figure 2.

Figure 2

Open in a new tab

The bacterial (A) and fungal (B) community on genus levels of fresh and ensiled K. pygmaea along the elevation gradient on the Tibetan Plateau. F2500, F3000, F4000, F4500, and F5000 represent samples of fresh K. pygmaea at corresponding altitude gradients. S2500, S3000, S4000, S4500, and S5000 represent samples of K. pygmaea silages at corresponding altitude gradients.

For the fungal community, 27 fungal genera with RA above 5% were detected in all samples (Figure 2B). Pyrenochaetopsis and Didymella accounted for 32.3 and 10.8% of the total sequence in F2500, which decreased to 14.2 and 3.1% in F3000 silages, respectively. Auriculibuller became the most dominant genus in F3000. Saitozyma increased from 2.4% in F2500 to 30.6% of the total sequence for F4000. Unclassified_f_Helotiaceae and Unclassified_p_Ascomycota were the most dominant genera in F4500 and F5000, respectively. After 60 days of ensiling, Podospora, Phlebia, Schizophyllum, and Candida became the dominant genera in S2500. Unclassified_f_Ustilentylomataceae, Issatchenkia, and Schizophyllum were the dominant genera in S3000. S4000 had the most genera with RA above 5%, and Podospora was the most dominant genus. Schizophyllum and Cystobasidium were the dominant genera in S4500. Rhodotorula dominated the fungal community of S5000. Candida was present in all silages with the highest RA in S2500. The RA of Schizophyllum in S2500, S3000, and S4500 were above 10%. There was a quadratic trend in the RA of Issatchenkia along the elevation gradient, with the highest RA in S3000.

Effect of Elevation Gradient and Abiotic Factors on the Microbial Communities of K. pygmaea Along the Elevation Gradient

To analyze the effect of elevation gradient and abiotic factors on the microbial communities along the elevation gradient, RDA was performed for the bacterial communities of fresh and ensiled K. pygmaea. Altitude, temperature, WSC, CP, DM, and relative humidity had a significant effect on the variability of epiphytic bacterial communities and explained up to 57.13% (41.56 and 15.57% on RDA axes 1 and 2, respectively) of total variance of bacterial community (Figure 3A). In comparison, precipitation, relative humidity, temperature, and NDF had a significant effect on the bacterial communities of silages, explaining up to 58.02% (38.83 and 19.19% on RDA axes 1 and 2, respectively) (Figure 3B) of total variance of bacterial community of silages.

Figure 3.

Figure 3

Open in a new tab

Redundancy analysis of environmental factors and bacterial community of fresh (A) and ensiled (B) K. pygmaea along the elevation gradient on the Tibetan Plateau. The axes are labeled with the percentage of total variance explained (%). Red arrow lengts indicate the variance explained by environmental factors, and the blue arrow lengths indicate the variance explained by the bacterial community. T Individual samples are represented with circles, triangles, diamonds, squares, and cross. F2500, F3000, F4000, F4500, and F5000 represent samples of fresh K. pygmaea at corresponding altitude gradients. S2500, S3000, S4000, S4500, and S5000 represent samples of K. pygmaea silages at corresponding altitude gradients. T, temperature; HR, relative humidity; WSC, water-soluble carbohydrate; CP, crude protein; DM, dry matter; P, average precipitation; NDF, neutral detergent fiber.

The CCA was performed for fungal community of fresh and ensiled K. pygmaea. For the fresh K. pygmaea, relative humidity, temperature, DM, elevation gradient, and precipitation had a significant effect on the variability of fungal community of fresh K. pygmaea and were explainable up to 45.41% (26.04 and 19.37% on CCA axes 1 and 2, respectively) of total variance of fungal community (Figure 4A). In comparison, relative humidity, temperature, NDF, DM, WSC, altitude, and precipitation had a significant effect on the fungal community of K. pygmaea silages, explaining up to 33.13% (17.58 and 15.55% on CCA axes 1 and 2, respectively) (Figure 4B) of total fungal community variability.

Figure 4.

Figure 4

Open in a new tab

Canonical correspondence analysis of environmental factors and fungal community of fresh (A) and ensiled (B) K. pygmaea along the elevation gradient on the Tibetan Plateau. The canonical axes are labeled with the percentage of total variance explained (%). Red arrow lengths indicate the variance explained by environmental factors, and bright blue inverted triangle represents the interpretation of the fungal community presented as a single data point. Individual samples are represented with circles, triangles, diamonds, squares, and cross. F2500, F3000, F4000, F4500, and F5000 represent samples of fresh K. pygmaea at corresponding altitude gradients. S2500, S3000, S4000, S4500, and S5000 represent samples of K. pygmaea silages at corresponding altitude gradients. T, temperature; HR, relative humidity; WSC, water-soluble carbohydrate; DM, dry matter; P, average precipitation; NDF, neutral detergent fiber.

Discussion

Variations in Chemical Composition and Microbial Community of Fresh K. pygmaea Along the Elevation Gradient

In the Tibetan Plateau, alpine plants have developed special strategies to help survive the harsh environments, including sharp temperature shifts, strong ultraviolet radiation exposure, and low oxygen content (Li et al., 2014). The restrained plant respiration induced by decreasing temperature along the elevation gradients resulted in the accumulation of soluble carbohydrate, CP, and ether extract in cell protoplasm of the plant (Ding et al., 2020). In this study, the CP concentration of fresh K. pygmaea increased up to 15.76 g kg−1 DM at 4,000 m; however, F4500 and F5000 showed lower CP concentration and the lowest WSC concentration among all fresh grasses. This might be attributed to the advanced lignification of plant cell walls in high-elevation regions. The K. pygmaea in this study were harvested at narrower harvest window within 15 days instead of consistent growth stage, and the vegetative growth of K. pygmaea in high-elevation regions might be premature termination compared with that of the low-elevation regions. Han and Ren (2015) reported that the end of the growth season advanced 0.6 day for every 200 m higher elevations. Thus, more CP and WSC in F4500 and F5000 were embedded in lignified cell walls than other grasses.

F3000 and F5000 showed the highest and lowest microbial populations, respectively. This might be attributed to their higher and lower moistures than K. pygmaea harvested from other altitudes. It is well known that decreasing moisture (relative humidity) creates a less hospitable environment for microorganisms to grow, although different types of fungus or bacteria require different amounts of water (in vapor form) to reproduce and grow (Cabral, 2010). Microbes that have the ability to survive in extremely cold, strong ultraviolet rays, and hypoxia conditions are rare, Dong et al. (2010) also reported that bacterial isolates obtained from Tibetan lakes were either phylogenetically or physiologically unique. The lowest numbers of yeast, Enterobacteriaceae, and total bacteria in F5000 among all fresh K. pygmaea might be attributed to the harsh environment, which is characterized by low temperature, strong ultraviolet rays, and hypoxia.

Altitudinal Distribution Patterns of Microbial Community in Fresh K. pygmaea

The decrease in the phyllosphere fungal diversity might be related to the increased physiological challenges with the increasing altitude, resulting in fewer fungal species survived in the highest elevations. However, the phyllosphere bacterial diversity increased with the increasing altitude. It was well known that bacteria and archaea had higher adaptation ability to extreme environments than fungi because of the lower complexity of prokaryotic cells compared to eukaryotic fungi (Gostinčar et al., 2022). Bacterial and fungal richness showed a unimodal distribution, with peak abundance at F4000 and F3000, respectively. This is consistent with the pattern of plant richness at large spatial scales, which showed a unimodal relationship with altitude, with the peaked richness in the middle elevations (Oommen and Shanker, 2005).

Plant phyllosphere harbor a diverse variety of microorganisms, which have been shown to play an important role in the adaptation of the plant host to different environmental stressors by enhancing tolerance to heat, cold, drought, UV radiation, and salinity (Al Ashhab et al., 2021). Plants in cold environments harbor complex, host-specific, and cold-adapted microbial communities, which may play a key functional roles in plant growth and survival under cold conditions. In this study, the dominant epiphytic bacteria in fresh K. pygmaea are Enterobacter, Exiguobacterium, Curtobacterium, and Pseudomonas, which were usually isolated from cold environment. Marian et al. (2022) reviewed that Pseudomonas spp. isolated from cold environments could be used to promote plant growth under cold stress, whereas other microorganisms isolated from cold environments (e.g., Enterobacter, Exiguobacterium, and Pseudomonas) promoted plant growth under normal conditions (16–25°C), although their effect on cold-stressed plants was not yet investigated. The dominant epiphytic bacterial genera in fresh K. pygmaea also were difference from that of fresh corn cultivated in low-altitude region of Southwestern China, which was dominated by Lactobacillus, Acetobacter, Weissella, Pseudomonas, Acinetobacter, and Burkholderia (Guan et al., 2018).

Streptococcus is detected in K. pygmaea harvested from 4,000 m a.s.l. Fan et al. (2020) reported that the RA of Streptococcus in the rumen of yaks increased with altitude and proposed that these microorganisms might adapt well to low-temperature and low-oxygen environments. Sphingomonas are observed in K. pygmaea harvested from higher elevations (above 4,000 m a.s.l.). Some species of Sphingomonas can tolerate extreme cold conditions and be found in high-altitude and low-temperature environments of the Indian Himalayas (Dasauni and Nailwal, 2020) because they can produce many antioxidative enzymes to reduce the damage caused by reactive oxygen species (Luo et al., 2020). Acidiphilium and Arthrobacter were only detected in the highest elevation of 5,000 m a.s.l., where they are characterized by extreme environments. Li L. et al. (2020) performed the comparative genomic analysis on Acidiphilium to address the evolutionary history of the genus Acidiphilium and proposed that Acidiphilium originated in mild conditions and could adapt to extreme environments after the acquisition of many essential functions. Members of Arthrobacter are commonly identified in Antarctic soil communities. Dsouza et al. (2015) reported that the genomes of the seven Antarctic Arthrobacter isolates contained several features that may be beneficial for growth and survival in the Antarctic soil environment. Ge et al. (2020) also isolated four unknown strains belonging to the genus Arthrobacter from plateau wildlife on the Tibetan Plateau.

For the fungi, Pyrenocchaetopsis are present in fresh K. pygmaea from elevations below 4,000 m a.s.l., and its RA decreased with the increasing elevation. Pyrenochaetopsis was one of the rhizospheric soil fungal genera in low-altitude sites rather than high- and medium-altitude sites (Jamil et al., 2020). Protomyces and Leucosporidium are present in fresh K. pygmaea from elevations below 4,000 m a.s.l. before ensiling, and its RA increased with the increasing elevation. Rhodotorula and Saitozyma were found in all fresh K. pygmaea except F5000 with the highest RA in F4000. Rhodotorula himalayensis sp. has been isolated from Roopkund Lake of the Himalayan mountain ranges (Shivaji et al., 2008). Saitozyma pseudoflava also has been isolated from phylloplane in Tibet, China (Li A. H. et al., 2020). In the study by Touchette et al. (2022), Rhodotorula JG1 was used as a model yeast to determine its adaptations to cold temperatures and found that Rhodotorula frigidialcoholis adapted to cold temperatures in the Antarctic dry valley permafrost through a variety of mechanisms, including increasing expression of the PPP genes, increasing the production of carotenoids, sphingolipids, unsaturated fatty acid, and exopolysaccharides while coupled with a reduction in expression of growth, transcriptional and translational machinery genes. Didymella, Ariculibuller, Zymoseptoria, and Sampaiozyma are found in K. pygmaea from lower elevations (below 3,000 m a.s.l.); however, they are absent in higher elevations. Didymella and Zymoseptoria were also detected in fresh corn (Benjamim Da Silva et al., 2021; Kung et al., 2021). The exclusive presence of Unclassified_f_Helotiaceae and Unclassified_p_Ascomycota in F4500 and F5000 may be explained by a combination of geographic isolation and unique environmental conditions on the Tibetan Plateau. This indicated that high-altitude Tibetan Plateau harbor its unique assemblage of fungi, which could well be adapted to the extreme conditions.

Correlations Between Environmental Parameters and Microbial Community in Fresh K. pygmaea

Climate is one of the major factors that shape microbial communities in the nature. The variations in phyllosphere bacterial community were related to environmental and biotic factors (Al Ashhab et al., 2021). Physiological profiles of the crop concerning abiotic factors affect the availability of nutrients, water, and a wide range of secondary metabolites on the leaf surface, which further and therefore significantly affect the epiphytic microbial communities (Liu et al., 2020). Altitude is strongly influenced by the epiphytic bacterial and fungal community composition. In this study, relative humidity, temperature, and altitude have a strong effect explaining 41.56 and 15.57% in axes 1 and 2, respectively, accounting for the total variance in bacterial community composition (Figure 4A). Beattie (2002) also found that the microbial communities of leaves were significantly affected by leaves' moisture.

In the fungal community, relative humidity, temperature, and precipitation explained 26.04 and 19.37% in CCA axes 1 and 2, respectively, of the total variations of fungal community (Figure 4B). Temperature and measures of moisture availability, including relative humidity and precipitation, affected the fungal community composition. Faticov et al. (2021) have shown that the fungal community composition changed along the elevational gradient and was also affected by precipitation.

The Fermentation Profiles of K. pygmaea Along the Elevation Gradient

Ensiling without any inoculants or starter cultures is a natural and spontaneous fermentative process depending on the epiphytic microorganism. In this study, all silage pH values are above 5.0, indicating that all K. pygmaea underwent a weak LA-fermentation. Kung et al. (2018) reviewed that the ratio of LA/AA is a qualitative indicator of silage fermentation, and quality silage usually has a ratio of LA/AA about 2.5–3.0. In this study, the LA/AA of all silages ranged from 0.56 to 2.19, confirming the poor fermentation of K. pygmaea silages. Especially, S5000 silages showed the lowest LA/AA (0.56) and were dominated by the bacterial family of Enterobacteriaceae (76.59%) (Avila and Carvalho, 2020). The high AA concentrations of K. pygmaea silages in this study was attributed to the flourish of Enterobacteria, metabolizing fermentable substrates into AA (Heron et al., 1993). Most of the Enterobacteria are undesirable for silage fermentation because they compete with LAB for sugars at the beginning of ensiling; however, Enterobacteria are generally sensitive to low pH, and their counts in silage usually decline sharply when the pH falls below 4.5 (McGarvey et al., 2013). In this study, the slow decline of pH favors the proliferation of Enterobacteria.

The highest pH in S5000 silages was related to its highest DM, which could not provide sufficient moisture to support the growth of bacteria, restricting the silage fermentation. In addition, the high DM contents makes forage difficult to be compacted to generate anaerobic environment for ensiling fermentation, resulting in the enrichment of aerobic yeast, such as Rhodotorula, which are non-fermentative and strictly aerobic yeast (Hatoum et al., 2012). In this study, Rhodotorula became the dominant fungal genus in S5000 after 60 days of ensiling. In contrast, S3000 silages showed the lowest pH and highest LA concentration among all silages, which are related to their highest LAB numbers and lowest DM contents in fresh K. pygmaea. Proper moisture at harvest is essential to getting a good pack and fermentation (Borreani et al., 2018). In this study, although Lactobacillus dominated the S4000 after 60 days of ensiling, S4000 still exhibited poor fermentation quality as well as other four regions. The lack of high-efficiency LAB and fermentable substrates might contribute to the restricted fermentation of K. pygmaea.

The flourish of Enterobacteria partially contributed to the prevalence of ammonia N in silage because Enterobacteria had a proteolytic activity to produce ammonia and biogenic amines (Driehuis et al., 2018). In this study, the higher ammonia N concentrations in S3000 and S4000 than other silages were consistent with the detectable butyric acid in S3000 and S4000. Accordingly, poorly preserved silage is obtained with high contents of butyric acid and ammonia N, which is associated with clostridial activity (Buxton and Muck, 2003). The lowest ammonia N concentration in S5000 was related to its highest DM among all silages. The chances of a clostridial fermentation can be minimized by ensiling forages above 35% DM because clostridia are intolerant of high osmotic pressure (Kung et al., 2018).

In the fresh K. pygmaea before ensiling, the phyllosphere bacterial community exhibited regular altitudinal distribution pattern; however, the dominant bacterial genera in silages were absolutely different among five elevations after 60 days of ensiling. Zi et al. (2021) reported that environmental factors affected the epiphytic bacterial community of forages, which have a greater impact on the initial stage of silage fermentation, whereas their effects on the microbial communities were reduced with the process of ensiling. In addition, they suggested that geographical factors and their effect on the silage microbiome should be considered to make provisions to ensure high-quality silage production (Zi et al., 2021). In this study, the complex epiphytic microbial composition contributed to the poor fermentation quality of K. pygmaea silages. Thus, it is concluded that inoculating LAB to K. pygmaea on the Tibetan plateau before ensiling is highly recommended.

The major fungal genera identified in fresh K. pygmaea were Pyrenochaetopsis, Auriculibuller, Saitozyma, Rhodotorula, and Unclassified_f _Helotiaceae. After 60 days of ensiling, the fungal composition significantly changed, and Schizophyllum, Phodotorula, Rhodotorula, Candida, and Issatchenkia became the most dominant fungal genera in silages. Most molds do not tolerate at low pH and low-oxygen concentrations; nevertheless, yeasts can remain active due to their tolerance to low pH and their ability to ferment sugars to ethanol, allowing them to survive during the ensiling process (Avila and Carvalho, 2020). There are significant differences in fungal community among K. pygmaea 60-day silages from five regions, which may have been influenced by the initial fungal community composition of fresh material (Romero et al., 2021).

Conclusion

The altitude is a crucial factor that shapes the phyllosphere bacterial and fungal communities of K. pygmaea, which has unique bacterial and fungal community composition in high elevation gradient of the Tibetan Plateau. The natural ensiling of K. pygmaea underwent a weak LA fermentation, indicated by high pH above 5.0 and low LA/AA. Thus, considering the complex epiphytic microbial composition in fresh K. pygmaea, inoculating LAB to K. pygmaea before ensiling is highly recommended on the Tibetan Plateau.

Data Availability Statement

The original contributions presented in the study are included in the article/Supplementary Material, further inquiries can be directed to the corresponding author/s.

Author Contributions

XYu: conceiving the idea, designing the experiment, and writing—review and editing. XYa: sampling and analysis, data analysis, writing–original draft, and writing—review and editing. YB: formal analysis, methodology, and writing—review and editing. AG: writing—review and English editing. TS, WenkW, PM, and WenbW: sampling, analysis, and editing. All co-authors participated in discussions and revised the manuscript. All authors contributed to the article and approved the submitted version.

Funding

This research was supported by the National Natural Science Foundation of China (31960355), Integration and Demonstration of Crop Straw Comprehensive Utilization Technology in Tibet (XZ201901NB07), and State Key Laboratory of Barley and Yak Germplasm Resources and Genetics Improvement (Tibet Academy of Agricultural and Animal Husbandry Sciences) (XZNKY-2019-C-007K09).

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.

Acknowledgments

We are grateful to Tianzeng Song for K. pygmaea sample collection.

Supplementary Material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fmicb.2022.874582/full#supplementary-material

Click here for additional data file. (160.3KB, docx)

References

  1. Al Ashhab A., Meshner S., Alexander-Shani R., Dimerets H., Brandwein M., Bar-Lavan Y., et al. (2021). Temporal and spatial changes in phyllosphere microbiome of acacia trees growing in arid environments. Front. Microbiol. 12, 656269. 10.3389/fmicb.2021.656269 [DOI] [PMC free article] [PubMed] [Google Scholar]
  2. Avila C. L. S., Carvalho B. F. (2020). Silage fermentation-updates focusing on the performance of micro-organisms. J. Appl. Microbiol. 128, 966–984. 10.1111/jam.14450 [DOI] [PubMed] [Google Scholar]
  3. Beattie G. (2002). “Leaf surface waxes and the process of leaf colonization by microorganisms,” in Phyllosphere microbiology L. S, H. E and E. V. (APS PRESS) 3–26. [Google Scholar]
  4. Benjamim Da Silva E., Costa D. M., Santos E. M., Moyer K., Hellings E., Kung L. (2021). The effects of Lactobacillus hilgardii 4785 and Lactobacillus buchneri 40788 on the microbiome, fermentation, and aerobic stability of corn silage ensiled for various times. J. Dairy Sci. 104, 10678–10698. 10.3168/jds.2020-20111 [DOI] [PubMed] [Google Scholar]
  5. Borreani G., Tabacco E., Schmidt R. J., Holmes B. J., Muck R. E. (2018). Silage review: factors affecting dry matter and quality losses in silages. J. Dairy Sci. 101, 3952–3979. 10.3168/jds.2017-13837 [DOI] [PubMed] [Google Scholar]
  6. Broderick G. A., Kang J. H. (1980). Automated simultaneous determination of ammonia and total amino acids in ruminal fluid and in vitro media. J. Dairy Sci. 63, 64–75. [DOI] [PubMed] [Google Scholar]
  7. Buxton D. R., Muck R. E. (2003). Silage Science and Technology. Madison, WI: American Society of Agronomy. 10.2134/agronmonogr42 [DOI] [Google Scholar]
  8. Cabral J. P. (2010). Water microbiology. Bacterial pathogens and water. Int. J. Environ. Res. Public Health 7, 3657–3703. 10.3390/ijerph7103657 [DOI] [PMC free article] [PubMed] [Google Scholar]
  9. Can M., Wei W., Zi H., Bai M., Liu Y., Gao D., et al. (2020). Genome sequence of Kobresia littledalei, the first chromosome-level genome in the family Cyperaceae. Sci. Data. 7, 175. 10.1038/s41597-020-0518-3 [DOI] [PMC free article] [PubMed] [Google Scholar]
  10. Dasauni K., Nailwal T. K. (2020). “Biodiversity of microbial life: Indian Himalayan region,” in Recent Advancements in Microbial Diversity, 1.∧eds. S. De Mandal and P. Bhatt. 1 ed (Academic Press; ), 1–17. 10.1016/B978-0-12-821265-3.00001-3 [DOI] [Google Scholar]
  11. Ding Z., Bai J., Xu D., Li F., Zhang Y., Guo X. S. (2020). Microbial community dynamics and natural fermentation profiles of ensiled alpine grass elymus nutans prepared from different regions of the Qinghai-Tibetan Plateau. Front. Microbiol. 11. 10.3389/fmicb.2020.00855 [DOI] [PMC free article] [PubMed] [Google Scholar]
  12. Dong H., Jiang H., Yu B., Liu X. (2010). Impacts of environmental change and human activity on microbial ecosystems on the Tibetan Plateau, NW China. GSA Today 4–10. 10.1130/GSATG75A.1 [DOI] [Google Scholar]
  13. Driehuis F., Wilkinson J. M., Jiang Y., Ogunade I., Adesogan A. T. (2018). Silage review: Animal and human health risks from silage. J. Dairy Sci. 101, 4093–4110. 10.3168/jds.2017-13836 [DOI] [PubMed] [Google Scholar]
  14. Dsouza M., Taylor M. W., Turner S. J., Aislabie J. (2015). Genomic and phenotypic insights into the ecology of Arthrobacter from Antarctic soils. BMC Genomics 16, 36. 10.1186/s12864-015-1220-2 [DOI] [PMC free article] [PubMed] [Google Scholar]
  15. Fan Q., Wanapat M., Yan T., Hou F. (2020). Altitude influences microbial diversity and herbage fermentation in the rumen of yaks. BMC Microbiol. 20, 370. 10.1186/s12866-020-02054-5 [DOI] [PMC free article] [PubMed] [Google Scholar]
  16. Faticov M., Abdelfattah A., Roslin T., Vacher C., Hamback P., Blanchet F. G., et al. (2021). Climate warming dominates over plant genotype in shaping the seasonal trajectory of foliar fungal communities on oak. New Phytol. 231, 1770–1783. 10.1111/nph.17434 [DOI] [PubMed] [Google Scholar]
  17. Ge Y., Tao Y., Yang J., Lai X. H., Jin D., Lu S., et al. (2020). Arthrobacter yangruifuii sp. nov. and Arthrobacter zhaoguopingii sp. nov., two new members of the genus Arthrobacter. Int. J. Syst. Evol. Microbiol. 70, 5287–5295. 10.1099/ijsem.0.004414 [DOI] [PubMed] [Google Scholar]
  18. Gostinčar C., Zalar P., Gunde-Cimerman N. (2022). No need for speed: slow development of fungi in extreme environments. Fungal Biol. Rev. 39, 1–14. 10.1016/j.fbr.2021.11.002 [DOI] [Google Scholar]
  19. Guan H., Yan Y., Li X., Li X., Shuai Y., Feng G., et al. (2018). Microbial communities and natural fermentation of corn silages prepared with farm bunker-silo in Southwest China. Bioresource. Technol. 265, 282–290. 10.1016/j.biortech.2018.06.018 [DOI] [PubMed] [Google Scholar]
  20. Han Z., Ren Z. (2015). Remote sensing analysis of vegetation phenology characteristics in shaanxi province based on whittaker smoother method. J. Desert Res. 35, 901–906. [Google Scholar]
  21. Handley K. M. (2019). Determining microbial roles in ecosystem function: redefining microbial food webs and transcending kingdom barriers. mSystems 4. 10.1128/mSystems.00153-19 [DOI] [PMC free article] [PubMed] [Google Scholar]
  22. Hatoum R., Labrie S., Fliss I. (2012). Antimicrobial and probiotic properties of yeasts: from fundamental to novel applications. Front. Microbiol. 3, 421. 10.3389/fmicb.2012.00421 [DOI] [PMC free article] [PubMed] [Google Scholar]
  23. Heron S. J. E., Wilkinson J. F., Duffus C. M. (1993). Enterobacteria associated with grass and silages. J. Appl. Bacteriol. 75, 13–17. 10.1111/j.1365-2672.1993.tb03401.x [DOI] [Google Scholar]
  24. Jamil A., Yang J.-Y., Su D.-F., Tong J.-Y., Chen S.-Y., Luo Z.-W., et al. (2020). Rhizospheric soil fungal community patterns of Duchesnea indica in response to altitude gradient in Yunnan, southwest China. Can. J. Microbiol. 66, 359–367. 10.1139/cjm-2019-0589 [DOI] [PubMed] [Google Scholar]
  25. Krishnamoorthy U., Muscato T. V., Sniffen C. J., Van Soest P. J. (1982). Nitrogen fractions in selected feedstuffs. J. Dairy Sci. 65, 217–225.574520 [Google Scholar]
  26. Kung L., Savage R. M., Da Silva E. B., Polukis S. A., Smith M. L., Johnson A. C. B., et al. (2021). The effects of air stress during storage and low packing density on the fermentation and aerobic stability of corn silage inoculated with Lactobacillus buchneri 40788. J. Dairy Sci. 104, 4206–4222. 10.3168/jds.2020-19746 [DOI] [PubMed] [Google Scholar]
  27. Kung L., Shaver R. D., Grant R. J., Schmidt R. J. (2018). Silage review: Interpretation of chemical, microbial, and organoleptic components of silages. J. Dairy Sci. 101, 4020–4033. 10.3168/jds.2017-13909 [DOI] [PubMed] [Google Scholar]
  28. Li A. H., Yuan F. X., Groenewald M., Bensch K., Yurkov A. M., Li K., et al. (2020). Diversity and phylogeny of basidiomycetous yeasts from plant leaves and soil: Proposal of two new orders, three new families, eight new genera and one hundred and seven new species. Stud. Mycol. 96, 17–140. 10.1016/j.simyco.2020.01.002 [DOI] [PMC free article] [PubMed] [Google Scholar]
  29. Li L., Liu Z., Zhang M., Meng D., Liu X., Wang P., et al. (2020). Insights into the metabolism and evolution of the genus acidiphilium, a typical acidophile in acid mine drainage. mSystems 5. 10.1128/mSystems.00867-20 [DOI] [PMC free article] [PubMed] [Google Scholar]
  30. Li X., Yang Y., Ma L., Sun X., Yang S., Kong X., et al. (2014). Comparative proteomics analyses of Kobresia pygmaea adaptation to environment along an elevational gradient on the central Tibetan Plateau. PLoS ONE. 9, e98410. 10.1371/journal.pone.0098410 [DOI] [PMC free article] [PubMed] [Google Scholar]
  31. Liu H., Brettell L. E., Singh B. (2020). Linking the Phyllosphere Microbiome to Plant Health. Trends Plant Sci. 25, 841–844. 10.1016/j.tplants.2020.06.003 [DOI] [PubMed] [Google Scholar]
  32. Luo Y., Zhou M., Zhao Q., Wang F., Gao J., Sheng H., et al. (2020). Complete genome sequence of Sphingomonas sp. Cra20, a drought resistant and plant growth promoting rhizobacteria. Genomics 112, 3648–3657. 10.1016/j.ygeno.2020.04.013 [DOI] [PubMed] [Google Scholar]
  33. Marian M., Licciardello G., Vicelli B., Pertot I., Perazzolli M. (2022). Ecology and potential functions of plant-associated microbial communities in cold environments. FEMS Microbiol. Ecol. 98, fiab161. 10.1093/femsec/fiab161 [DOI] [PMC free article] [PubMed] [Google Scholar]
  34. McAllister T. A., Duniere L., Drouin P., Xu S., Wang Y., Munns K., et al. (2018). Silage review: Using molecular approaches to define the microbial ecology of silage. J. Dairy Sci. 101, 4060–4074. 10.3168/jds.2017-13704 [DOI] [PubMed] [Google Scholar]
  35. McGarvey J. A., Franco R. B., Palumbo J. D., Hnasko R., Stanker L., Mitloehner F. M. (2013). Bacterial population dynamics during the ensiling of Medicago sativa (alfalfa) and subsequent exposure to air. J. Appl. Microbiol. 114, 1661–1670. 10.1111/jam.12179 [DOI] [PubMed] [Google Scholar]
  36. Oommen M. A., Shanker K. (2005). Elevational species richness patterns emerge from multiple local mechanisms in himalayan woody plants. Ecology 86, 3039–3047. 10.1890/04-1837 [DOI] [Google Scholar]
  37. Romero J. J., Park J., Joo Y., Zhao Y., Killerby M., Reyes D. C., et al. (2021). A combination of Lactobacillus buchneri and Pediococcus pentosaceus extended the aerobic stability of conventional and brown midrib mutants-corn hybrids ensiled at low dry matter concentrations by causing a major shift in their bacterial and fungal community. J. Anim. Sci. 99. 10.1093/jas/skab141 [DOI] [PMC free article] [PubMed] [Google Scholar]
  38. Shivaji S., Bhadra B., Rao R. S., Pradhan S. (2008). Rhodotorula himalayensis sp. nov., a novel psychrophilic yeast isolated from Roopkund Lake of the Himalayan mountain ranges, India. Extremophiles 12, 375–381. 10.1007/s00792-008-0144-z [DOI] [PubMed] [Google Scholar]
  39. Thomas T. A. (1977). An automated procedure for the determination of soluble carbohydrates in herbage. J. Sci. Food Agr. 28, 639–642. [Google Scholar]
  40. Touchette D., Altshuler I., Gostincar C., Zalar P., Raymond-Bouchard I., Zajc J., et al. (2022). Novel Antarctic yeast adapts to cold by switching energy metabolism and increasing small RNA synthesis. ISME J. 16, 221–232. 10.1038/s41396-021-01030-9 [DOI] [PMC free article] [PubMed] [Google Scholar]
  41. Wei C., Sun D., Yuan W., Li L., Dai C., Chen Z., et al. (2022). Metagenomics revealing molecular profiling of microbial community structure and metabolic capacity in Bamucuo, Tibet. bioRxiv. 2022, 476867. 10.1101/2022.01.18.476867 [DOI] [PubMed] [Google Scholar]
  42. Yuan Y., Si G., Wang J., Luo T., Zhang G. (2014). Bacterial community in alpine grasslands along an altitudinal gradient on the Tibetan Plateau. FEMS Microbiol. Ecol. 87, 121–132. 10.1111/1574-6941.12197 [DOI] [PubMed] [Google Scholar]
  43. Zhou J. W., Mi J. D., Degen A. A., Ding L. M., Guo X. S., Shang Z. H., et al. (2017). Urinary purine derivatives excretion, rumen microbial nitrogen synthesis and the efficiency of utilization of recycled urea in Tibetan and fine-wool sheep. Anim. Feed Sci. Tech. 227, 24–31. 10.1016/j.anifeedsci.2017.03.005 [DOI] [Google Scholar]
  44. Zi X. J., Li M., Yu D. G., Tang J., Zhou H. L., Chen Y. Y. (2021). Natural fermentation quality and bacterial community of 12 pennisetum sinese varieties in southern China. Front. Microbiol. 4. 10.3389/fmicb.2021.627820 [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

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

Supplementary Materials

Click here for additional data file. (160.3KB, docx)

Data Availability Statement

The original contributions presented in the study are included in the article/Supplementary Material, further inquiries can be directed to the corresponding author/s.

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

RESOURCES