Elsevier

Applied Soil Ecology

Volume 153, September 2020, 103573
Applied Soil Ecology

Medicago sativa and soil microbiome responses to Trichoderma as a biofertilizer in alkaline-saline soils

https://doi.org/10.1016/j.apsoil.2020.103573Get rights and content

Abstract

The use of Trichoderma biofertilizer (BOF) has been proposed to observably elevate plant growth and crop productivity. In addition, mowing can greatly accelerate plant shoot regrowth to increase aboveground biomass and nutrient contents. We aimed to measure the effects of Trichoderma BOF on Medicago sativa growth in saline-alkali soils, especially the effects on the underlying microbial ecological mechanisms, under non-mowed and mowed conditions. We thus carried out a pot experiment to investigate the growth of M. sativa under different fertilization regimes and utilization conditions, and the corresponding responses of soil physicochemical variables and the soil microbiome were also explored. Fertilization, mowing and their interaction had significant (P = 0.000) effects on M. sativa shoot dry weight, while only fertilization had a significant (P = 0.000) effect on M. sativa root dry weight. Compared with nonamended fertilizer (CK) and organic fertilizer (OF) treatments, Trichoderma BOF treatment significantly (P < 0.05) increased the biomass of M. sativa. High bacterial HShannon and SChao1 values in mowed system and high fungal HShannon and SChao1 values in the non-mowed system were significantly (P < 0.05) correlated with a high M. sativa biomass. Mantel test results showed that soil microbial community composition was significantly (P = 0.001) correlated with M. sativa biomass in both the mowed and non-mowed systems. In addition, variance partitioning analysis (VPA) revealed that soil properties were the main factor explaining the variation of soil microbial community composition, accounting for 14.1% for bacteria and 16.5% for fungi. In conclusion, Trichoderma BOF can effectively alter soil properties and the soil microbial diversity and community, resulting in increased M. sativa biomass in alkaline-saline soils in both mowed and non-mowed systems.

Introduction

Soil salinization, which leads mainly to soil compaction and soil nutrient decline, an important abiotic stress that severely affects the development of agriculture and can even destroy ecological environment. Saline-alkali soils, which are characterized by relatively high pH values and salt concentrations and relatively low levels of soil organic matter and nutrient contents, is unable to support the healthy growth of crops (Pascale et al., 2005). The low productivity of saline-alkali soils is attributed primarily to poor microbial activity (Shao et al., 2018). Recently, the cultivation of saline-tolerant forage species adapted to saline-alkali soils has gained increased amounts of attention. Medicago sativa, an excellent perennial leguminous forage grass species, is widely cultivated and has a positive effect on the development of animal husbandry (Hermann et al., 2002). Accumulating evidence (Y.C. Wang et al., 2007; Postnikova et al., 2013; Liu et al., 2018) has shown that M. sativa can tolerate a certain degree of saline-alkali stress. Li et al. (2010) reported that M. sativa is extremely sensitive to saline-alkali stress, especially during the germination and early-seedling phases.

Trichoderma spp., which are well-known plant growth promoters, can significantly accelerate plant growth through a series of mechanisms (Altomare et al., 1999; Naseby et al., 2000; Banani et al., 2013). Many studies have shown that inoculation with Trichoderma significantly promotes the growth of various plant species (Kucuk et al., 2008; Zhang et al., 2018; Singh et al., 2019). The combination of Trichoderma strains and organic fertilizers (OFs) to produce biofertilizers (BOFs) is effective for obtaining high crop yields, and the promotion effect of BOFs is better than that of either OF or Trichoderma strains alone (Zhang et al., 2013a, Zhang et al., 2013b). The application of BOF (including functional microbes) can restore healthy and active soil microflora within a relatively short period, effectively improving soil properties and increasing soil fertility, thus playing a positive role in plant growth. A good soil microflora is an effective guarantee for promoting plant growth (Philippot et al., 2013). Although Trichoderma BOF has a positive role in normal agricultural soils, the facilitation effect of Trichoderma BOF in saline-alkali soils has rarely been reported.

Mowing is one of the most common cultivation practices of forage grass and is primarily employed in M. sativa production (Barać et al., 2012). M. sativa rapidly recovers after mowing, which supports the maintenance of stable yields. Mowing can elevate total plant biomass mainly because it is beneficial to promote plants to generate new leaves (Robson et al., 2007; Zhang et al., 2019). However, the report of Todd et al. (1992) demonstrated that plant shoot removal by mowing can be accompanied by reduced root biomass and related N contents. The suitable stage for M. sativa mowing is the first-flower stage, which guarantees the best nutrient contents and yields (Radović et al., 2009). However, the promotion effects of different fertilization regimes under non-mowed and mowed conditions, especially the effects of the underlying microbial mechanisms, have rarely been studied.

The M. sativa cultivar ‘Zhong-Mu No. 1,’ which is somewhat resistant to saline-alkaline stress, was used in this study. We applied different fertilizers (CK, nonamended fertilizer; OF, organic fertilizer; and BOF, Trichoderma biofertilizer) under non-mowed and mowed conditions to address the following questions: (i) Does BOF significantly increase M. sativa growth more than CK and OF does in both mowed and non-mowed systems? (ii) How do the different treatments impact the soil properties and the soil microbial diversity and community? (iii) Do correlations exist between soil properties, the soil microbial diversity and community, and M. sativa biomass? And (iv) Among these factors (fertilization regime, non-mowed/mowed conditions, and soil properties), which mainly affects the soil microbial community?

Section snippets

Trichoderma strain, seeds, soil and fertilizers used in the greenhouse experiments

The strain NAU-T14 used throughout this study was isolated from soil at the Dongying Comprehensive Experimental Station (37°18′26″ E, 118°38′15″ N), Dongying city, Shandong Province, China; the strain was identified as Trichoderma harzianum (Fig. S1a, b, CCTCC M 2018520, China Center for Type Culture Collection). T. harzianum NAU-14 is usually cultivated on potato dextrose agar (PDA) plates and incubated at 28 °C.

M. sativa seeds (Zhong-Mu No. 1, Zhang et al., 2019) were employed in our

Coupling of soil properties and M. sativa growth

Fertilization, mowing and their interaction had significant (P < 0.001) effects on M. sativa shoot dry weight (Fig. 1a), but only fertilization had a significant (P < 0.001) effect on M. sativa root dry weight (Fig. 1b). Compared with those in the CK treatment, the shoot dry weight and root dry weight in the non-mowed treatment significantly elevated by 34.4% (P = 0.003) and 71.7% (P = 0.004), respectively, when M. sativa was treated with OF but increased by 64.8% (P < 0.001) and 117.4% (P

Discussion

The M. sativa biomass (both shoot dry weight and root dry weight) varied significantly under the different fertilization regimes (CK, OF, and BOF), which was primarily due to the altered soil nutrient contents and the effective activity of the microbial inoculants. The OF and BOF treatments, which have substantial soil organic matter and nutrient contents, improved soil properties and soil fertility better than the other treatments did according to the initial analysis (Jamil et al., 2004). The

Conclusions

Trichoderma BOF and mowing effectively altered soil properties, soil bacterial and fungal diversities, and soil bacterial and fungal communities, which ultimately increased M. sativa biomass in alkaline-saline soils. Soil bacterial HShannon and SChao1 values in the mowed system and fungal HShannon and SChao1 values in the non-mowed system were significantly correlated with M. sativa biomass. Soil properties had a significant influence on soil microbial community composition, which was also

Declaration of competing interest

The authors declare no conflicts of interest of this work.

Acknowledgments

This study was supported by the Earmarked Fund for China Agriculture Research System (CARS-34) and the China Scholarship Council (CSC No. 201906855001). We are very grateful to Y.Q. Huo for her assistance in the greenhouse and to Dr. Z.Z. Shen and Z.B. Zhou for their contribution to our revised work.

References (59)

  • J. Zhao et al.

    Effects of organic-inorganic compound fertilizer with reduced chemical fertilizer application on crop yields, soil biological activity and bacterial community structure in a rice-wheat cropping system

    Appl. Soil Ecol.

    (2016)
  • V. Acosta-Martínez et al.

    Soil microbial communities and function in alternative systems to continuous cotton

    Soil Sci. Soc. Am. J.

    (2010)
  • J. Ahn et al.

    Human gut microbiome and risk for colorectal cancer

    J. Natl. Cancer Inst.

    (2013)
  • S.D. Allison et al.

    Resistance, resilience, and redundancy in microbial communities

    Proc. Natl. Acad. Sci. U. S. A.

    (2008)
  • C. Altomare et al.

    Solubilization of phosphates and micronutrients by the plant-growth-promoting and biocontrol fungus Trichoderma harzianum Rifai 1295-22

    Appl. Environ. Microbiol.

    (1999)
  • H. Banani et al.

    Characterization of resistance mechanisms activated by Trichoderma harzianum T39 and benzothiadiazole to downy mildew in different grapevine cultivars

    Plant Pathol.

    (2013)
  • S.R. Barać et al.

    Testing results of mower with different cutting devices in alfalfa mowing

    Res. J. Agr. Sci.

    (2012)
  • N.C. Brady et al.

    The Nature and Properties of Soils

    (1996)
  • J.G. Caporaso et al.

    QIIME allows analysis of high-throughput community sequencing data

    Nat. Methods

    (2010)
  • J.G. Caporaso et al.

    Global patterns of 16S rRNA diversity at a depth of millions of sequences per sample

    Proc. Natl. Acad. Sci. U. S. A.

    (2011)
  • G. Chaer et al.

    Comparative resistance and resilience of soil microbial communities and enzyme activities in adjacent native forest and agricultural soils

    Microb. Ecol.

    (2009)
  • J.M. Chaparro et al.

    Manipulating the soil microbiome to increase soil health and plant fertility

    Biol. Fertil. Soils

    (2012)
  • H. Chu et al.

    Soil bacterial diversity in the Arctic is not fundamentally different from that found in other biomes

    Environ. Microbiol.

    (2010)
  • P.A. Dimitriu et al.

    Relationship between soil properties and patterns of bacterial b-diversity across reclaimed and natural boreal forest soils

    Microb. Ecol.

    (2010)
  • R.C. Edgar

    UPARSE: highly accurate OTU sequences from microbial amplicon reads

    Nat. Methods

    (2013)
  • M. Hartmann et al.

    Distinct soil microbial diversity under long-term organic and conventional farming

    ISME J.

    (2014)
  • M.L. Hermann et al.

    Evaluation of hay-type and grazing-tolerant alfalfa cultivars in season-long or complementary rotational stocking systems for beef cows

    J. Anim. Sci.

    (2002)
  • J.T. Hollibaugh

    Environmental factors shaping microbial community structure in salt marsh sediments

    Mar. Ecol. Prog. Ser.

    (2010)
  • M. Jamil et al.

    Impact of organic wastes (Bagasse Ash) on the yield of wheat (Triticum aestivum L.) in a calcareous soil

    Int. J. Agric. Biol.

    (2004)
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