Effects of artificial forest and grass on soil fungal community at southern Ningxia mountain
ZHANG Shu-meng, HUANG Yi-mei, NI Yin-xia, ZHONG Qi-qi
Key Laboratory of Plant Nutrition and the Agri-environment in Northwest China, Ministry of Agriculture, College of Natural Resources and Environment, Northwest A & F University, Yangling 712100, China
It is of importance to evaluate potential ofsoil fertility and health status after vegetation restoration at southern Ningxia mountain, Chinese Loess Plateau. Therefore, three typical grasslands, including the Stipa bungeana Trin (SB) of natural grassland restoration, the Medicago sativa (MS) of artificial grassland reatoration and Caragana korshinskii Kom (CK) of artificial shrub restoration were selected as experimental sites. Fungi community composition and diversity of surface soil (0~20cm) were analyzed by using Miseq high-throughput sequencing technology. Response of soil fungi communities to environmental factors was assessed through redundancyanalysis (RDA). The identified taxa in various resolutions were:27 phyla, 44 classes, 70 orders and 91 families. The dominant phyla were Ascomycota and Basidiomycota, with relative abundance of 71.8% and15.2%, respectively. The dominant classes were Sordariomycetes, Dothideomycetes, Agaricomycetes and Pezizomycetes. Gibberella, Colpoda, Hydropisphaera, Floricola, Funneliformis and Marcelleina were the dominant genera in this study. Abundance and diversity of soil fungi were highest in MS and lowest in CK. Abundance of Glomeromycota were were highest in SB (4.8%); abundance of Ascomycota were highest in MS (82.6%) lowest in CK (56.8%); abundance of Basidiomycota and Unclassified were highest in MS (25.3% and 7.9%, respectively) and lowest in MS (7.1% and 0.8%, respectively). Abundance of Pezizomycetes were highest in SB (17.8%) and had significant difference correlated to CK. Atthe site of SB, abundance of Agaricomycetes were highest and obviously higher than that of CK. Heatmap shows that although there were similarities of soil fungi communities between MS and SB. SB, MS and CK had the highest abundance of Arbuscular mycorrhizal fungi, soil pathogenic fungi and Colpoda (a kind of protozoan), respectively. In conclusion, compared to the restoration of natural grassland, restoration of artificial grassland and shrub had great influence on the community composition and diversity of soil fungi. RDA showed that soil water, total organic carbon and total nitrogen were the main soil parameters influencing fungal communities.
Barbi F, Prudent E, Vallon L, et al. Tree species select diverse soil fungal communities expressing different sets of lignocellulolytic enzyme-encoding genes[J]. Soil Biology and Biochemistry, 2016,100:149-159.
[2]
Filion M, St-Arnaud M, Fortin J A. Direct interaction between the arbuscular mycorrhizal fungus Glomus intraradices and different rhizosphere microorganisms[J]. New Phytologist, 1999, 141(3):525-533.
[3]
Mukerji K G. Concepts in Mycorrhizal Research[M]. New Delhi:Springer Netherlands, 1996:385.
[4]
Smith K P, Goodman R M. Host variation for interactions with beneficial plant-associated microbes[J]. Annual Review of Phytopathology, 1999,37:473-491.
Huang Y M, Michel K, An S S, et al. Changes in microbial-community structure with depth and time in a chronosequence of restored grassland soils on the Loess Plateau in northwest China[J]. Journal of Plant Nutrition and Soil Science, 2011,174(5):765-774.
Wang Z, Chen Q, Liu L, et al. Responses of soil fungi to 5-year conservation tillage treatments in the drylands of northern China[J]. Applied Soil Ecology, 2016,101:132-140.
Jones D L, Willett V B. Experimental evaluation of methods to quantify dissolved organic nitrogen (DON) and dissolved organic carbon (DOC) in soil[J]. Soil Biology and Biochemistry, 2006, 38(5):991-999.
[23]
Wu J, Joergensen R G, Pommerening B, et al. Measurement of soil microbial biomass C by fumigation-extraction-An automated procedure[J]. Soil Biology and Biochemistry, 1990,22(8):1167-1169.
Lienhard P, Terrat S,Prévost-Bouré N C, et al. Pyrosequencing evidences the impact of cropping on soil bacterial and fungal diversity in Laos tropical grassland[J]. Agronomy for Sustainable Development, 2014,34(2):525-533.
[28]
Degrune F, Dufrêne M, Colinet G, et al. A novel sub-phylum method discriminates better the impact of crop management on soil microbial community[J]. Agronomy for Sustainable Development, 2015,35(3):1157-1166.
[29]
Silva A P D, Babujia L C, Franchini J C, et al. Soil structure and its influence on microbial biomass in different soil and crop management systems[J]. Soil and Tillage Research, 2014,142(1):42-53.
[30]
Desjardins A E. Gibberella from A (venaceae) to Z (eae)[J]. Annual Review of Phytopathology, 2003,41(1):177-198.
[31]
Ann E W M D. Pseudallescheria:An underdiagnosed fungus?[J]. Diagnostic Cytopathology, 2001,25(3):153-157.
[32]
金静.渤海、黄海海域山东沿岸海洋木生真菌的分类研究[D]. 山东:山东农业大学, 2004.
[33]
Li W, Gao W, Zhang M, et al. p-Terphenyl Derivatives from the Endolichenic FungusFloricola striata[J]. Journal of Natural Products. 2016,79(9):2188-2194.
Liu J, Sui Y, Yu Z, et al. Soil carbon content drives the biogeographical distribution of fungal communities in the black soil zone of northeast China[J]. Soil Biology and Biochemistry, 2015,83:29-39.
[44]
Bridge P D, Newsham K K. Soil fungal community composition at Mars Oasis, a southern maritime Antarctic site, assessed by PCR amplification and cloning[J]. Fungal Ecology, 2009,2(2):66-74.
Zhang T, Wang N F, Liu H Y, et al. Soil pH is a Key Determinant of Soil Fungal Community Composition in the Ny-Alesund Region, Svalbard (High Arctic)[J]. Frontiers in Microbiology, 2016,7(244):1-10.