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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2021, Vol. 15 Issue (4) : 77    https://doi.org/10.1007/s11783-020-1370-6
RESEARCH ARTICLE
Fungal diversity and its mechanism of community shaping in the milieu of sanitary landfill
Rong Ye1, Sai Xu2, Qian Wang1, Xindi Fu1, Huixiang Dai1, Wenjing Lu1()
1. School of Environment, Tsinghua University, Beijing 100084, China
2. Jiangsu Key Laboratory of Chemical Pollution Control and Resources Reuse, School of Environmental and Biological Engineering, Nanjing University of Science and Technology, Nanjing 210094, China
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Abstract

Ascomycota was the predominant phylum in sanitary landfill fungal communities.

• Saprophytic fungi may be of special importance in landfill ecology.

• Both richness and diversity of fungal community were lower in leachate than refuse.

• Physical habitat partly contributed to the geographic variance of fungal community.

• NO3 was considered the most significant abiotic factor shaping fungal community.

Land filling is the main method to dispose municipal solid waste in China. During the decomposition of organic waste in landfills, fungi play an important role in organic carbon degradation and nitrogen cycling. However, fungal composition and potential functions in landfill have not yet been characterized. In this study, refuse and leachate samples with different areas and depths were taken from a large sanitary landfill in Beijing to identify fungal communities in landfills. In high-throughput sequencing of ITS region, 474 operational taxonomic units (OTUs) were obtained from landfill samples with a cutoff level of 3% and a sequencing depth of 19962. The results indicates that Ascomycota, with the average relative abundance of 84.9%, was the predominant phylum in landfill fungal communities. At the genus level, Family Hypocreaceae unclassified (15.7%), Fusarium (9.9%) and Aspergillus (8.3%) were the most abundant fungi found in the landfill and most of them are of saprotrophic lifestyle, which plays a big role in nutrient cycling in ecosystem. Fungi existed both in landfilled refuse and leachate while both the richness and evenness of fungal communities were higher in the former. In addition, fungal communities in landfilled refuse presented geographic variances, which could be partly attributed to physical habitat properties (pH, dissolved organic carbon, volatile solid, NH4+, NO2 and NO3), while NO3 was considered the most significant factor (p<0.05) in shaping fungal community.

Keywords Sanitary landfill      Fungal community      Diversity      Saprotroph      Physical habitat      Environmental factor     
Corresponding Author(s): Wenjing Lu   
Issue Date: 25 November 2020
 Cite this article:   
Rong Ye,Sai Xu,Qian Wang, et al. Fungal diversity and its mechanism of community shaping in the milieu of sanitary landfill[J]. Front. Environ. Sci. Eng., 2021, 15(4): 77.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-020-1370-6
https://academic.hep.com.cn/fese/EN/Y2021/V15/I4/77
Sample name Sample site Depth (m) Filling age (year)
A03(L)* A 3 4
A06(L) A 6 6
A09(L) A 9 8
A12(L) A 12 10
A15(L) A 15 12
B03* B 3 1
B06 B 6 2
B09 B 9 3
B12 B 12 4
B15 B 15 5
C03(L) C 3 2
C06(L) C 6 3
C09(L) C 9 4
C12(L) C 12 5
C15(L) C 15 6
Tab.1  Sampling scheme
Fig.1  pH variation (a) and dissolved organic carbon (DOC) concentrations (b) of refuse samples (A, B, C) and leachate samples (AL, CL) from different depth of a landfill. Small letters above bars indicate significant difference among parameter values of different refuse samples and capital letters indicate significant difference among different leachate samples.
Fig.2  The concentrations of ammonia (a), nitrite (b) and nitrate (c) in refuse samples (A, B, C) and leachate samples (AL, CL) from different depth of the landfill. Small letters above bars indicate significant difference among parameter values of different refuse samples and capital letters indicate significant difference among different leachate samples.
Fig.3  Species accumulation curve (a) and the alpha diversity-Chao index (b) and Shannon index (c) -of fungal communities in landfill.
Fig.4  Relative abundance of top 20 genera (average relative abundance>1%) of fungal communities in refuse samples (a) and leachate samples (b).
Fig.5  The relative abundance of different tropic modes (Pathotroph, Saproroph and Symbiotroph) of fungi among landfill communities; the data was obtained from the probable and high probable classification via FUNGuild. Sa/Pa denotes the ratio of saprotroph to pathotroph.
Fig.6  (a) Nonmetric multidimensional scaling (NMDS) analysis of fungal communities in landfill samples based on “Bray–Curtis” distance. Dashed circle means confidence level of 0.68, representing 68% of fungal community. (b) Redundancy analysis (RDA) of relationships between fungal communities and environmental factors (pH, VS, DOC, ammonia, nitrite, and nitrate) in landfill refuse samples.
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