Sanitary landfill improved CNPS microbial functional gene abundance compared to non-sanitary landfill

被引:6
|
作者
Luo, Yuzhen [1 ,2 ,3 ,4 ]
Zhang, Weiwei [1 ,4 ]
Li, Yaying [2 ]
Wang, Yongjie [3 ]
Yao, Huaiying [2 ,5 ]
Han, Jigang [1 ,4 ]
机构
[1] Shanghai Acad Landscape Architecture Sci & Planni, Key Lab Natl Forestry & Grassland Adm Ecol Landsc, Shanghai 200232, Peoples R China
[2] Chinese Acad Sci, NUEORS, Inst Urban Environm, Ningbo 315800, Peoples R China
[3] Shanghai Ocean Univ, Coll Food Sci & Technol, Shanghai 200120, Peoples R China
[4] Shanghai Engn Res Ctr Landscaping Challenging Urb, Shanghai 200232, Peoples R China
[5] Wuhan Inst Technol, Sch Environm Ecol & Biol Engn, Wuhan 430205, Peoples R China
基金
国家重点研发计划;
关键词
HT-Q-PCR; Landfill cover soil; Microbial gene abundance; Nutrient cycling; METHANOTROPHIC COMMUNITIES; COVER SOILS; HEAVY-METALS; DIVERSITY; METHANE; FERTILIZATION; RESTORATION; BACTERIAL; DECOMPOSITION; CONTAMINATION;
D O I
10.1007/s11368-019-02426-z
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Purpose The landfill soil microbes related to nutrient cycling, such as carbon (C), nitrogen (N), phosphorus (P), and sulfur (S) cycling, are changed by continuous waste decomposition. Monitoring the changes that occur in CNPS functional genes in different types of landfill cover soils as a whole is vital to our understanding of microbial function in element cycling. Materials and methods The high-throughput quantitative polymerase chain reaction-based chip (HT-Q-PCR) method was used to explore differences in the abundance of 71 CNPS functional genes in cover soils (0-20 cm, 20-40 cm, and 40-60 cm) from two types of landfills (sanitary and non-sanitary) and to examine the soil pH and the concentrations of C, N, P, S, and 6 heavy metals. Results and discussion The absolute abundances of CNPS functional genes varied greatly, with the highest gene abundance reaching 5.28 x 10(9) copies per gram of soil, and 11% (8/71) of the genes not detected. Among the detected genes, there was a much higher functional gene abundance in the sanitary landfill than in the non-sanitary landfill cover soils, and the difference in gene abundance became more significant with increasing sampling depth. In addition to landfill type and sampling depth, the soil pH, soil dissolved organic carbon (DOC), available N (AN), and available S (AS) correlated significantly to functional gene abundance. Conversely, soil heavy metals, such as Cu, Cd, Cr, Zn, and Ni, had no effects on functional gene abundance, which might be due to their low contents. Conclusions Our results suggest that sanitary landfill increases soil CNPS gene abundance compared to that of non-sanitary landfill. The findings provide suggestions for landfill treatment and ecological protection, especially regarding vegetation restoration.
引用
收藏
页码:99 / 108
页数:10
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