4.7 Article

Investigation on the microbial community of an accelerating stabilization landfill by aeration engineering

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Publisher

SPRINGER HEIDELBERG
DOI: 10.1007/s11356-023-29039-x

Keywords

Solid waste; Landfill; Stabilization; Microbial community; Aeration; Bioreactor landfill

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The microbial community of an aerobic landfill undergoing aeration engineering was studied. Municipal solid waste samples were taken from two aeration well sites with different landfill temperatures and stabilization levels. Analysis of the physical, chemical, and microbial properties of the waste revealed differences in bacterial distribution, influenced by ammonia-nitrogen and moisture content. Aeration engineering enhanced the abundance of methane oxidation, sulfide oxidation, and aerobic chemoheterotrophy, accelerating the landfill stabilization process.
The microbial community of the landfill undergoing aerobic stabilization process by aeration engineering was investigated. The municipal solid wastes (MSWs) were sampled from two aeration well sites with different landfill temperatures (65.5 & DEG;C and 41.7 & DEG;C) under higher and lower stabilization level. The physical component, chemical property, and microbial population of MSWs were analyzed and compared. The result showed that the phylum Firmicutes was dominant in the aerobic landfill; and the genus Weissella and Syntrophaceticus were more abundant in high, and low temperature site, respectively. The bacterial distribution showed difference on two temperature sites and four landfill depths, mainly affected by the ammonia-nitrogen and moisture content of MSWs. The ecological profiles of the microorganisms responded the aeration engineering were predicted. The anaerobic hydrolytic and acetogenic microorganisms were decreased in abundance, while the facultative Lactobacillus increased when the landfill under a higher stabilization level. The function abundances of methane oxidation, sulfide oxidation, and aerobic chemoheterotrophy were enriched by aeration engineering, which was the microbial mechanism for accelerating the stabilization process of landfill.

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