Soil aggregate size mediates the variations in the abundance and function of ammonia oxidizers in heavy metal-contaminated soil under different nitrogen fertilization regimes

被引:2
作者
Huang, Xian [1 ,2 ,4 ]
Tang, Shuting [1 ,3 ]
Zeng, Meng [2 ,4 ]
Qin, Zhongkai [2 ,4 ]
Liang, Jialiang [2 ,4 ]
Chen, Yuyuan [2 ,4 ]
Wu, Yamei [2 ,4 ]
Chen, Shuairen [2 ,4 ]
Yu, Fangming [1 ,2 ,4 ]
Li, Yi [1 ,2 ,4 ]
机构
[1] Guangxi Normal Univ, Key Lab Ecol Rare & Endangered Species & Environm, Minist Educ, Guilin, Peoples R China
[2] Guangxi Normal Univ, Coll Environm & Resources, 15th YuCai St, Guilin 541004, Peoples R China
[3] Sun Yat Sen Univ, Sch Environm Sci & Engn, Guangzhou 510006, Peoples R China
[4] Guangxi Normal Univ, Guangxi Key Lab Environm Proc & Remediat Ecol Frag, Guilin 541004, Peoples R China
基金
中国国家自然科学基金;
关键词
Ammonia-oxidizing archaea; Ammonia-oxidizing bacteria; amoA gene abundance; Nitrification potential; Potential ammonia oxidation; LONG-TERM FERTILIZATION; COMMUNITY STRUCTURE; PHOSPHORUS FERTILIZATION; CARBON SEQUESTRATION; OXIDE EMISSIONS; NITRIFICATION; BACTERIA; ARCHAEA; POPULATIONS; FRACTIONS;
D O I
10.1016/j.apsoil.2024.105448
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Mining has led to dramatic ecosystem degradation, the destruction of vegetation and irreversible damage to soil structure and nutrient cycling; additionally, heavy metal (HM) contamination has affected soil nitrogen (N) cycle-associated microorganisms and disrupted soil aggregate structure. To explore the mechanism of soil N recovery in mining areas, we investigated the effects of two N fertilizers (urea (U) and ammonium chloride (AC)) and nine different fertilization patterns on the nitrification process and ammonia oxidizers in soil aggregates via incubation experiments. The results showed that different N treatments had different influences on the distribution of AOA and AOB amoA gene abundance and microbial community structure in soil aggregates. The AOB amoA gene abundance was significantly greater than the AOA amoA gene abundance in aggregates. The dominant species of AOA and AOB were Nitrososphaera and Nitrosospira , respectively, which were mainly found in microaggregates and accounted for 10.3 % to 25.0 % and 31.5 % to 60.1 %, respectively, of the microaggregates. Dissolved organic nitrogen (DON) can be used as an important variable to explain variations in AOA communities, and microbial nitrogen (MBN) content, tartaric acid content, cellulase activity and AOB amoA gene abundance can be used as important variables to explain variations in AOB communities. N fertilizer addition resulted in potential ammonia oxidation (PAO) values ranging from 0.079 to 0.236, 0.100 to 0.5953 and 0.146 to 0.905 mu g.NO2--N d(-1) g(-1) in mega-, macro- and microaggregates, respectively, which suggested that PAO values increased with decreasing aggregate size. In addition, the total nitrification potential (TNP) in macroaggregates was greater than that in mega- and microaggregates, which was the main reason for the increase in the NO3 content in macroaggregates. AOB amoA gene abundance was significantly positively correlated with TNP, and AOB amoA gene abundance was more significantly positively correlated with PAO values than was AOA gene abundance, which suggests that AOB dominated ammonia oxidation and nitrification processes in aggregates. Our research contributes to an understanding of the mechanisms underlying the effects of different types of N fertilizers on nitrification processes and ammonia oxidizers in soil aggregates and provides insights into N management in contaminated soils in mining areas.
引用
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页数:13
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