Effect of nitrogen fertilization on the abundance of nitrogen cycling genes in agricultural soils: A meta-analysis of field studies

氧化亚氮还原酶 反硝化 氮气循环 硝化作用 氨单加氧酶 亚硝酸盐还原酶 氮气 农学 自行车 固氮酶 人口 固氮 硝酸还原酶 生态学 生物 肥料 硝酸盐 化学 细菌 遗传学 有机化学 考古 人口学 社会学 历史
作者
Yang Ouyang,Sarah E. Evans,Maren Friesen,Lisa K. Tiemann
出处
期刊:Soil Biology & Biochemistry [Elsevier]
卷期号:127: 71-78 被引量:254
标识
DOI:10.1016/j.soilbio.2018.08.024
摘要

Quantification of functional genes involved in nitrogen (N) transformation improves our understanding of N-cycling microbial population responses to environmental disturbance. Agricultural N fertilization affects N-cycling gene abundances in soil, but the general patterns and variability of N cycling gene abundances in response to N fertilization have yet to be synthesized. We conducted a meta-analysis comprising 47 field studies in agricultural ecosystems. We included five marker genes important to N-cycling: nifH (encoding nitrogenase; key enzyme for N fixation), amoA (encoding ammonia monooxygenase; key enzyme for nitrification), nirK and nirS (encoding nitrite reductase; key enzyme for denitrification), and nosZ (encoding nitrous oxide reductase; key enzyme for denitrification). We found that N fertilization had no effect on the abundance of nifH, but significantly increased archaeal amoA (31%), bacterial amoA (313%), nirK (53%), nirS (40%) and nosZ (75%), respectively. N fertilizer form (inorganic versus organic) strongly affected the response of most selected N-cycling genes to N fertilization; organic fertilizers often had a much stronger effect than inorganic fertilizers. N fertilization duration, crop rotation, and soil pH were also important factors regulating the response of most N-cycling genes to N fertilization. Genes involved in nitrification and denitrification were significantly correlated with each other. Improvement in understanding of the response of N-cycling gene abundance to enhanced N input will help develop quantitative models of N availability and N fluxes and improve strategies for reducing reactive N gas emissions and N management in agricultural ecosystems.
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