State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, China.
University of Chinese Academy of Sciences, Beijing, China.
Appl Environ Microbiol. 2018 Aug 31;84(18). doi: 10.1128/AEM.01031-18. Print 2018 Sep 15.
Long-term effects of inorganic and organic fertilization on nitrification activity (NA) and the abundances and community structures of ammonia-oxidizing bacteria (AOB) and ammonia-oxidizing archaea (AOA) were investigated in an acidic Ultisol. Seven treatments applied annually for 27 years comprised no fertilization (control), inorganic NPK fertilizer (N), inorganic NPK fertilizer plus lime (CaCO) (NL), inorganic NPK fertilizer plus peanut straw (NPS), inorganic NPK fertilizer plus rice straw (NRS), inorganic NPK fertilizer plus radish (NR), and inorganic NPK fertilizer plus pig manure (NPM). In nonfertilized soil, the abundance of AOA was 1 order of magnitude higher than that of AOB. Fertilization reduced the abundance of AOA but increased that of AOB, especially in the NL treatment. The AOA communities in the control and the N treatments were dominated by the and B1 clades but shifted to clade A in the NL and NPM treatments. cluster 8a was found to be the most dominant AOB in all treatments. NA was primarily regulated by soil properties, especially soil pH, and the interaction with AOB abundance explained up to 73% of the variance in NA. When NL soils with neutral pH were excluded from the analysis, AOB abundance, especially the relative abundance of cluster 8a, was positively associated with NA. In contrast, there was no association between AOA abundance and NA. Overall, our data suggest that cluster 8a of AOB played an important role in the nitrification process in acidic soil following long-term inorganic and organic fertilization. The nitrification process is an important step in the nitrogen (N) cycle, affecting N availability and N losses to the wider environment. Ammonia oxidation, which is the first and rate-limiting step of nitrification, was widely accepted to be mainly regulated by AOA in acidic soils. However, in this study, nitrification activity was correlated with the abundance of AOB rather than that of AOA in acidic Ultisols. cluster 8a, a phylotype of AOB which preferred warm temperatures, and low soil pH played a predominant role in the nitrification process in the test Ultisols. Our results also showed that long-term application of lime or pig manure rather than plant residues altered the community structure of AOA and AOB. Taken together, our findings contribute new knowledge to the understanding of the nitrification process and ammonia oxidizers in subtropical acidic Ultisol under long-term inorganic and organic fertilization.
长期施用无机和有机肥料对酸性土壤中硝化活性(NA)以及氨氧化细菌(AOB)和氨氧化古菌(AOA)的丰度和群落结构的影响进行了研究。27 年来,每年进行 7 次处理,包括不施肥(对照)、无机 NPK 肥料(N)、无机 NPK 肥料加石灰(CaCO)(NL)、无机 NPK 肥料加花生秸秆(NPS)、无机 NPK 肥料加稻草(NRS)、无机 NPK 肥料加萝卜(NR)和无机 NPK 肥料加猪粪(NPM)。在未施肥的土壤中,AOA 的丰度比 AOB 高 1 个数量级。施肥降低了 AOA 的丰度,但增加了 AOB 的丰度,特别是在 NL 处理中。对照和 N 处理中的 AOA 群落主要由 和 B1 类群主导,但在 NL 和 NPM 处理中转变为 A 类群。在所有处理中,8a 聚类被发现是最主要的 AOB。NA 主要受土壤性质调控,特别是土壤 pH,与 AOB 丰度的相互作用解释了 NA 变异的 73%。当排除中性 pH 的 NL 土壤进行分析时,AOB 丰度,特别是 8a 聚类的相对丰度,与 NA 呈正相关。相比之下,AOA 丰度与 NA 之间没有关联。总的来说,我们的数据表明,在长期施用无机和有机肥料后,酸性土壤中的 AOB 8a 聚类在硝化过程中发挥了重要作用。硝化作用是氮(N)循环中的一个重要步骤,影响 N 的可用性和 N 向更广泛环境的损失。氨氧化,即硝化作用的第一步和限速步骤,被广泛认为是酸性土壤中氨氧化的主要调控因子。然而,在这项研究中,硝化活性与 AOB 的丰度而不是 AOA 的丰度相关,在酸性 Ultisols 中。8a 聚类,一种偏好温暖温度和低土壤 pH 的 AOB 型,在测试 Ultisols 的硝化过程中发挥了主要作用。我们的结果还表明,长期施用石灰或猪粪而不是植物残体改变了 AOA 和 AOB 的群落结构。总的来说,我们的研究结果为理解亚热带酸性 Ultisol 在长期无机和有机施肥下的硝化过程和氨氧化提供了新的知识。