韩建, 张玉铭, 何红波, 李俊娣, 胡春胜, 李晓欣, 董文旭, 刘秀萍, 张丽娟. 长期不同施氮量下微生物残体氮对土壤氮库稳定性和玉米氮素吸收的影响[J]. 中国生态农业学报 (中英文), 2024, 32(5): 1−14. DOI: 10.12357/cjea.20240116
引用本文: 韩建, 张玉铭, 何红波, 李俊娣, 胡春胜, 李晓欣, 董文旭, 刘秀萍, 张丽娟. 长期不同施氮量下微生物残体氮对土壤氮库稳定性和玉米氮素吸收的影响[J]. 中国生态农业学报 (中英文), 2024, 32(5): 1−14. DOI: 10.12357/cjea.20240116
HAN J, ZHANG Y M, HE H B, LI J D, HU C S, LI X X, DONG W X, LIU X P, ZHANG L J. Impact of microbial residue nitrogen on soil nitrogen pool stability and maize nitrogen uptake under long-term varying nitrogen applications[J]. Chinese Journal of Eco-Agriculture, 2024, 32(5): 1−14. DOI: 10.12357/cjea.20240116
Citation: HAN J, ZHANG Y M, HE H B, LI J D, HU C S, LI X X, DONG W X, LIU X P, ZHANG L J. Impact of microbial residue nitrogen on soil nitrogen pool stability and maize nitrogen uptake under long-term varying nitrogen applications[J]. Chinese Journal of Eco-Agriculture, 2024, 32(5): 1−14. DOI: 10.12357/cjea.20240116

长期不同施氮量下微生物残体氮对土壤氮库稳定性和玉米氮素吸收的影响

Impact of microbial residue nitrogen on soil nitrogen pool stability and maize nitrogen uptake under long-term varying nitrogen applications

  • 摘要: 在农田生态系统中, 化肥氮的施用是保障粮食高产稳产并维持土壤氮库稳定的重要管理措施, 土壤微生物既是土壤氮素矿化的驱动者, 也是土壤氮素固持的贡献者, 在氮素保蓄和供应方面发挥着积极作用, 直接影响作物的氮素吸收利用。本研究依托中国科学院栾城农业生态系统试验站小麦-玉米轮作农田14年长期不同施氮水平定位试验, 选取玉米季施氮量150 kg(N)∙hm−2 (N150)、200 kg(N)∙hm−2 (N200)和300 kg(N)∙hm−2 (N300) 3个典型处理, 通过微区施用15N标记氮肥, 在收获期测定玉米产量、地上部总吸氮量和肥料氮吸收量, 分析0~20 cm土层土壤全氮(TN)、微生物残体氮MRN, 包括真菌残体氮(FRN)和细菌残体氮(BRN)、固定态铵(FN)、矿质氮(NH4+-N+NO3-N, MN)和其他有机氮(ON)含量及不同氮库对15N的截获, 并通过多元回归分析和路径分析建立各形态氮库与玉米氮素吸收的相关关系, 研究土壤“老氮”和肥料“新氮”在土壤氮库中的分配及其对作物吸收利用的影响, 为研究区氮肥高效利用和地力培肥提供理论支撑。结果表明, 玉米产量和氮素吸收以及土壤TN含量均以N200最高, 此施氮量有利于作物高产和土壤氮库培育。N300的肥料氮吸收和残留量高于N200, 表明N300的土壤氮“激发效应”强于N200, 会诱导土壤“老氮”的更多矿化和损失, 其土壤TN库稳定性差、更新程度较大。总氮库中, MRN占主导, N200显著高于其他处理, 对TN的贡献均在50%以上, 且FRN主导了MRN的累积。N200的土壤FRN∶BRN比值显著高于N150和N300, 表明适宜施氮可显著提升真菌在氮素积累中的贡献, 提升土壤氮库的稳定性; 施氮不足(N150)或过量施氮(N300)提升了细菌在氮素积累中的贡献, 不利于稳定土壤氮库。N300的MN和FN含量显著高于其他处理, 表明过量施肥更多提升的是活性氮库。由此可见, 适宜施氮可优化土壤氮库分配, 促进更多的氮进入微生物残体氮库, 显著提高土壤微生物途径对氮的固持作用, 促进土壤对氮素的保蓄与供应良性运行, 保障了玉米氮素吸收与产量形成, 为指导华北平原农田地力培肥与氮肥减施提供了科学依据。了科学依据。

     

    Abstract: In agricultural ecosystems, the application of chemical fertilizer nitrogen is an important management measure to ensure high and stable grain yield and maintain soil nitrogen stability. Soil microorganisms are both drivers of soil nitrogen mineralization and contributors to soil nitrogen retention, playing an active role in nitrogen storage and supply, directly affecting crop nitrogen absorption and utilization. This study is based on the 14-year long-term different nitrogen application level positioning experiment of wheat-corn rotation farmland in Luancheng Agricultural Ecosystem Experimental Station, Chinese Academy of Sciences. It selected three typical treatments of corn season nitrogen application amounts of 150 kg(N)∙hm−2 (N150), 200 kg(N)∙hm−2 (N200) and 300 kg(N)∙hm−2 (N300). By applying 15N labeled nitrogen fertilizer in micro-regions, the corn yield, total nitrogen absorption of the above-ground part, and fertilizer nitrogen absorption were measured at harvest, and the contents of total nitrogen (TN), microbial residue nitrogen MRN, including fungal residue nitrogen (FRN) and bacterial residue nitrogen (BRN), fixed ammonium (FN), mineral nitrogen (NH4+-N+NO3-N, MN) and other organic nitrogen (ON) in the 0~20 cm soil layer and the interception of 15N by different nitrogen pools were analyzed. Through multiple regression analysis and path analysis, the correlation between various forms of nitrogen pools and corn nitrogen absorption was established. The distribution of soil "old nitrogen" and fertilizer "new nitrogen" in soil nitrogen pools and their effects on crop absorption and utilization were studied, providing theoretical support for the efficient use of nitrogen fertilizer and soil fertility cultivation in the study area. The results showed that corn yield, nitrogen absorption and soil TN content were all highest at N200, which is conducive to high crop yield and soil nitrogen pool cultivation. The absorption and residual amount of fertilizer nitrogen at N300 were higher than those at N200, indicating that the soil nitrogen "stimulation effect" at N300 was stronger than that at N200, which would induce more mineralization and loss of soil "old nitrogen", and its soil TN pool stability was poor and the renewal degree was larger. Among the total nitrogen pools, MRN was dominant, N200 was significantly higher than other treatments, contributing more than 50% to TN, and FRN dominated the accumulation of MRN. The soil FRN:BRN ratio of N200 was significantly higher than that of N150 and N300, indicating that appropriate nitrogen application can significantly increase the contribution of fungi to nitrogen accumulation and improve the stability of soil nitrogen pool; insufficient nitrogen application (N150) or excessive nitrogen application (N300) increased the contribution of bacteria to nitrogen accumulation, which is not conducive to the stability of soil nitrogen pool. The MN and FN content of N300 was significantly higher than other treatments, indicating that excessive fertilization mainly increases the active nitrogen pool. Therefore, appropriate nitrogen application can optimize the distribution of soil nitrogen pool, promote more nitrogen into the microbial residue nitrogen pool, significantly improve the nitrogen retention function of soil microbial pathway, promote the benign operation of soil nitrogen storage and supply, ensure the formation of corn nitrogen absorption and yield, and provide scientific basis for guiding soil fertility cultivation and nitrogen fertilizer reduction in the North China Plain.ain.

     

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