肖未, 吴庆峰, 李伏生. 滴灌水氮管理对玉米种植土壤无机氮含量和氧化亚氮排放的影响[J]. 华南农业大学学报, 2023, 44(3): 410-419. doi: 10.7671/j.issn.1001-411X.202204004
    引用本文: 肖未, 吴庆峰, 李伏生. 滴灌水氮管理对玉米种植土壤无机氮含量和氧化亚氮排放的影响[J]. 华南农业大学学报, 2023, 44(3): 410-419. doi: 10.7671/j.issn.1001-411X.202204004
    XIAO Wei, WU Qingfeng, LI Fusheng. Effect of drip irrigation and nitrogen management on inorganic nitrogen content and nitrous oxide emission in maize-planting soil[J]. Journal of South China Agricultural University, 2023, 44(3): 410-419. doi: 10.7671/j.issn.1001-411X.202204004
    Citation: XIAO Wei, WU Qingfeng, LI Fusheng. Effect of drip irrigation and nitrogen management on inorganic nitrogen content and nitrous oxide emission in maize-planting soil[J]. Journal of South China Agricultural University, 2023, 44(3): 410-419. doi: 10.7671/j.issn.1001-411X.202204004

    滴灌水氮管理对玉米种植土壤无机氮含量和氧化亚氮排放的影响

    Effect of drip irrigation and nitrogen management on inorganic nitrogen content and nitrous oxide emission in maize-planting soil

    • 摘要:
      目的  获得玉米种植土壤氧化亚氮(N2O)减排的滴灌施肥模式,揭示不同滴灌灌水量和施氮比例下土壤无机氮含量对土壤N2O排放的影响。
      方法  在移动防雨棚内开展2季玉米3种滴灌灌水量(W60、W80和W100分别为田间持水量的50%~60%、70%~80%和90%~100%)和2种滴灌施氮比例(等N量为180 kg · hm−2,其中,F55为50%氮肥作基肥土施、50%氮肥作滴灌施肥,F37为30%氮肥作基肥土施、70%氮肥作滴灌施肥)的田间试验,测定生育期内土壤N2O通量和不同生育时期土壤无机氮含量,计算不同生育时期和全生育期土壤N2O排放量,分析土壤N2O通量与土壤无机氮含量之间的关系。
      结果  2季玉米土壤的N2O排放规律相似;相同施氮比例下,W100水分处理下土壤N2O排放通量在多数玉米生育时期高于W60和W80,表明高水分处理下土壤N2O排放通量高于中、低水分处理;相同水分处理下,除夏季玉米苗期外,土壤N2O排放通量施氮比例F55比F37更低。从整个生育时期土壤N2O累积排放量来看,春季玉米种植土壤W60F55处理N2O累积排放量低于其他处理,W80F55次之,夏季玉米种植土壤则是W60F37和W80F55处理的N2O累积排放量均较低。另外,2季玉米的土壤N2O通量与硝态氮和亚硝态氮含量之间显著相关,相关系数分别为0.433~0.579和0.396~0.532。
      结论  W80F55处理(田间持水量的70%~80%,以及50%氮肥作基肥土施,50%氮肥作滴灌施肥)降低种植玉米的土壤N2O排放。此外,土壤硝态氮和亚硝态氮含量显著影响土壤N2O排放。

       

      Abstract:
      Objective  The objectives of this study were to obtain a rational drip fertigation mode for reducing nitrous oxide (N2O) emission in maize-planting soil, and reveal the effects of soil inorganic nitrogen content on N2O emission under different drip irrigation amount and nitrogen fertigation ratios.
      Method  In the mobile rainproof shelter, two-season maize experiments with three drip irrigation amount (W60, W80 and W100 were 50%−60%, 70%−80% and 90%−100% of field water holding capacity, respectively) and two nitrogen fertigation proportions (F55: 50% nitrogen fertilizer applied to soil as basal fertilizer, and 50% nitrogen fertilizer as fertigation, F37: 30% nitrogen fertilizer applied to soil as basal fertilizer, and 70% nitrogen fertilizer as fertigation; Both of F55and F37 had the equal nitrogen rate of 180 kg·hm−2) were carried out. The soil N2O flux over the whole growth stage and soil inorganic nitrogen content at different growth stages were measured. Soil N2O emissions at the different growth stages and over the whole growth stage were calculated and the relationships between soil N2O flux and soil inorganic nitrogen content were analyzed.
      Result  The N2O emission fluxes of corn soil in two seasons were similar. Under the same nitrogen application ratio, soil N2O emission fluxes under W100 water treatment were higher than those under W60 and W80 in most maize growth periods, indicating that soil N2O emission fluxes under high water treatment were higher than those under medium and low water treatment. Under the same water treatment, soil N2O emission flux ratio of F55 was lower than that of F37 except in summer maize seedling stage. During the whole growth period, the cumulative emission of soil N2O under W60F55 treatment in spring was lower than that under other treatments, followed by W80F55, while those under W60F37 and W80F55 treatments in summer were lower. In addition, in two seasons, soil N2O flux was significantly correlated with nitrate nitrogen and nitrite nitrogen contents, with correlation coefficients ranging from 0.433 to 0.579 and 0.396 to 0.532, respectively.
      Conclusion  W80F55 treatment (70%−80% field water holding capacity, 50% nitrogen fertilizer as basal fertilizer and 50% nitrogen fertilizer as fertigation) reduces N2O emission from maize-planting soil. In addition, soil nitrate nitrogen and nitrite nitrogen contents significantly affect soil N2O emission.

       

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