• ISSN 1008-505X
  • CN 11-3996/S
徐胜光, 高召华, 林丽, 陈泽斌, 陈武荣, 李冰, 余磊. 氮素形态和光照强度对水稻表土及根际 N2O 排放的影响[J]. 植物营养与肥料学报, 2016, 22(5): 1319-1328. DOI: 10.11674/zwyf.15402
引用本文: 徐胜光, 高召华, 林丽, 陈泽斌, 陈武荣, 李冰, 余磊. 氮素形态和光照强度对水稻表土及根际 N2O 排放的影响[J]. 植物营养与肥料学报, 2016, 22(5): 1319-1328. DOI: 10.11674/zwyf.15402
XU Sheng-guang, GAO Zhao-hua, LIN Li, CHEN Ze-bin, CHEN Wu-rong, LI Bing, YU Lei. N2O emissions from rice phyllosphere and rhizosphere when supplied with different nitrogen forms and light intensities[J]. Journal of Plant Nutrition and Fertilizers, 2016, 22(5): 1319-1328. DOI: 10.11674/zwyf.15402
Citation: XU Sheng-guang, GAO Zhao-hua, LIN Li, CHEN Ze-bin, CHEN Wu-rong, LI Bing, YU Lei. N2O emissions from rice phyllosphere and rhizosphere when supplied with different nitrogen forms and light intensities[J]. Journal of Plant Nutrition and Fertilizers, 2016, 22(5): 1319-1328. DOI: 10.11674/zwyf.15402

氮素形态和光照强度对水稻表土及根际 N2O 排放的影响

N2O emissions from rice phyllosphere and rhizosphere when supplied with different nitrogen forms and light intensities

  • 摘要:
    目的 稻田生态系统是 N2O 的重要排放源,本研究旨在探讨氮素形态和光照对水稻根际、叶际 N2O 排放作用及其机制。
    方法 试验采用水培方法,在小型光控培养箱内进行,供试作物为水稻。将水稻地上部和地下部严格分隔在试验装置内室和外室,用气相色谱法测定水稻根、叶界面排放的 N2O 量。首先进行了弱光 (8:00~18:00, 4000 Lux;18:00~22:00, 0 Lux) 和供氮量一致条件下 (N 90 mg/L),NO3-N、NH4NO3 和 NH4+-N 3 种氮素形态对水稻根、叶界面 N2O 排放的影响的试验。在此基础上,进行了不同光照条件下 弱光 (8:00~18:00, 4000 Lux; 18:00~22:00, 0 Lux)、强光 (8:00~18:00, 8000 Lux; 18:00~22:00, 0 Lux) 和自然光不同氮素形态对水稻根、叶界面 N2O 排放的影响的试验。
    结果 1) 相同供氮水平、弱光条件下,NO3-N、NH4NO3、NH4+-N 处理的水稻分蘖期叶际及根际 N2O 排放速率分别为 6.37、5.03、0.46 μg/(pot·h) 和 16.30、15.71、1.31 μg/(pot·h),开花结实期及成熟衰老期亦获得相似的结果。NO3-N、NH4NO3 处理水稻根际、叶际 N2O 排放量显著高于 NH4+-N ( P < 0.05)。 2) 弱光照条件下,NO3-N、NH4NO3 和 NH4+-N 处理的水稻开花结实期叶际 N2O 平均排放速率分别为 10.47、3.70、0.26 μg/(pot·h),强光照条件下分别为 20.83、10.82、2.08 μg/(pot·h),两种光照条件下 3 种氮源处理之间 N2O 平均排放速率差异显著,自然光照条件下 NO3-N 与 NH4NO3 处理间水稻叶际 N2O 排放差异不显著。 3) 在弱光条件下,NO3-N、NH4NO3 和 NH4+-N 处理的水稻根际 N2O 排放速率分别为 27.76、5.19、0.30 μg/(pot·h),强光条件下分别为 32.83、16.41、1.27 μg/(pot·h),自然光条件下分别为 16.49、20.21、1.74 μg/(pot·h)。NH4NO3 处理水稻根际 N2O 排放随光照增强而增加,自然光条件下 NO3-N 与 NH4NO3 处理间水稻根际 N2O 排放差异不显著,但弱光条件下差异显著; 4) 叶际 N2O 排放速率 ( Y) 与根际 N2O 排放速率 ( X) 间呈极显著正相关, Y = 1.963 + 0.444 X ( R2 = 0.661, P < 0.01)。
    结论 不论光照条件强弱,供应 NO3-N 均显著提高水稻根、叶界面的 N2O-N 排放,NH4NO3 次之。光照越强,排放就越明显。叶际 N2O 排放可以反映出根际的排放,因此,水稻施肥应尽量选用铵态氮肥,避免使用硝态氮以及含有硝态氮的肥料。

     

    Abstract:
    Objectives Paddy ecosystem is an important source of N2O emission, this paper is aimed to clarify the effects of different nitrogen forms under different light intensities on N2O emission from rice phyllosphere and rhizosphere and the mechanism of these effects.
    Methods Hydroponic methods with rice were adopted in small incubators in which the light was controlled. The incubators were separated into inner and outer chambers, and the above-ground part of rice was completely sealed in the inner chamber and the roots in the outer chamber. The N2O emissions from rice phyllosphere and rhizosphere were measured by gas chromatography method. It was firstly studied about the effects of three N forms (NO3-N, NH4NO3-N, NH4+-N) on N2O emission of rice phyllosphere and rhizosphere under weak light (8:00-18:00, 4000 Lux) and same N applications (90 mg/L). Then the experiments were conducted to further study the effects of different N forms on N2O emission from rice phyllosphere and rhizosphere under different light intensities (weak light, 8:00-18:00, 4000 Lux; 18:00-22:00, 0 Lux; strong light, 8:00-18:00, 8000 Lux, 18:00-22:00, 0 Lux and natural sunlight, respectively).
    Results 1) Under NO3-N, NH4NO3 and NH4+-N with weak light, the mean rates of N2O emission from phyllosphere and rhizosphere were 6.37, 5.03 and 0.46 μg/(pot·h), respectively, and 16.30, 15.71 and 1.31 μg/(pot·h), respectively, during rice tillering stage, and similar results were obtained during rice flowering, seeding and mature aging stages under the same conditions. 2) Under weak light, the N2O emissions from rice phyllosphere treated with NO3-N, NH4NO3 and NH4+-N were 10.47, 3.70 and 0.26 μg/(pot·h), respectively, and 20.83, 10.82 and 2.08 μg/(pot·h) with strong light, respectively, during flowering and seeding stages. There were significant differences in N2O emissions among the three N forms under these two light intensities, but no significant difference in N2O emissions between NO3-N and NH4NO3 under the sunlight. 3) Under NO3-N, NH4NO3 and NH4+-N with the weak light during flowering and seeding stages, the N2O emissions of rice rhizosphere were 27.76, 5.19 and 0.30 μg/(pot·h), respectively. Under the strong light, the N2O emission rates were 20.83, 10.82 and 2.08 μg/(pot·h), respectively, and 16.49, 20.21 and 1.74 μg/(pot·h), respectively, under the sunlight. The N2O emission from rhizosphere was high with high light intensity under NH4NO3. No significant difference was observed in the N2O emission between NO3-N and NH4NO3 under sunlight, but did under weak light. 4) There was a significantly positive linear regression relationship between N2O emission from rice phyllosphere( Y) and rhizosphere( X) ( Y = 1.963 + 0.444 X, R2 = 0.661, P < 0.01).
    Conclusions The N2O emissions from rice phyllosphere and rhizosphere can be increased significantly by NO3-N, followed by NH4NO3. The N2O emissions is also increased with the increase of light intensity. The N2O emissions of phyllosphere can reflect the N2O emissions of rhizosphere. Therefore, while applying N fertilizers, ammonium fertilizers should be preferentially used and nitrate nitrogen and fertilizers containing nitrate nitrogen should be avoided.

     

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