氮素形态和光照强度对水稻表土及根际N2O排放的影响
文献类型:期刊论文
作者 | 徐胜光1; 高召华2; 李冰3; 余磊[*]1; 林丽1; 陈泽斌1; 陈武荣1 |
刊名 | 植物营养与肥料学报
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出版日期 | 2016 |
卷号 | 22期号:5页码:1319-1328 |
关键词 | 氮素形态 根际 水稻 N 2 O 排放 叶际 N20排放 |
其他题名 | N 2 O emissions from rice phyllosphere and rhizosphere when supplied with different nitrogen forms and light intensities |
通讯作者 | yulei0425@163.com |
中文摘要 | 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(8:0018:00,4000 Lux;18:0022:00,0 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(8:0018:00,4000 Lux;18:0022:00,0 Lux)、强光(8:0018:00,8000 Lux;18:0022:00,0 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、0.46μg/(pot·h)和16.30、15.71、1.31μg/(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、0.26μg/(pot·h),强光照条件下分别为20.83、10.82、2.08μg/(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、0.30μg/(pot·h),强光条件下分别为32.83、16.41、1.27μg/(pot·h),自然光条件下分别为16.49、20.21、1.74μg/(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)间呈极显著正关,Y=1.963+0.444X(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。 |
英文摘要 |
Paddy ecosystem is an important source of N 2 O emission, this paper is aimed to clarify
the effects of different nitrogen forms under different light intensities on N 2 O 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 N 2 O emissions from rice phyllosphere and rhizosphere were measured by gas chromatography method. It was firstly studied about the effects of three N forms (NO 3 – -N, NH 4 NO 3 -N, NH 4 + -N) on N 2 O 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 N 2 O 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 NO 3 – -N, NH 4 NO 3 and NH 4 + -N with weak light, the mean rates of N 2 O 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 N 2 O emissions from rice phyllosphere treated with NO 3 – -N, NH 4 NO 3 and NH 4 + -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 N 2 O emissions among the three N forms under these two light
intensities, but no significant difference in N 2 O emissions between NO 3 – -N and NH 4 NO 3 under the sunlight. 3) Under NO 3 – -N, NH 4 NO 3 and NH 4 + -N with the weak light during flowering and seeding stages, the N 2 O emissions of rice rhizosphere were 27.76, 5.19 and 0.30 μg/(pot·h), respectively. Under the strong light, the N 2 O 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 N 2 O emission from rhizosphere was high with high light intensity under NH 4 NO 3 . No significant difference was observed in the N 2 O emission between NO 3 – -N and NH 4 NO 3 under sunlight, but did
under weak light. 4) There was a significantly positive linear regression relationship between N 2 O emission from rice phyllosphere(Y) and rhizosphere(X) (Y = 1.963 + 0.444X, R 2 = 0.661, P < 0.01). 【Conclusions】The N 2 O emissions from rice phyllosphere and rhizosphere can be increased significantly by NO 3 – -N, followed by NH 4 NO 3 . The N 2 O emissions is also increased with the increase of light intensity. The N 2 O emissions of phyllosphere can reflect the N 2 O 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. |
收录类别 | 其他 |
资助信息 | 国家自然科学基金项目(31160412,41361056);云南省基础研究面上项目(2011fz183);昆明学院人才引进项目(yjl12012)资助 |
语种 | 中文 |
源URL | [http://159.226.149.26:8080/handle/152453/10691] ![]() |
专题 | 昆明动物研究所_中国科学院昆明灵长类研究中心 |
作者单位 | 1.昆明学院 云南省都市特色农业工程技术研究中心;云南昆明 650214 2.云南农业大学资源与环境学院;云南昆明650201 3.中国科学院昆明动物研究所,云南昆明65022 |
推荐引用方式 GB/T 7714 | 徐胜光,高召华,李冰,等. 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. |
APA | 徐胜光.,高召华.,李冰.,余磊[*].,林丽.,...&陈武荣.(2016).氮素形态和光照强度对水稻表土及根际N2O排放的影响.植物营养与肥料学报,22(5),1319-1328. |
MLA | 徐胜光,et al."氮素形态和光照强度对水稻表土及根际N2O排放的影响".植物营养与肥料学报 22.5(2016):1319-1328. |
入库方式: OAI收割
来源:昆明动物研究所
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