王潇洁, 柳佳蓉, 李若林, 王世辰, 马静, 祝贞科, 张广斌, 徐华. 施氮量对太湖流域再生稻产量和温室气体排放的影响[J]. 中国生态农业学报 (中英文), 2024, 32(0): 1−11. DOI: 10.12357/cjea.20240093
引用本文: 王潇洁, 柳佳蓉, 李若林, 王世辰, 马静, 祝贞科, 张广斌, 徐华. 施氮量对太湖流域再生稻产量和温室气体排放的影响[J]. 中国生态农业学报 (中英文), 2024, 32(0): 1−11. DOI: 10.12357/cjea.20240093
WANG X J, LIU J R, LI R L, WANG S C, MA J, ZHU Z K, ZHANG G B, XU H. The impact of nitrogen application rate on rice yield and greenhouse gas emissions of ratoon rice in the Taihu Lake region[J]. Chinese Journal of Eco-Agriculture, 2024, 32(0): 1−11. DOI: 10.12357/cjea.20240093
Citation: WANG X J, LIU J R, LI R L, WANG S C, MA J, ZHU Z K, ZHANG G B, XU H. The impact of nitrogen application rate on rice yield and greenhouse gas emissions of ratoon rice in the Taihu Lake region[J]. Chinese Journal of Eco-Agriculture, 2024, 32(0): 1−11. DOI: 10.12357/cjea.20240093

施氮量对太湖流域再生稻产量和温室气体排放的影响

The impact of nitrogen application rate on rice yield and greenhouse gas emissions of ratoon rice in the Taihu Lake region

  • 摘要: 探索氮肥施用量对再生稻产量及温室气体排放(CH4和N2O)的影响, 以期为太湖流域种植再生稻的最佳施氮量提供参考。本研究于2022年4—10月在江苏宜兴采用静态箱-气相色谱法观测CH4和N2O排放通量, 试验设置3种再生季施氮量FL1: 75 kg(N)·hm−2、FL2: 125 kg(N)·hm−2、FL3: 175 kg(N)·hm−2, 头季均施240 kg(N)·hm−2, 同时设置不施肥处理(FL0)作为对照, 并在水稻收获时测定产量及其构成因子。试验结果显示, 促芽肥造成的N2O排放峰值最大, 且随施肥量的增加呈线性增加趋势, 总量占整个生育期的10.0%~50.7%; 两个稻季(头季+再生季)的N2O排放总量在1.30~8.69 kg(N)·hm−2范围内, 再生季排放量占6.94%~22.7%, 再生季N2O排放系数为0.38%~1.71%。两季CH4排放总量为58.1~78.7 kg·hm−2, 再生季占13.3%~23.8%, CH4排放总量随施氮量增加影响较小。两季水稻总产量为8.33~11.6 t·hm−2, 再生季占34.0%~46.1%, FL2和FL3的再生季产量分别较FL1增加32.3%和17.4%, 这与有效穗数分别增加27.2%和13.5%有关。两季温室气体排放强度为0.26~0.54 t CO2 e·t−1, FL3和FL2较FL1分别增加38.5%和10.3%。综上, 再生季施氮量为125 kg·hm−2时能获得高产且温室气体排放强度相对低, 是太湖流域蓄留再生稻值得推荐的氮肥施用量。

     

    Abstract: Exploring the effect of nitrogen (N) application rate on yield and greenhouse gas emissions (CH4 and N2O) of ratoon rice, to provide data reference for the optimal N application rate for planting ratoon rice in the Taihu Lake region. From April to October 2022, a static chamber-gas chromatography method was used to observe the CH4 and N2O emission fluxes of ratoon rice under three different N fertilization rates FL1: 75 kg(N)·hm−2, FL2: 125 kg(N)·hm−2, FL3: 175 kg(N)·hm−2 in Yixing, Jiangsu, and meanwhile setting no fertilization treatment (FL0) as a control. The yield and its constituent factors were observed during the rice harvest. The results showed that the peak N2O emission caused by bud-promoting fertilizer was the highest, and it showed a linear increasing trend with the increase of N fertilization rate, the total amount it caused accounted for 10.0%−50.7% of the entire growth period. Overall, the total (main reason+ratoon reason) N2O emissions ranged from 1.30 to 8.69 kg(N)·hm−2, with 6.94%−22.7% derived from ratoon rice, the N2O emission factor during the ratoon season ranged from 0.38% to 1.71%. Seasonal cumulative CH4 emissions ranged from 58.1 kg·hm−2 to 78.7 kg·hm−2, with 13.3%−23.8% in ratoon rice. The total CH4 emissions were not significantly impacted by the increase in the N application rate. The total rice yield was 8.33−11.6 t·hm−2, and the ratoon rice yield contributed 34.0%−46.1%. Compared with FL1, the ratoon season yields of FL2 and FL3 were increased by 32.3% and 17.7% respectively, which was related to the increase of effective panicle number by 27.2% and 13.5% respectively. The greenhouse gas emission intensity during the entire growth period was 0.26−0.54 t(CO2) e·t−1, and compared with FL1, FL3 increased by 38.5%, and FL2 increased by 10.3%. Overall, both high yield and relatively low greenhouse gas emission intensity can be obtained by applying 125 kg(N)·hm−2 in ratoon season. This N application rate is worth recommending for storing ratoon rice in the Taihu Lake region.

     

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