长期玉米秸秆还田对冬小麦-夏玉米种植体系NO排放的影响

Effect of long-term maize residues incorporation on NO emissions from a winter wheat-summer maize cropping system

  • 摘要: 为定量分析冬小麦-夏玉米种植体系NO排放量对玉米秸秆还田的响应及其主要影响因素, 本研究基于长期定位施肥试验(始于1990年), 设置不施肥对照(CK)、施化肥(NPK)和化肥加玉米秸秆(NPKS) 3种处理, 连续2年(2022年10月—2024年10月)观测NO通量的动态变化。结果表明, CK处理NO通量低, NPK和NPKS处理NO通量高峰均出现在施肥后。NO通量与土壤温度和孔隙含水量的边界线分别符合逻辑斯蒂克和高斯模型, 与铵态氮和硝态氮浓度的边界线均符合线性模型。CK、NPK和NPKS处理NO年排放量分别为0.18~0.19、0.31~0.81和0.65~1.10 kg/hm2。在两个冬小麦季, NPKS排放量较NPK分别低60%和高28%, 但差异均不显著; 在两个夏玉米季, NPKS排放量较NPK显著增加60%~231% (P<0.05)。NPKS年排放量较NPK显著增加37%~113% (P<0.05), 这可能与NPKS土壤有机质含量较NPK显著提高约20%有关(P<0.05)。在夏玉米季, 土壤有机质对NO通量的促进作用在温暖潮湿的环境中被放大; 在冬小麦季, 受低温胁迫及秸秆还田的影响, 土壤有机质的作用可能被削弱或掩盖。总之, 在长期玉米秸秆还田条件下, 冬小麦-夏玉米种植体系NO年排放量显著增加, NO减排需重点关注夏玉米季。

     

    Abstract: Agroecosystems are a significant source of nitric oxide (NO) which serves as an air pollutant. There is an urgent need to quantify and control NO emissions from agroecosystems. The NO fluxes were measured in a long-term (since 1990) fertilized winter wheat-maize cropping system for two years (from October 2022 to October 2024). The aims were to quantify the responses of NO emissions to maize stalk incorporation and to identify the major regulatory factors. The field trials included an unfertilized control (CK), chemical fertilizers (NPK), chemical fertilizers combined with maize residues (NPKS). The CK treatment was not fertilized throughout the year. The NPK and NPKS treatments received the same amount of urea, with nitrogen application rates of 165 and 188 kg/hm2 in the winter wheat and maize seasons, respectively. All wheat straw and maize stalk were removed from CK and NPK at harvest. For NPKS, maize stalk (with a nitrogen application rate averaging 40 kg/hm2) was retained at the time of maize harvest while wheat straw was removed at the time of winter wheat harvest. The results showed that the NO fluxes were low in CK, while they always peaked following fertilization in NPK and NPKS. The boundary lines of NO fluxes followed a logistic model and a Gaussian model against soil temperature and water-filled pore space, respectively, and linear models against ammonium and nitrate concentrations. The CK, NPK, and NPKS treatments showed annual NO emissions of 0.18−0.19, 0.31−0.81, and 0.65−1.10 kg/hm2, respectively. In the two winter wheat seasons, cumulative NO emissions of NPKS were either 60% lower or 28% higher than those of NPK. In the two maize seasons, cumulative NO emissions of NPKS were 60%−231% higher (P<0.05). Annual NO emissions of NPKS were 37%−113% higher than those of NPK (P<0.05). The enhanced NO emissions mostly occurred in maize seasons, which were attributed to the 20% higher soil organic matter content of NPKS than that of NPK (P<0.05). In maize seasons, the promoting effect of soil organic matter on NO fluxes may be amplified in a warm and humidity environment, while such effect may be weakened or overrode by low temperature and stalk incorporation in winter wheat seasons. With long-term maize stalk incorporation, annual NO emissions from the winter wheat-maize cropping system were significantly enhanced, and mitigation efforts need to focus on the maize season.

     

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