• ISSN 1008-505X
  • CN 11-3996/S
CHENG Bo-hao, BAI Jin-ze, LIU Zhen-yuan, SONG Jia-jie, XU Hong-wei, WANG Xing, REN Guang-xin, FENG Yong-zhong. Short-term effects of straw return on N2O emissions from wheat and maize rotation fields in Guanzhong area[J]. Journal of Plant Nutrition and Fertilizers, 2023, 29(6): 1002-1012. DOI: 10.11674/zwyf.2022562
Citation: CHENG Bo-hao, BAI Jin-ze, LIU Zhen-yuan, SONG Jia-jie, XU Hong-wei, WANG Xing, REN Guang-xin, FENG Yong-zhong. Short-term effects of straw return on N2O emissions from wheat and maize rotation fields in Guanzhong area[J]. Journal of Plant Nutrition and Fertilizers, 2023, 29(6): 1002-1012. DOI: 10.11674/zwyf.2022562

Short-term effects of straw return on N2O emissions from wheat and maize rotation fields in Guanzhong area

  • Objectives The responses of environmental factors and soil N2O emissions to short-term straw return were analyzed for more accurate evaluation of the benefits of short-term straw return in terms of N2O emissions under fertilization.
    Methods A field trial was conducted in Guanzhong area, Shaanxi Province, from 2020 to 2021. The cropping system was winter wheat and summer maize rotation. A two-factor split-zone design was adopted, with the main factor of straw return (W1) and no return (W0), and the sub-factor of fertilization, composing 6 treatments, as: no fertilizer (W1, W0), nitrogen fertilizer (W1N, W0N) and nitrogen and phosphorus fertilizer (W1NP, W0NP). Soil water content, temperature, NO3-N, NH4+-N, and available P content, N2O emission fluxes were measured, crop yields were investigated, and the relationships between soil N2O emissions and environmental factors were explored.
    Results The soil water content in W1 treatment was 1.1%–16.3% higher than in W0, and the peak soil NO3--N content in W1N treatment was 17.6%–30.5% higher than in W0N. The soil NO3-N and NH4+-N contents of two N and two NP treatments first increased rapidly and then decreased slowly as the growth period progressed, and the peak soil NO3-N of N treatments was 17.0%−20.8% higher than that of NP treatment. The soil available P content in NP treatments increased rapidly and then decreased slowly as the growth period progressed, and significantly higher than those in no fertilizer and N treatments on average. The soil N2O emission fluxes arrived peaks at 6 days and 12 days after fertilization in winter wheat and summer maize seasons, respectively. Compared with W0N and W0NP, W1N and W1NP increased the peak soil N2O emissions by 5.0% and 38.5%, and the annually cumulative N2O emissions by 291.13 g/hm2 and 379.99 g/hm2, respectively (P<0.05). The cumulative annual soil N2O emission in treatment W1N was 298.14 g/hm2 higher than in W1NP (P<0.05). W1NP decreased 2.43% and 298.14 g/hm2 of the peak and cumulative annual N2O emission, compare to W1N, while W0NP decreased 54.67% and 386.99 g/hm2 of peak and cumulative annual N2O emission, compared to W0N . Correlation analysis revealed that N2O emission fluxes were positively correlated with soil temperature and water content in maze season, and NO3-N, NH4+-N, and available P contents in both maize and wheat seasons (P<0.01). Under the same straw return condition, the N2O emission intensity showed descent order of N fertilization, NP application, and no fertilization. Under the same fertilization, the N2O emission intensity with straw return was higher than without straw return
    Conclusions Whether straw was returned to the field or not, the combined N and P application was more effective in reducing cumulative N2O emissions than N fertilizer alone, as the increased soil available P content and lower soil NO3-N peak content. Although straw returning to the field also increased the soil available phosphorus content in the short term, its higher soil moisture content and NO3-N content led to higher N2O emission flux and cumulative N2O emissions from farmland. This short term adverse ecological impact should be considered in the evaluation of straw return.
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