• ISSN 1008-505X
  • CN 11-3996/S
TIAN Yu-ping, SHUANG Rui-chen, LIU Yuan-qing, WANG Li-gang, MENG Fan-qiao. Contribution of nitrogen sources to NH3 volatilization in plastic-shed soilrevealed by 15N natural abundance[J]. Journal of Plant Nutrition and Fertilizers, 2024, 30(2): 242-251. DOI: 10.11674/zwyf.2023383
Citation: TIAN Yu-ping, SHUANG Rui-chen, LIU Yuan-qing, WANG Li-gang, MENG Fan-qiao. Contribution of nitrogen sources to NH3 volatilization in plastic-shed soilrevealed by 15N natural abundance[J]. Journal of Plant Nutrition and Fertilizers, 2024, 30(2): 242-251. DOI: 10.11674/zwyf.2023383

Contribution of nitrogen sources to NH3 volatilization in plastic-shed soilrevealed by 15N natural abundance

  • Objectives Excessive nitrogen (N) fertilization results in serious ammonia (NH3) volatilization in plastic-shed vegetable production in China. The NH3 volatilization as affected by fertilizer types was studied using the 15N natural abundance in the fertilizers, and the contribution rate was quantitatively analyzed for the scientific nitrogen management with less nitrogen loss.
    Methods A 40-day tomato-pot production experiment was conducted, the test brown soil was neither applied with any fertilizer nor used for cropping. Taking no N fertilizer as control (CK), three treatments at the same N basal application rate (N 3 g/pot) were set up, i.e. only chicken manure compost (M), only urea fertilizer (U), and half chicken manure half urea (MU). The NH3 volatilization rate and cumulative emission were monitored by static chamber method. The contribution of fertilizer to total NH3 volatilization in soil was quantified by the 15N natural abundance method.
    Results The NH3 volatilization rate increased rapidly and reached peak within 3 to 6 days after basal N fertilization, and then slowly decreased to the level of pre-fertilization at the 33th day after the basal N fertilization. The net NH3 volatilization accumulation in M treatment was 60.8% and 63.1% lower than in MU and U treatment, respectively (P<0.05), and that in MU (4.62%) was not reduced significantly, relative to U treatment. The corresponding NH3 volatilization coefficients were 1.37% (U), 1.29% (MU) and 0.51% (M), respectively. The measured δ15N-NH3 values decreased rapidly as the NH3 volatilization proceeded, and gradually increased to the level of pre-fertilization. The M treatment had higher average δ15N-NH3 values compared to the MU and U treatments. The contribution to NH3 volatilization were 30.5% for chicken manure in M treatment, 53.1% for urea in U treatment, and 28.6% and 56.6% for chicken manure and urea in the MU treatment, respectively.
    Conclusions Under the same fertilizer N rate, application of chicken manure could reduce the total NH3 volatilization significantly, but the combined application of chicken manure and urea would not show significantly mitigation effect, compared to urea application. Isotope fractionation analysis during NH3 volatilization revealed that the contribution of chicken manure and urea to soil NH3 volatilization is not significantly affected by single or combined application. Therefore, controlling the chemical N input is crucial for reducing NH3 volatilization.
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