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The contribution of nitrogen transformation processes to total N2O emissions from soils used for intensive vegetable cultivation

机译:氮素转化过程对蔬菜精耕细作土壤总N2O排放的贡献

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The rapid expansion of intensively farmed vegetable fields has substantially contributed to the total N2O emissions from croplands in China. However, to date, the mechanisms underlying this phenomenon have not been completely understood. To quantify the contributions of autotrophic nitrification, heterotrophic nitrification, and denitrification to N2O production from the intensive vegetable fields and to identify the affecting factors, a N-15 tracing experiment was conducted using five soil samples collected from adjacent fields used for rice-wheat rotation system (WF), or for consecutive vegetable cultivation (VF) for 0.5 (VF1), 6 (VF2), 8 (VF3), and 10 (VF4) years. Soil was incubated under 50% water holding capacity (WHC) at 25A degrees C for 96 h after being labeled with (NH4NO3)-N-15 or NH (4) (15) NO3. The average N2O emission rate was 24.2 ng N kg(-1) h(-1) in WF soil, but it ranged from 69.6 to 507 ng N kg(-1) h(-1) in VF soils. Autotrophic nitrification, heterotrophic nitrification and denitrification accounted for 0.3-31.4%, 25.4-54.4% and 22.5-57.7% of the N2O emissions, respectively. When vegetable soils were moderately acidified (pH, 6.2 to a parts per thousand yenaEuro parts per thousand 5.7), the increased N2O emissions resulted from the increase of both the gross autotrophic and heterotrophic nitrification rates and the N2O product ratio of autotrophic nitrification. However, once severe acidification occurred (as in VF4, pH a parts per thousand currency signaEuro parts per thousand 4.3) and salt stress increased, both autotrophic and heterotrophic nitrification rates were inhibited to levels similar to those of WF soil. The enhanced N2O product ratios of heterotrophic nitrification (4.84aEuro degrees), autotrophic nitrification (0.93aEuro degrees) and denitrification processes were the most important factors explaining high N2O emission in VF4 soil. Data from this study showed that various soil conditions (e.g., soil salinity and concentration of NO (3) (-) or NH (4) (+) ) could also significantly affect the sources and rates of N2O emission.
机译:集约化蔬菜种植地的迅速发展为中国农田的N2O排放总量做出了巨大贡献。但是,迄今为止,尚未完全理解这种现象的潜在机制。为了量化自养硝化,异养硝化和反硝化对密集蔬菜田生产N2O的贡献并确定影响因素,使用从相邻稻田轮作中收集的五个土壤样品进行了N-15示踪试验系统(WF)或连续蔬菜种植(VF)的时间为0.5(VF1),6(VF2),8(VF3)和10(VF4)年。用(NH4NO3)-N-15或NH(4)(15)NO3标记后,将土壤在50%持水量(WHC)下于25A摄氏度下孵育96小时。在WF土壤中,N2O的平均排放率为24.2 ng N kg(-1)h(-1),而在VF土壤中,N2O的平均排放率为69.6至507 ng N kg(-1)h(-1)。自养硝化,异养硝化和反硝化分别占N2O排放的0.3-31.4%,25.4-54.4%和22.5-57.7%。当菜园土壤被适度酸化(pH值为6.2到千分之一欧元/千分之一欧元5.7)时,N2O排放量的增加是由于总自养硝化率和异养硝化率的增加以及自养硝化的N2O产物比率增加。但是,一旦发生严重的酸化作用(如VF4中,pH值等于千分之一欧元等于十分之几千欧元等于4.3),盐胁迫增加,自养和异养硝化率均被抑制到与WF土壤相似的水平。异养硝化(4.84aEuro度),自养硝化(0.93aEuro度)和反硝化过程中N2O生成比例的提高是解释VF4土壤中N2O排放高的最重要因素。这项研究的数据表明,各种土壤条件(例如,土壤盐度和NO(3)(-)或NH(4)(+)的浓度)也会显着影响N2O的排放源和排放速率。

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