Ni Xue, Hao Qing-Ju, Chen Shi-Jie, Li Xiao-Xi, Shi Xiao-Jun, Jiang Chang-Sheng
Key Laboratory of Eco-environments in Three Gorges Reservoir Region of Ministry of Education, College of Resources and Environment, Southwest University, Chongqing 400716.
National Purple Soil Fertility and Fertilizer Efficiency Monitoring Base, Chongqing 400716, China.
Huan Jing Ke Xue. 2019 Feb 8;40(2):893-903. doi: 10.13227/j.hjkx.201806139.
To investigate the effects of plastic film mulching and nitrogen fertilizer application on NO emissions from a chili-radish rotation system, field observations were conducted from May 2014 to April 2016 in the Key Field Station for Monitoring of Eco-Environment of Purple Soil of the Ministry of Agriculture of China in the farm of Southwest University in Chongqing. Static opaque and gas chromatography was used to determine emissions. Eight treatments were set up in the field experiment:control routine (no N application and no plastic film mulching; NN0), control mulching (FN0), low N routine (NN1), low N mulching (FN1), conventional N routine (NN2), conventional N mulching (FN2), high N routine (NN3), and high N mulching (FN3). The characteristics and influencing factors of NO emissions and the changes of soil carbon and nitrogen composition across all treatments were examined. The results demonstrated significant differences in NO emissions from the vegetable fields between mulching and no mulching treatments. The mean NO flux under no mulching was significantly greater than that of mulching during the chili growing season (<0.05), but the opposite was true during the radish growing season (<0.05). During the experimental period, the average annual cumulative NO emissions from nitrogen-free, low-nitrogen, medium-nitrogen, and high-nitrogen vegetable plots under mulching treatment were 244.91, 730.49, 903.32, and 1865.45 mg·m, respectively; the average annual cumulative NO emissions under no mulching treatment were 221.48, 840.33, 1256.50, and 1469.67 mg·m, respectively. The NO emissions from vegetable plots with different N application gradients showed an increase in NO emissions from vegetable plots as N application increased. By calculating the NO emissions coefficient, it was determined that the NO emissions coefficient was reduced to a certain extent under mulching treatment during the chili season, while there was no obvious trend in the radish season. From May 2014 to April 2015, the NO emissions coefficients of low-nitrogen application under two mulching treatments were both the highest under the same mulching levels during the chili growing season, but they were both the highest in the high-nitrogen application under two mulching levels during the radish growing season. From May 2015 to April 2016, the highest NO emissions coefficient was observed in the high-nitrogen application under two mulching treatments during the chili season; however, the lowest values were observed in the low-nitrogen application under two mulching treatments during the radish growing season. Such results may be related to the duration of plastic film mulching and the type of plant. The NO fluxes were both significantly positively correlated to the content of soil N and soil temperature. Plastic film mulching can increase the soil N to a certain extent and can therefore can affect NO emissions.
为探究地膜覆盖和氮肥施用对辣椒-萝卜轮作系统一氧化氮(NO)排放的影响,于2014年5月至2016年4月在中国农业农村部紫色土生态环境监测重点野外科学观测试验站(位于重庆西南大学农场)开展了田间观测。采用静态暗箱-气相色谱法测定排放情况。田间试验设置了8个处理:常规对照(不施氮且不覆盖地膜;NN0)、覆盖对照(FN0)、低氮常规(NN1)、低氮覆盖(FN1)、常规氮常规(NN2)、常规氮覆盖(FN2)、高氮常规(NN3)和高氮覆盖(FN3)。研究了所有处理下NO排放的特征、影响因素以及土壤碳氮组成的变化。结果表明,覆膜处理与不覆膜处理的菜地NO排放存在显著差异。在辣椒生长季,不覆膜处理下的平均NO通量显著高于覆膜处理(P<0.05),而在萝卜生长季则相反(P<0.05)。试验期间,覆膜处理下无氮、低氮、中氮和高氮菜地的年均累积NO排放量分别为244.91、730.49、903.32和1865.45 mg·m;不覆膜处理下的年均累积NO排放量分别为221.48、840.33、1256.50和1469.67 mg·m。不同施氮梯度菜地的NO排放随施氮量增加而增加。通过计算NO排放系数发现,辣椒季覆膜处理下NO排放系数有所降低,而萝卜季无明显变化趋势。2014年5月至2015年4月,辣椒生长季两种覆膜处理下低氮施用量的NO排放系数在相同覆膜水平下均最高,但萝卜生长季两种覆膜水平下高氮施用量的NO排放系数均最高。2015年5月至2016年4月,辣椒季两种覆膜处理下高氮施用量的NO排放系数最高;而萝卜生长季两种覆膜处理下低氮施用量的NO排放系数最低。这些结果可能与地膜覆盖持续时间和植物类型有关。NO通量均与土壤氮含量和土壤温度显著正相关。地膜覆盖可在一定程度上增加土壤氮含量,进而影响NO排放。