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Combined effects of nitrogen deposition and biochar application on emissions of N2O, CO2 and NH3 from agricultural and forest soils

机译:氮沉降和生物炭施用对农业和森林土壤N2O,CO2和NH3排放的综合影响

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摘要

Both nitrogen (N) deposition and biochar can affect the emissions of nitrous oxide (N2O), carbon dioxide (CO2) and ammonia (NH3) from different soils. Here, we have established a simulated wet N deposition experiment to investigate the effects of N deposition and biochar addition on N2O and CO2 emissions and NH3 volatilization from agricultural and forest soils. Repacked soil columns were subjected to six N deposition events over a 1-year period. N was applied at rates of 0 (N0), 60 (N60), and 120 (N120) kg Nh a(-1) yr(-1) without or with biochar (0 and 30 t ha(-1) yr-1). For agricultural soil, adding N increased cumulative N2O emissions by 29.8% and 99.1% (p < 0.05) from the N60 and N120 treatments, respectively as compared to without N treatments, and N120 emitted 53.4% more (p < 0.05) N2O than the N60 treatment; NH3 volatilization increased by 33.6% and 91.9% (p < 0.05) from the N60 and N120 treatments, respectively, as compared to without N treatments, and N120 emitted 43.6% more (p < 0.05) NH3 than N60; cumulative CO2 emissions were not influenced by N addition. For forest soil, adding N significantly increased cumulative N2O emissions by 141.2% (p < 0.05) and 323.0% (p < 0.05) from N60 and N120 treatments, respectively, as compared to without N treatments, and N120 emitted 75.4% more (p < 0.05) N2O than N60; NH3 volatilization increased by 39.0% (p < 0.05) and 56.1% (p < 0.05) from the N60 and N120 treatments, respectively, as compared to without N treatments, and there was no obvious difference between N120 and N60 treatments; cumulative CO2 emissions were not influenced by N addition. Biochar amendment significantly (p < 0.05) decreased cumulative N2O emissions by 20.2% and 25.5% from agricultural and forest soils, respectively, and increased CO2 emissions slightly by 7.2% and NH3 volatilization obviously by 21.0% in the agricultural soil, while significantly decreasing CO2 emissions by 31.5% and NH3 volatilization by 22.5% in the forest soil. These results suggest that N deposition would strengthen N2O and NH3 emissions and have no effect on CO2 emissions in both soils, and treatments receiving the higher N rate at N120 emitted obviously more N2O and NH3 than the lower rate at N60. Under the simulated N deposition circumstances, biochar incorporation suppressed N2O emissions in both soils, and produced contrasting effects on CO2 and NH3 emissions, being enhanced in the agricultural soil while suppressed in the forest soil
机译:氮(N)的沉积和生物炭都会影响不同土壤中一氧化二氮(N2O),二氧化碳(CO2)和氨(NH3)的排放。在这里,我们建立了一个模拟的湿N沉积实验,以研究N沉积和生物炭添加对农业和森林土壤中N2O和CO2排放以及NH3挥发的影响。重新包装的土壤柱在1年内经历了6次N沉积事件。在不使用或使用生物炭(0和30 t ha(-1)yr-1的情况下)以0(N0),60(N60)和120(N120)kg Nh a(-1)yr(-1)的比率施用N )。对于农业土壤,与未施氮处理相比,与不施氮处理相比,施氮增加了N60和N120处理的累积N2O排放分别增加了29.8%和99.1%(p <0.05),并且N120排放的N2O比施氮处理增加了53.4%(p <0.05)。 N60处理;与不使用N处理相比,N60和N120处理的NH3挥发分别增加了33.6%和91.9%(p <0.05),并且N120排放的NH3比N60增加了43.6%(p <0.05)。累积的二氧化碳排放量不受氮添加的影响。对于森林土壤,与未施氮处理相比,与不施氮处理相比,加入氮显着增加了N60和N120处理的累积N2O排放量分别为141.2%(p <0.05)和323.0%(p <0.05),并且N120排放量增加了75.4%(p <0.05)N2O大于N60;与未施氮处理相比,N60和N120处理的NH3挥发分别增加了39.0%(p <0.05)和56.1%(p <0.05),并且N120和N60处理之间没有明显的差异。累积的二氧化碳排放量不受氮添加的影响。生物炭改良显着(p <0.05)分别使农业和森林土壤中的累积N2O排放量减少了20.2%和25.5%,并使农业土壤中的CO2排放量略微增加了7.2%,NH3挥发明显增加了21.0%,同时显着降低了CO2森林土壤中的二氧化碳排放量减少了31.5%,氨气挥发减少了22.5%。这些结果表明,氮沉降将增强两种土壤中的N2O和NH3排放,而对CO2排放没有影响,并且在N120处获得较高N比率的处理明显比在N60处较低的比率排放更多的N2O和NH3。在模拟的氮沉降条件下,生物炭的掺入抑制了两种土壤中的N2O排放,并对CO2和NH3排放产生了相反的影响,在农业土壤中得到增强,而在森林土壤中得到抑制

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