Karlsruhe Institute of Technology, Institute of Meteorology and Climate Research-Atmospheric Environmental Research, Garmisch-Partenkirchen, Germany.
Karlsruhe Institute of Technology, Institute of Meteorology and Climate Research-Atmospheric Environmental Research, Garmisch-Partenkirchen, Germany.
Sci Total Environ. 2022 Feb 10;807(Pt 2):151051. doi: 10.1016/j.scitotenv.2021.151051. Epub 2021 Oct 25.
Crop residues may serve as a significant source of soil emissions of NO and other trace gases. According to the emission factors (EFs) set by the Intergovernmental Panel on Climate Change (IPCC), NO emission is proportional to the amount of N added by residues to the soil. However, the effects of crop residues on the source and sink strength of agroecosystems for trace gases are regulated by their properties, such as the C and N content; C/N ratio; lignin, cellulose, and soluble fractions; and residue humidity. In the present study, an automated dynamic chamber method was used in combination with soil mesocosms to simultaneously measure the effects of nine different crop residues (oilseed rape, winter wheat, field pea, maize, potato, mustard, red clover, sugar beet, and ryegrass) on soil respiration (CO) and reactive N fluxes (NO, NO, and NH) at a high temporal resolution. Specifically, crop residues were incorporated in the 0-4 cm topsoil layer and incubated for 60 days at a constant temperature (15 °C) and water-filled pore space (60% WFPS). Residue incorporation immediately and sharply increased soil NO and CO emissions, but these were short-lived and returned to background levels within respectively 10 and 30 days. The magnitude of increase in soil NO flux following residue incorporation was lower than that in CO and NO fluxes, with peak emissions observed around day 20. Overall, the N content or C/N ratio of the applied residue could not sufficiently explain the variation in soil NO and NO emissions. The range of the calculated NO EFs over a 60-day period was -0.17 to +4.5, being wider than that proposed by the IPCC (+0.01 to +1.1). Therefore, the residue maturity stage may be used as a simple proxy to estimate the NO + NO emissions from incorporated residue.
作物残体可能是土壤排放 NO 和其他痕量气体的重要来源。根据政府间气候变化专门委员会 (IPCC) 设定的排放因子 (EF),NO 排放与残体向土壤添加的 N 量成正比。然而,作物残体对痕量气体农业生态系统源汇强度的影响受其特性的调节,例如 C 和 N 含量;C/N 比;木质素、纤维素和可溶部分;以及残体湿度。在本研究中,采用自动化动态室法结合土壤中培养箱,同时测量了 9 种不同作物残体(油菜、冬小麦、田豌豆、玉米、马铃薯、芥菜、红三叶草、甜菜和黑麦草)对土壤呼吸(CO)和反应性 N 通量(NO、NO 和 NH)的影响,具有高时间分辨率。具体而言,将作物残体掺入 0-4 cm 的表土层中,并在恒定温度(15°C)和充满水的孔隙空间(60%WFPS)下培养 60 天。残体掺入立即且急剧增加了土壤 NO 和 CO 排放,但这些排放是短暂的,在分别 10 和 30 天内恢复到背景水平。残体掺入后土壤 NO 通量增加的幅度低于 CO 和 NO 通量,峰值排放出现在第 20 天左右。总体而言,施加残体的 N 含量或 C/N 比不能充分解释土壤 NO 和 NO 排放的变化。在 60 天期间计算的 NO EF 的范围为-0.17 至+4.5,比 IPCC 提出的范围(0.01 至+1.1)更宽。因此,残体成熟度阶段可作为估算掺入残体中 NO+NO 排放的简单替代指标。