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Estimating nitrogen flows of agricultural soils at a landscape level - A modelling study of the Upper Enns Valley, a long-term socio-ecological research region in Austria

机译:在景观水平上估算农业土壤的氮流量-奥地利长期社会生态研究区上恩斯山谷的模型研究

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This paper explores the fate of reactive nitrogen (Nr) on the landscape scale of present agricultural production practice on arable and grassland soils. We use the soil modelling tool Landscape DNDC (landscape scale DeNitrification-DeComposition model) to quantify resulting flows of Nr distributed to the atmosphere, hydrosphere and the crops. Test area is a watershed in the Austrian Alps characterized by arable production in the low-lying areas and grassland in the mountains. The approach considers an overall budget of nitrogen, and determines the nitrogen use efficiency for individual crops and crop rotations, with average levels found at 85% for the arable area and 68-98% for the grassland areas. Modelled Nr flows are compared to the values resulting from the national emission factor (EF) method used for the Austrian emission inventory. For the arable part of the study region, the annual sum of released Nr emissions derived from Landscape DNDC modelling is lower than the result of the EF method by about 13% (or 7 kg N ha(-1)). Model results are lower also for other Nr species, yet nitrate leaching rates as well as ammonia emissions contribute a major share. For grassland areas, nitrate leaching values estimated by Landscape DNDC greatly depend on local specifics and substantially exceed EF estimates. All other modelled Nr species are lower than the EF results. The model set-up allows to characterize spatially explicit effects of mitigation measures. As an example, we identify nitrous oxide (N2O) hot spots in the study region, and we quantify the N2O emission saving potential if focusing reduction efforts to such hot spots. Reducing fertilization of hot spots by half could remove 14% of N2O emission for 5% less crop yield and a loss of grassland yield by 1% when extrapolated to the whole study area. (c) 2019 The Authors. Published by Elsevier B.V. This is an open access article under the CC BY license (http://creativecommons.org/licenses/by/4.0/).
机译:本文以可耕地和草地土壤的当前农业生产实践的景观尺度探讨了活性氮(Nr)的命运。我们使用土壤建模工具Landscape DNDC(景观尺度DeNitrification-DeComposition模型)来量化分配到大气,水圈和农作物中的Nr流量。试验区是奥地利阿尔卑斯山的一个分水岭,其特征是在低洼地区和山区草地上进行耕作。该方法考虑了氮的总体预算,并确定了单个作物和作物轮作的氮利用效率,耕地的平均水平为85%,草原地区的平均水平为68-98%。将模拟的Nr流量与由用于奥地利排放清单的国家排放因子(EF)方法得出的值进行比较。对于研究区域的可耕部分,从景观DNDC模型得出的释放Nr的年排放总量比EF方法的结果低约13%(或7 kg N ha(-1))。其他Nr物种的模型结果也较低,但是硝酸盐的浸出率以及氨的排放量占主要份额。对于草原地区,Landscape DNDC估算的硝酸盐淋失值在很大程度上取决于当地的具体情况,大大超过了EF的估计值。所有其他建模的Nr物种均低于EF结果。通过模型设置,可以表征缓解措施在空间上的显式效果。例如,我们确定了研究区域中的一氧化二氮(N2O)热点,并且如果集中精力减少此类热点,我们就可以量化N2O减排的潜力。如果将热点施肥减少一半,则可以将N2O排放量减少14%,从而使作物产量降低5%,而将其推算到整个研究区域时,草地产量的损失<1%。 (c)2019作者。由Elsevier B.V.发布。这是CC BY许可下的开放获取文章(http://creativecommons.org/licenses/by/4.0/)。

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