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Identifying Spatial Heterogeneity in Ammonia Emissions from Agricultural Fertilization

机译:确定农业施肥产生的氨排放中的空间异质性

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Improved predictions for regional-scale modeling of atmospheric particulate matter (PM) formation and reactive nitrogen deposition to different ecosystems can be provided by developing improved NH3 emission inventories (EI), especially from agricultural fertilization (AF) and soils at spatial and temporal resolutions required by chemical transport models (CTMs). The Sparse Matrix Operator Kernel Emissions (SMOKE) model produces gridded emission inputs by disaggregating the National Emission Inventory (NEI) data using spatial surrogates and temporal factors to scales required by CTMs. For AF, NEI provides county-level NH_3 estimates produced by annual fertilizer sales data and approximate emission factors. Thus, SMOKE can only produce spatially averaged NH3 emissions that do not capture localized hotspots from crop-specific AF practices and soil-atmosphere interactions. According to NEI, AF contributed 55% of the anthropogenic NH_3 emissions to the atmosphere in Illinois (IL) in 2008. We have developed a high-spatial resolution; 4 km × 4 km EI for AF based NH_3 emissions for IL by improving existing spatial surrogate ratios in SMOKE by combining crop-specific fertilization rates with cropland distribution. While our total emissions estimates are within 2% of NEI, since both methods are constrained by fertilizer sales data; there are two major improvements. Firstly, it captures localized NH_3 emission hotspots at sub-county resolutions absent in NEI. Secondly, it also apportions NH_3 emissions to specific crops with corn fertilization contributing to 48% of AF emissions. The identified hotspots are being evaluated by spatial autocorrelation techniques to assess the suitability of this newly developed approach. Local crop schedules are being used to estimate temporal factors to further refine inputs to SMOKE. The newly developed EI will provide improved NH_3 emission estimates as direct inputs to SMOKE for high-spatial and temporal resolution regional-scale CTM modeling studies in PM formation and reactive nitrogen deposition to different ecosystems.
机译:可以通过开发改进的NH3排放清单(EI)(尤其是来自农业施肥(AF)和土壤所需的时空分辨率),来提供有关不同生态系统的大气颗粒物(PM)形成和反应性氮沉积的区域尺度模型的改进预测。通过化学传输模型(CTM)。稀疏矩阵运算符内核排放量(SMOKE)模型通过使用空间替代量和时间因素来分解CTM所需的比例来分解国家排放清单(NEI)数据,从而生成网格化的排放量输入。对于AF,NEI提供了由年度化肥销售数据和近似排放因子得出的县级NH_3估算值。因此,SMOKE只能产生空间平均的NH3排放,而这些排放却无法捕获特定于作物的自动对焦操作和土壤-大气相互作用中的局部热点。根据NEI,AF在2008年将人为的NH_3排放量中的55%排放到了伊利诺伊州(IL)的大气中。通过将特定于作物的施肥率与农田分布相结合来改善SMOKE中现有的空间替代比,从而使基于AF的IL的NH_3排放达到4 km×4 km EI。尽管我们的总排放量估算值不超过NEI的2%,但由于这两种方法都受到肥料销售数据的限制;有两个主要改进。首先,它以NEI所不具备的亚县分辨率捕获局部的NH_3发射热点。其次,它还利用玉米施肥将NH_3排放分配给特定作物,这占AF排放的48%。正在通过空间自相关技术评估已识别的热点,以评估这种新开发方法的适用性。当地的作物计划被用于估算时间因素,以进一步完善对SMOKE的投入。新开发的EI将提供改进的NH_3排放估算值作为SMOKE的直接输入,以进行高空间和时间分辨率的区域规模CTM建模研究,以研究不同生态系统的PM形成和活性氮沉积。

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