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Carbonaceous aerosol source apportionment using the Aethalometer model – evaluation by radiocarbon and levoglucosan analysis at a rural background site in southern Sweden

机译:碳质气溶胶源分配使用聚体模型 - 瑞典南部农村背景现场的Radiocarbon和左葡萄糖分析评估

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With the present demand on fast and inexpensive aerosol source apportionment methods, the Aethalometer model was evaluated for a full seasonal cycle (June 2014–June 2015) at a rural atmospheric measurement station in southern Sweden by using radiocarbon and levoglucosan measurements. By utilizing differences in absorption of UV and IR, the Aethalometer model apportions carbon mass into wood burning (WB) and fossil fuel combustion (FF) aerosol. In this study, a small modification in the model in conjunction with carbon measurements from thermal–optical analysis allowed apportioned non-light-absorbing biogenic aerosol to vary in time. The absorption differences between WB and FF can be quantified by the absorption ?ngstr?m exponent (AAE). In this study AAEWB was set to 1.81 and AAEFF to 1.0. Our observations show that the AAE was elevated during winter (1.36?±?0.07) compared to summer (1.12?±?0.07). Quantified WB aerosol showed good agreement with levoglucosan concentrations, both in terms of correlation (R2?=?0.70) and in comparison to reference emission inventories. WB aerosol showed strong seasonal variation with high concentrations during winter (0.65?μg?m?3, 56?% of total carbon) and low concentrations during summer (0.07?μg?m?3, 6?% of total carbon). FF aerosol showed less seasonal dependence; however, black carbon (BC) FF showed clear diurnal patterns corresponding to traffic rush hour peaks. The presumed non-light-absorbing biogenic carbonaceous aerosol concentration was high during summer (1.04?μg?m?3, 72?% of total carbon) and low during winter (0.13?μg?m?3, 8?% of total carbon). Aethalometer model results were further compared to radiocarbon and levoglucosan source apportionment results. The comparison showed good agreement for apportioned mass of WB and biogenic carbonaceous aerosol, but discrepancies were found for FF aerosol mass. The Aethalometer model overestimated FF aerosol mass by a factor of 1.3 compared to radiocarbon and levoglucosan source apportionment. A performed sensitivity analysis suggests that this discrepancy can be explained by interference of non-light-absorbing biogenic carbon during winter. In summary, the Aethalometer model offers a cost-effective yet robust high-time-resolution source apportionment at rural background stations compared to a radiocarbon and levoglucosan alternative.
机译:随着对快速和廉价的气溶胶源分配方法的需求,通过使用RadioCarbon和左葡萄糖测量,评估了在瑞典南部的农村大气测量站的完整季节周期(2015年6月2015年6月)评估了聚体仪模型。通过利用紫外线和IR的吸收差异,聚体模型分配碳质量为木材燃烧(WB)和化石燃料燃烧(FF)气溶胶。在该研究中,模型中的微小修改与来自热光学分析的碳测量相结合允许分配的非光吸收的生物原味气溶胶随时间变化。 WB和FF之间的吸收差异可以通过吸收Δngstrαm指数(aae)量化。在本研究中,AAEWB设定为1.81和AAEFF至1.0。我们的观察结果表明,与夏季(1.12?±0.07)相比,冬季(1.36?±0.07)升高了AAE升高定量的WB气溶胶与左葡聚糖浓度良好,无论是相关性吗(R2?= 0.70),也与参考发射库存相比。 WB气溶胶在冬季(0.65Ωμg≤M≤3,56Ω·3,56Ω·3,56Ω%)和夏季的低浓度(0.07ΩΩm≤3,6?%总碳的浓度)和低浓度的季节性变化强。 FF气溶胶显示出较少的季节性依赖;然而,黑碳(BC)FF显示出对应于交通高峰时段峰值的明显昼夜图案。在夏季(1.04Ωμg≤M≤3,72Ω·3,72Ω·3,72Ω)和低温(0.13ΩΩm≤3,8≤8,总碳的含量)的假版(1.04ΩΩ·m≤3,72Ω·百分之) )。与含吡烃和左葡聚糖源分配结果相比,进一步的聚体仪表模型结果。比较表明,分配的WB和生物碳质气溶胶良好的吻合良好,但发现FF气溶胶质量差异差异。与无线碳和左葡葡聚糖源分配相比,聚体仪表模型将FF气溶胶质量估量为1.3倍。进行的敏感性分析表明,这种差异可以通过在冬季干扰非光吸收的生物碳而解释。总之,与无线电金和左葡葡聚糖替代方案相比,聚体仪表模型在农村背景站提供了一种经济效益但坚固的高度分辨率源分摊。

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