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Eight years of sub-micrometre organic aerosol composition data from the boreal forest characterized using a machine-learning approach

机译:八年的亚微米有机气溶胶组成数据来自北方森林,以机器学习方法为特征

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The Station for Measuring Ecosystem–Atmosphere Relations (SMEAR) II, located within the boreal forest of Finland, is a unique station in the world due to the wide range of long-term measurements tracking the Earth–atmosphere interface. In this study, we characterize the composition of organic aerosol (OA) at SMEAR II by quantifying its driving constituents. We utilize a multi-year data set of OA mass spectra measured in situ with an Aerosol Chemical Speciation Monitor (ACSM) at the station. To our knowledge, this mass spectral time series is the longest of its kind published to date. Similarly to other previously reported efforts in OA source apportionment from multi-seasonal or multi-annual data sets, we approached the OA characterization challenge through positive matrix factorization (PMF) using a rolling window approach. However, the existing methods for extracting minor OA components were found to be insufficient for our rather remote site. To overcome this issue, we tested a new statistical analysis framework. This included unsupervised feature extraction and classification stages to explore a large number of unconstrained PMF runs conducted on the measured OA mass spectra. Anchored by these results, we finally constructed a relaxed chemical mass balance (CMB) run that resolved different OA components from our observations. The presented combination of statistical tools provided a data-driven analysis methodology, which in our case achieved robust solutions with minimal subjectivity. Following the extensive statistical analyses, we were able to divide the 2012–2019 SMEAR II OA data (mass concentration interquartile range (IQR): 0.7, 1.3, and 2.6? μ g?m ?3 ) into three sub-categories – low-volatility oxygenated OA (LV-OOA), semi-volatile oxygenated OA (SV-OOA), and primary OA (POA) – proving that the tested methodology was able to provide results consistent with literature. LV-OOA was the most dominant OA type (organic mass fraction IQR: 49?%, 62?%, and 73?%). The seasonal cycle of LV-OOA was bimodal, with peaks both in summer and in February. We associated the wintertime LV-OOA with anthropogenic sources and assumed biogenic influence in LV-OOA formation in summer. Through a brief trajectory analysis, we estimated summertime natural LV-OOA formation of tens of ng?m ?3 ?h ?1 over the boreal forest. SV-OOA was the second highest contributor to OA mass (organic mass fraction IQR: 19?%, 31?%, and 43?%). Due to SV-OOA's clear peak in summer, we estimate biogenic processes as the main drivers in its formation. Unlike for LV-OOA, the highest SV-OOA concentrations were detected in stable summertime nocturnal surface layers. Two nearby sawmills also played a significant role in SV-OOA production as also exemplified by previous studies at SMEAR II. POA, taken as a mix of two different OA types reported previously, hydrocarbon-like OA (HOA) and biomass burning OA (BBOA), made up a minimal OA mass fraction (IQR: 2?%, 6?%, and 13?%). Notably, the quantification of POA at SMEAR II using ACSM data was not possible following existing rolling PMF methodologies. Both POA organic mass fraction and mass concentration peaked in winter. Its appearance at SMEAR II was linked to strong southerly winds. Similar wind direction and speed dependence was not observed among other OA types. The high wind speeds probably enabled the POA transport to SMEAR II from faraway sources in a relatively fresh state. In the event of slower wind speeds, POA likely evaporated and/or aged into oxidized organic aerosol before detection. The POA organic mass fraction was significantly lower than reported by aerosol mass spectrometer (AMS) measurements 2?to 4?years prior to the ACSM measurements. While the co-located long-term measurements of black carbon supported the hypothesis of higher POA loadings prior to year 2012, it is also possible that short-term (POA) pollution plumes were averaged out due to the slow time resolution of the ACSM combined with the further 3?h data averaging needed to ensure good signal-to-noise ratios (SNRs). Despite the length of the ACSM data set, we did not focus on quantifying long-term trends of POA (nor other components) due to the high sensitivity of OA composition to meteorological anomalies, the occurrence of which is likely not normally distributed over the 8-year measurement period. Due to the unique and realistic seasonal cycles and meteorology dependences of the independent OA subtypes complemented by the reasonably low degree of unexplained OA variability, we believe that the presented data analysis approach performs well. Therefore, we hope that these results encourage also other researchers possessing several-year-long time series of similar data to tackle the data analysis via similar semi- or unsupervised machine-learning approaches. This way the presented method could be further optimized and its usability explored and evaluated also in other environments.
机译:衡量生态系统 - 大气关系(SMEAR)II,位于芬兰的北方林林内,是世界上独特的车站,由于追踪地球大气界面的广泛的长期测量。在该研究中,我们通过量化其驱动成分来表征涂片II的有机气溶胶(OA)的组成。我们利用驻地原位测量的多年数据集OA质谱。为了我们的知识,这种质量谱时间序列是迄今为止最长的。类似于以前先前报告的OA源分配来自多季节或多年度数据集的努力,我们使用滚动窗口方法通过正矩阵分解(PMF)接近OA表征挑战。但是,发现了用于提取次要OA组件的现有方法对于我们的偏远地点不足。为了克服这个问题,我们测试了一个新的统计分析框架。这包括无监督的特征提取和分类阶段,以探索在测量的OA质谱上进行的大量无约束PMF运行。通过这些结果锚定,我们终于构建了一个缓解的化学质量平衡(CMB),从我们的观察结果中解析了不同的OA组件。统计工具的组合提供了一种数据驱动的分析方法,在我们的案例中实现了具有最小主观性的强大解决方案。在广泛的统计分析之后,我们能够将2012-2019污迹II OA数据分为三个子类别 - 低 - 挥发性氧化OA(LV-OOA),半挥发性含氧OA(SV-OOA)和初级OA(POA) - 证明测试方法能够提供与文学一致的结果。 LV-OOA是最占优势的OA型(有机质量分数IQR:49?%,62倍,73?%)。 LV-OOA的季节性循环是双峰,夏季和2月份的峰值。我们将冬季冬季含量与人为源源相关,并在夏季综合影响LV-OOA形成生物影响。通过简短的轨迹分析,我们估计夏季天然LV-OOA形成数十的造成的数量,在北方森林中的3?H?1。 SV-OOA是OA质量的第二高的贡献者(有机质量分数IQR:19?%,31μl和43μl%)。由于SV-OOA在夏天的透明高峰,我们估计生物过程作为其形成中的主要司机。与LV-OOA不同,在稳定的夏季夜间表面层中检测到最高的SV-OOA浓度。附近的两个锯木厂在SV-OOA生产中也发挥了重要作用,也可以通过以前的涂抹II的研究表明。 Poa作为先前报道的两种不同OA类型的混合物,烃类OA(HOA)和生物质燃烧OA(BboA),由最小的OA质量分数(IQR:2?%,6〜%和13个? %)。值得注意的是,在现有的滚动PMF方法中不可能使用ACSM数据来定量使用ACSM数据的POA。 POA有机质量分数和冬季峰值达到的质量浓度。它在涂抹II时的外观与强大的南风有关。在其他OA类型中没有观察到类似的风向和速度依赖性。高风速可能使POA运输能够以相对新鲜状态从遥远的源涂抹。在风速较慢的情况下,POA可能在检测前蒸发和/或在氧化有机气溶胶中蒸发。 POA有机质量分数明显低于气溶胶质谱仪(AMS)测量2的报告2?在ACSM测量前4年。虽然在2012年之前的黑碳的共同定位的长期测量支持的黑碳的假设中,但由于ACSM的缓慢时间分辨率,也可以平均短期(POA)污染羽毛使用进一步的3?H数据平均,以确保良好的信噪比(SNR)。尽管ACSM数据集的长度,但我们没有专注于量化POA(也不是其他组分)的长期趋势,因为OA组合物对气象异常的高灵敏度,其发生可能通常不会分布在8中 - 年测量期。由于独特逼真的季节性周期和气象依赖性的独立OA亚型,通过合理低的未解释的OA变异性,我们认为,所提出的数据分析方法表现良好。因此,我们希望这些结果还鼓励其他研究人员拥有几年长时间的类似数据,以通过类似的半或无监督的机器学习方法解决数据分析。这样,就可以进一步优化所呈现的方法,并且其可用性也在其他环境中探索和评估。

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