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Amines in boreal forest air at SMEAR II station in Finland

机译:在芬兰的涂抹II站的Boreal Forest Air中的胺

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We measured amines in boreal forest air in Finland both in gas and particle phases with 1h time resolution using an online ion chromatograph (instrument for Measuring AeRosols and Gases in Ambient Air – MARGA) connected to an electrospray ionization quadrupole mass spectrometer (MS). The developed MARGA-MS method was able to separate and detect seven different amines: monomethylamine (MMA), dimethylamine (DMA), trimethylamine (TMA), ethylamine (EA), diethylamine (DEA), propylamine (PA), and butylamine (BA). The detection limits of the method for amines were low (0.2–3.1ngm?3), the accuracy of IC-MS analysis was 11–37%, and the precision 10–15%. The proper measurements in the boreal forest covered about 8 weeks between March and December?2015. The amines were found to be an inhomogeneous group of compounds, showing different seasonal and diurnal variability. Total MMA (MMA(tot)) peaked together with the sum of ammonia and ammonium ions already in March. In March, monthly means for MMA were 2.4 and 6.8±9.1ngm?3 in gas and aerosol phases, respectively, and for NH3 and NH4+ these were 52±16 and 425±371ngm?3, respectively. Monthly medians in March for MMA(tot), NH3, and NH4+ were 2.4, 19 and 90ngm?3, respectively. DMA(tot) and TMA(tot) had summer maxima indicating biogenic sources. We observed diurnal variation for DMA(tot) but not for TMA(tot). The highest concentrations of these compounds were measured in July. Then, monthly means for DMA were 3.1 and 8.4±3.1ngm?3 in gas and aerosol phases, respectively, and for TMA these were 0.4±0.1 and 1.8±0.5ngm?3. Monthly medians in July for DMA were below the detection limit (DL) and 4.9ngm?3 in gas and aerosol phases, respectively, and for TMA these were 0.4 and 1.4ngm?3. When relative humidity of air was 90%, gas-phase DMA correlated well with 1.1–2nm particle number concentration (R2=0.63) suggesting that it participates in atmospheric clustering. EA concentrations were low all the time. Its July means were 0.36 and 0.4±0.4ngm?3 in gas and aerosol phases, respectively, but individual concentration data correlated well with monoterpene concentrations in July. Monthly means of PA and BA were below detection limits at all times.
机译:我们在芬兰的北方森林空气中测量芬兰的胺和颗粒阶段,使用在线离子色谱仪(用于测量气雾剂和环境空气 - Marga中的气体的仪器)连接到电喷雾电离四极杆质谱仪(MS)的仪器。开发的MARGA-MS方法能够分离和检测七种不同的胺:单甲胺(MMA),二甲胺(DMA),三甲胺(TMA),乙胺(EA),二乙胺(DEA),丙胺(PA)和丁胺(BA) )。胺的检测限率低(0.2-3.11Gm→3),IC-MS分析的精度为11-37%,精度10-15%。北方森林的适当测量约为3月至12月在2015年之间约8周。发现胺是一种不均匀的化合物组,显示出不同的季节性和昼夜变异性。总MMA(MMA(TOT))与3月份已经与氨和铵离子一起达到峰值。 3月份,MMA的月度手段分别为2.4和6.8±9.1GM?3分别在气溶胶阶段和NH 3和NH4 +中分别为52±16和425±371ng?3。 3月份MMA(TOT),NH3和NH4 +的月度中位数分别为2.4,19和90ngm?3。 DMA(TOT)和TMA(TOT)有夏季最大值,表明生物源。我们观察了DMA(Tot)的昼夜变化,但不适用于TMA(TOT)。 7月份测量了这些化合物的最高浓度。然后,DMA的每月手段分别为3.1和8.4±3.1ng,分别在气溶胶阶段和TMA中的3.4±0.1和1.8±0.5ngm?3。 7月份为DMA的月度中位数分别低于检测限(DL)和4.9ng)和4.9ng,分别在气溶胶阶段,并且对于TMA,这些是0.4和1.4ngm?3。当空气的相对湿度为90%时,气相DMA与1.1-2Nm颗粒数浓度(R2 = 0.63)相关,表明它参与大气聚类。 EA浓度一直都很低。其7月份分别为0.36和0.4±0.4ng?3,气体和气溶胶阶段分别为单选数据,7月份用单萜浓度良好地相关。 PA和BA的每月手段始终低于检测限。

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