日本秋田地区颗粒氮化合物及其气态前体中稳定氮同位素比值的季节变化趋势

H. Kawashima
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引用次数: 12

摘要

摘要:颗粒物(PM)对人体健康有不良影响。此外,由于PM在大气中的形成和行为机制非常复杂,为了有效降低PM浓度并达到环境标准,必须清楚地了解源-受体关系。稳定同位素比值可用于检测化学过程和区分来源。在环境科学中,特别是在气溶胶研究中,稳定同位素比率已被证明是鉴别来源的有力工具。然而,对二次气溶胶形成过程中同位素分馏的长期研究很少。本研究分析了日本秋田地区悬浮PM (SPM)中氨气(NH3)、二氧化氮(NO2)、硝酸蒸汽(HNO3)、硝态颗粒(NO3−)和铵态铵(NH4+)的稳定氮同位素比值(δ15N),探讨了气溶胶形成过程中的季节变化趋势和同位素分异。结果表明:SPM和δ15N-NH3气体δ15N-NH4+含量变化范围分别为1.3‰~ 38.5‰(平均16.1‰)和- 33.6‰~ - 0.0‰(- 16.9‰);δ15N-NO3−(SPM)、δ15N-NO2和δ15N-HNO3(气态)的变化范围分别为- 4.6‰~ 4.8‰(平均- 0.5‰)、- 8.2‰~ - 3.1‰(平均- 5.4‰)和- 7.5‰~ 2.7‰(平均- 5.0‰)。SPM中气态NH3转化为NH4+、气态NO2转化为气态HNO3、HNO3气体转化为NO3 -的年平均同位素分馏因子分别为+33.3‰、+0.5‰和+4.9‰。SPM中NH4+的同位素分馏率远高于NO3 -。随着气态前驱体化学反应的进行,SPM中的δ15N-NO3 -逐渐变重。
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Seasonal trends of the stable nitrogen isotope ratio in particulate nitrogen compounds and their gaseous precursors in Akita, Japan
Abstract Particulate matter (PM) can have adverse effects on human health. Moreover, because the mechanisms of PM formation and behavior in the atmosphere are notably complicated, to reduce PM concentrations effectively and meet environmental standards, source–receptor relationships must be clearly understood. Stable isotope ratios can be used to detect chemical processes and distinguish sources. In environmental science, especially in research on aerosols, stable isotope ratios have proven to constitute a powerful tool for source identification. However, there are few long-term studies of isotope fractionation during secondary aerosol formation. In this study, stable nitrogen isotope ratios (δ15N) of ammonia gas (NH3), nitrogen dioxide gas (NO2), nitric acid vapor (HNO3), particulate nitrate (NO3−), and ammonium (NH4+) in suspended PM (SPM) were analyzed to investigate seasonal trends and isotope fractionation during aerosol formation for long term sampling in Akita, Japan. The results indicated that δ15N-NH4+ in SPM and δ15N-NH3 gas ranged from 1.3‰ to 38.5‰ (mean 16.1‰) and from −33.6‰ to −0.0‰ (−16.9‰), respectively. Furthermore, δ15N-NO3− (SPM) and δ15N-NO2 and δ15N-HNO3 (gaseous) ranged from −4.6‰ to 4.8‰ (mean −0.5‰), from −8.2‰ to −3.1‰ (−5.4‰), and from −7.5‰ to 2.7‰ (−5.0‰), respectively. The mean annual isotope fractionation factors for transformations from gaseous NH3 to NH4+ in SPM, from gaseous NO2 to gaseous HNO3, and from HNO3 gas to NO3– in SPM in the atmospheric environment were +33.3‰, +0.5‰, and +4.9‰, respectively. Isotope fractionation of NH4+ in SPM was much higher than that of NO3– in SPM. As the chemical reaction from gaseous precursors progressed, δ15N-NO3– in SPM became steadily heavier.
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