Centre for Environmental Science and Engineering, Department of Civil Engineering, Indian Institute of Technology Kanpur, Kanpur 208016, India.
Environ Sci Pollut Res Int. 2012 May;19(4):1187-97. doi: 10.1007/s11356-011-0635-9. Epub 2011 Oct 20.
The kinetics of the transformation of ammonia and acid gases into components of PM(2.5) has been examined. The interactions of existing aerosols and meteorology with the transformation mechanism have also been investigated. The specific objective was to discern the kinetics for the gas-to-particle conversion processes where the reactions of NH(3) with H(2)SO(4), HNO(3), and HCl take place to form (NH(4))(2)SO(4), NH(4)NO(3), and NH(4)Cl, respectively, in PM(2.5).
A Teflon-based outdoor environmental chamber facility (volume of 12.5 m(3)) with state-of-the-art instrumentation to monitor the concentration-time profiles of precursor gases, ozone, and aerosol and meteorological parameters was built to simulate photochemical reactions.
The reaction rate constants of NH(3) with H(2)SO(4), HNO(3), and HCl (i.e., k (S), k (N), and k (Cl)) were estimated as (1) k (S) = 2.68 × 10(-4) (±1.38 × 10(-4)) m(3)/μmol/s, (2) k (N) = 1.59 × 10(-4) (±8.97 × 10(-5)) m(3)/μmol/s, and (3) k (Cl) = 5.16 × 10(-5) (±3.50 × 10(-5)) m(3)/μmol/s. The rate constants k (S) and k (N) showed significant day-night variations, whereas k (Cl) did not show any significant variation. The D/N (i.e., daytime/nighttime values) ratio was 1.3 for k (S) and 0.33 for k (N). The significant role of temperature, solar radiation, and O(3) concentration in the formation of (NH(4))(2)SO(4) was recognized from the correlation analysis of k (S) with these factors. The negative correlations of temperature with k (N) and k (Cl) indicate that the reactions for the formation of NH(4)NO(3) and NH(4)Cl seem to be reversible under higher temperature due to their semivolatile nature. It was observed that the rate constants (k (S), k (N), and k (Cl)) showed a positive correlation with the initial PM(2.5) levels in the chamber, suggesting that the existing surface of the aerosol could play a significant role in the formation of (NH(4))(2)SO(4), NH(4)NO(3), and NH(4)Cl.
Therefore, this study recommends an intelligent control of primary aerosols and precursor gases (NO( x ), SO(2), and NH(3)) for achieving reduction in PM(2.5) levels.
研究了氨和酸性气体转化为 PM(2.5) 成分的动力学。还研究了现有气溶胶和气象条件与转化机制的相互作用。具体目标是辨别气体到颗粒的转化过程的动力学,其中 NH(3)与 H(2)SO(4)、HNO(3)和 HCl 的反应分别形成(NH(4))(2)SO(4)、NH(4)NO(3)和 NH(4)Cl 在 PM(2.5)中。
建立了一个基于 Teflon 的户外环境室设施(体积为 12.5 m(3)),配备了先进的仪器,可监测前体气体、臭氧和气溶胶的浓度-时间曲线以及气象参数,以模拟光化学反应。
NH(3)与 H(2)SO(4)、HNO(3)和 HCl 的反应速率常数(即 k (S)、k (N)和 k (Cl)) 分别估计为 (1) k (S) = 2.68 × 10(-4) (±1.38 × 10(-4)) m(3)/μmol/s,(2) k (N) = 1.59 × 10(-4) (±8.97 × 10(-5)) m(3)/μmol/s,和 (3) k (Cl) = 5.16 × 10(-5) (±3.50 × 10(-5)) m(3)/μmol/s。k (S)和 k (N)的速率常数表现出显著的昼夜变化,而 k (Cl)没有表现出任何显著变化。D/N(即白天/夜间值)比值为 1.3 对于 k (S)和 0.33 对于 k (N)。通过与这些因素的相关性分析,认识到温度、太阳辐射和 O(3)浓度在(NH(4))(2)SO(4)形成中的重要作用。由于其半挥发性,温度与 k (N)和 k (Cl)的负相关表明,NH(4)NO(3)和 NH(4)Cl 的形成反应似乎在较高温度下是可逆的。观察到速率常数(k (S)、k (N)和 k (Cl))与室内初始 PM(2.5)水平呈正相关,表明气溶胶的现有表面可能在(NH(4))(2)SO(4)、NH(4)NO(3)和 NH(4)Cl 的形成中发挥重要作用。
因此,本研究建议对初级气溶胶和前体气体(NO(x)、SO(2)和 NH(3))进行智能控制,以实现 PM(2.5)水平的降低。