Non-Stationarity of Aerosol Extinction Coefficient per Unit of Mass in Autumn and Winter in Chengdu, China

Based on hourly observation data from the aethalometer and GRIMM180 environment particle monitor as well as the simultaneous data of visibility (V), relative humidity (RH) and nitrogen dioxide (NO<sub>2</sub>) from October to December in 2017 in Chengdu, the corresponding time series of...

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Bibliographic Details
Main Authors: Meng Yang, Changjian Ni, Yinshan Yang, Jin Fan
Format: Article
Language:English
Published: MDPI AG 2022-07-01
Series:Atmosphere
Subjects:
Online Access:https://www.mdpi.com/2073-4433/13/7/1064
Description
Summary:Based on hourly observation data from the aethalometer and GRIMM180 environment particle monitor as well as the simultaneous data of visibility (V), relative humidity (RH) and nitrogen dioxide (NO<sub>2</sub>) from October to December in 2017 in Chengdu, the corresponding time series of aerosol extinction coefficient per unit of mass is retrieved. The generalized additive models (GAMs) are adopted to analyze the non-stationarity of the time series of aerosol extinction coefficient per unit of mass and to explore the responses of the aerosol extinction coefficient per unit of mass to the aerosol component structure factors (<i>ρ</i><sub>BC</sub>/<i>ρ</i><sub>PM10</sub>, <i>ρ</i><sub>PM1</sub>/<i>ρ</i><sub>PM2.5</sub>, <i>ρ</i><sub>PM1~2.5</sub>/<i>ρ</i><sub>PM2.5</sub> and <i>ρ</i><sub>PM2.5</sub>/<i>ρ</i><sub>PM10</sub>; <i>ρ</i> represents particle mass concentration) and RH. The results show that through the comparative analysis of stationary and non-stationary models, the time series of aerosol extinction coefficient per unit of mass in autumn and winter in Chengdu is non-stationary. In addition, the RH and aerosol component structure factors are all significant nonlinear covariates that affect the non-stationarity of the aerosol extinction coefficient per unit of mass. According to the influence of covariates, the sequence is as follows: RH > <i>ρ</i><sub>BC</sub>/<i>ρ</i><sub>PM10</sub> > <i>ρ</i><sub>PM2.5</sub>/<i>ρ</i><sub>PM10</sub> > <i>ρ</i><sub>PM1</sub>/<i>ρ</i><sub>PM2.5</sub>. At PM<sub>2.5</sub> pollution concentration (<i>ρ</i><sub>PM2.5</sub> > 75 μg m<sup>−3</sup>), according to the influence of covariates, the sequence is as follows: RH > <i>ρ</i><sub>PM1~2.5</sub>/<i>ρ</i><sub>PM2.5</sub> > <i>ρ</i><sub>BC</sub>/<i>ρ</i><sub>PM10</sub> > <i>ρ</i><sub>PM2.5</sub>/<i>ρ</i><sub>PM10</sub>. Moreover, the interaction between RH and aerosol component structure factors significantly affects the aerosol extinction coefficient per unit of mass. The condition of high RH, high <i>ρ</i><sub>PM2.5</sub>/<i>ρ</i><sub>PM10</sub>, high <i>ρ</i><sub>PM1</sub>/<i>ρ</i><sub>PM2.5</sub> and low <i>ρ</i><sub>BC</sub>/<i>ρ</i><sub>PM10</sub> has a synergistic amplification effect on the increase of the aerosol extinction coefficient per unit of mass. At PM<sub>2.5</sub> pollution concentration, the synergistic effect of high RH, high <i>ρ</i><sub>PM2.5</sub>/<i>ρ</i><sub>PM10</sub>, high <i>ρ</i><sub>PM1~2.5</sub>/<i>ρ</i><sub>PM2.5</sub> and low <i>ρ</i><sub>BC</sub>/<i>ρ</i><sub>PM10</sub> is beneficial to the increase of the aerosol extinction coefficient per unit of mass.
ISSN:2073-4433