Abstract

Fine particulate matter (PM2.5) has a considerable impact on the environment, climate change, and human health. Herein, we introduce a deep neural network model for deriving ground-level, hourly PM2.5 concentrations by Himawari-8 aerosol optical depth, meteorological variables, and land cover information. A total of 151,726 records were collected from 313 ground-level PM2.5 monitoring stations (spread across the North China Plain) to calibrate and test the proposed model. The sample- and site-based cross-validation yielded satisfactory performance, with correlation coefficients > 0.8 (R = 0.86 and 0.83, respectively). Furthermore, the variation in mean ground-level hourly PM2.5 concentrations, using 2017 data, showed that the proposed method could be applied for spatiotemporal continuous PM2.5 monitoring. This study will serve as a reference for the application of geostationary meteorological satellite to perform ground-level PM2.5 estimation and the utilization in atmospheric monitoring.

Highlights

  • Fine particulate matter (PM2.5), which consists of particles with aerodynamic diameters \ 2.5 lm, has attracted considerable scientific attention (Pope & Dockery, 2006)

  • A total of 151,726 records were collected from 313 ground-level PM2.5 monitoring stations to calibrate and test the proposed model

  • The variation in mean ground-level hourly PM2.5 concentrations, using 2017 data, showed that the proposed method could be applied for spatiotemporal continuous PM2.5 monitoring

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Summary

Introduction

Fine particulate matter (PM2.5), which consists of particles with aerodynamic diameters \ 2.5 lm, has attracted considerable scientific attention (Pope & Dockery, 2006). Several studies were conducted for estimating PM2.5 concentrations from the aerosol optical depth (AOD), derived by satellite remote sensing, including multiple linear regression (Chu et al, 2016; Gupta & Christopher, 2008, 2009; Kacenelenbogen et al, 2006; Liu et al, 2005; Paciorek et al, 2008; Schaap et al, 2009; Wang, 2003; Yao et al 2018), mixed-effect models (Just et al 2015; Kloog et al 2011, 2012, 2014; Lee et al 2012; Zheng et al 2016), geographically weighted regressions (Bai et al, 2016; Guo et al, 2017; He & Huang, 2018a, b; Hu, 2009; Ma et al, 2014; You et al, 2015; Zou et al, 2016), and chemical transport models (Crouse et al., Journal of the Indian Society of Remote Sensing (August 2021) 49(8):1839–1852. Random forests (Chen et al, 2018; Hu et al, 2017), deep belief networks (DBNs) (Li et al, 2018; Liu et al, 2018), deep neural networks (DNNs) (Wang & Sun, 2019), and machine learning models with high-dimensional expansion (Xue et al, 2019) have been used, and they have delivered superior prediction accuracy and applicability

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