Abstract

Abstract. Over the past 20 years, advances in satellite remote sensing of pollution-relevant species have made space-borne observations an increasingly important part of atmospheric chemistry research and air quality management. This progress has been facilitated by advanced UV–vis spectrometers, such as the Ozone Monitoring Instrument (OMI) on board the NASA Earth Observing System (EOS) Aura satellite, and continues with new instruments, such as the Ozone Mapping and Profiler Suite (OMPS) on board the NASA–NOAA Suomi National Polar-orbiting Partnership (SNPP) satellite. In this study, we demonstrate that it is possible, using our state-of-the-art principal component analysis (PCA) retrieval technique, to continue the long-term global SO2 pollution monitoring started by OMI with the current and future OMPS instruments that will fly on the NOAA Joint Polar Satellite System (JPSS) 1, 2, 3, and 4 satellites in addition to SNPP, with a very good consistency of retrievals from these instruments. Since OMI SO2 data have been primarily used for (1) providing regional context on air pollution and long-range transport on a daily basis and (2) providing information on point emission sources on an annual basis after data averaging, we focused on these two aspects in our OMI–OMPS comparisons. Four years of retrievals (2012–2015) have been compared for three regions: eastern China, Mexico, and South Africa. In general, the comparisons show relatively high correlations (r = 0. 79–0.96) of daily regional averaged SO2 mass between the two instruments and near-unity regression slopes (0.76–0.97). The annual averaged SO2 loading differences between OMI and OMPS are small (< 0.03 Dobson unit (DU) over South Africa and up to 0.1 DU over eastern China). We also found a very good correlation (r = 0. 92–0.97) in the spatial distribution of annual averaged SO2 between OMI and OMPS over the three regions during 2012–2015. The emissions from ∼ 400 SO2 sources calculated with the two instruments also show a very good correlation (r = ∼ 0.9) in each year during 2012–2015. OMPS-detected SO2 point source emissions are slightly lower than those from OMI, but OMI–OMPS differences decrease with increasing strength of source. The OMI–OMPS SO2 mass differences on a pixel by pixel (daily) basis in each region can show substantial differences. The two instruments have a spatial correlation coefficient of 0.7 or better on < ∼ 50 % of the days. It is worth noting that consistent SO2 retrievals were achieved without any explicit adjustments to OMI or OMPS radiance data and that the retrieval agreement may be further improved by introducing a more comprehensive Jacobian lookup table than is currently used.

Highlights

  • Sulfur dioxide (SO2) is an important pollutant gas that has significant impacts on the environment and climate at global, regional, and local scales

  • A principal component analysis (PCA) SO2 algorithm was developed and applied to Ozone Monitoring Instrument (OMI) (Li et al, 2013, 2017). This approach greatly reduces the noise and bias compared with the previous band residual difference (BRD) OMI SO2 algorithm (Krotkov et al, 2006), allows smaller sources to be detected from space (Fioletov et al, 2015, 2016; McLinden et al, 2016b), and enables trends to be studied for more regions

  • Taking advantage of the 4-year overlap between OMI and Ozone Mapping and Profiler Suite (OMPS) local afternoon measurements and applying the same PCA algorithm to retrieve SO2, we demonstrate that OMI and OMPS SO2 retrievals are highly consistent for the world’s most polluted regions from 2012 through 2015

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Summary

Introduction

Sulfur dioxide (SO2) is an important pollutant gas that has significant impacts on the environment and climate at global, regional, and local scales. A principal component analysis (PCA) SO2 algorithm was developed and applied to OMI (Li et al, 2013, 2017) This approach greatly reduces the noise and bias compared with the previous band residual difference (BRD) OMI SO2 algorithm (Krotkov et al, 2006), allows smaller sources to be detected from space (Fioletov et al, 2015, 2016; McLinden et al, 2016b), and enables trends to be studied for more regions. One of the strengths of the PCA technique is that it does not require instrument-specific, explicit corrections to satellite-measured radiance data This makes it relatively straightforward to adapt to other instruments and reduces the chance of introducing retrieval biases between different instruments. In this paper we apply the PCA technique to OMPS measurements (2012–2015) to examine the feasibility of continuing the OMI anthropogenic SO2 dataset with OMPS

OMI and OMPS SO2 data
OMPS SO2 data
OMI and OMPS data filtering and gridding
Emission from OMI and OMPS
OMI and OMPS SO2 spatial and temporal comparison
Regional daily SO2
Instrument performance and trends
Findings
Conclusions
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