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. 2025 Aug 16;9(8):e2025GH001423.
doi: 10.1029/2025GH001423. eCollection 2025 Aug.

Physics-Based Spatial Oversampling of TROPOMI NO2 Observations to US Neighborhoods Reveals the Disparities of Air Pollution

Affiliations

Physics-Based Spatial Oversampling of TROPOMI NO2 Observations to US Neighborhoods Reveals the Disparities of Air Pollution

Xiaomeng Jin et al. Geohealth. .

Abstract

Satellite observations provide continuous and global coverage observations of air pollutants, widely used to inform health impacts and air pollution disparities. Linking satellite retrievals with socioeconomic or health data involves matching the irregularly shaped satellite observations with administrative units. Here, we develop a physics-based approach to spatially oversample nitrogen dioxide (NO2) retrievals from TROPOspheric Monitoring Instrument (TROPOMI) directly to United States (US) neighborhoods (i.e., block groups). The physics-based oversampling approach considers each satellite pixel as a sensitivity distribution, meaning that satellite instruments are more sensitive to the neighborhoods at the center than at the edge of the observations. We show that directly oversampling satellite observations to administrative shapes is a more accurate and computationally efficient approach than the commonly used gridding approaches, and it is advantageous for shorter temporal windows. Combining the newly developed NO2 data set with demographic data, we find widespread racial/ethnic and income-related NO2 disparities across the US. NO2 disparities are even more pronounced during the most polluted days, suggesting greater acute health effects for overburdened communities. We expect that the resolution-adaptive, neighborhood-level, and GIS-compatible NO2 data set would lower barriers of the public to access and interpret satellite observations, facilitating the actionable applications of satellite observations.

Keywords: NO2; TROPOMI; air pollution disparity; environmental justice; remote sensing; spatial oversampling.

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Conflict of interest statement

The authors declare no conflicts of interest relevant to this study.

Figures

Figure 1
Figure 1
(a) Illustration of the 2‐D Gaussian spatial response function of a single satellite observation overlaid with the administrative boundaries of 10 block groups in the satellite field of view. The response function is projected to the Cartesian space and normalized by the sum. (b) Comparison of the weight assigned to each block group (labeled in a) based on overlap areas (AWO‐BG) or the Gaussian weight (PGO‐BG). The area is normalized by the area of the satellite pixel polygon.
Figure 2
Figure 2
Map of 5‐year average (2019–2023) NO2 at block group level over contiguous United States with zoom‐in maps of NO2 for 10 CBSAs with the highest level of NO2. The block‐group NO2 is calculated using PGO‐BG approach. Block groups where NO2 exceeds top 10% national level (>5.5 × 1015 molecules/cm2) are aggregated and outlined in black. The numbers in the zoomed‐in maps represent the mean NO2 column density (in unit of 1015 molecules/cm2), with the values in brackets indicating the minimum and maximum within each core‐based statistical areas.
Figure 3
Figure 3
Maps of block‐group level TROPOspheric Monitoring Instrument NO2 for New York City based on 5‐year average (upper panel) and top 5% polluted days (bottom panel) using three oversampling methods: (a) Physics‐based Gaussian oversampling to block groups (PGO‐BG); (b) area weighted average oversampling to block groups (AWO‐BG); (c) area weighted average method oversampling to a regular grid of 0.01° × 0.01° (AWO‐Grid).
Figure 4
Figure 4
Maps of NO2 disparities related to (a) race/ethnicity and (b) income over all CBSAs of contiguous United States derived from block‐group TROPOspheric Monitoring Instrument NO2 oversampled with PGO‐BG approach. The racial/ethnic disparity is defined as the relative difference in population‐weighted average NO2 between white non‐Hispanic and minority groups (including Hispanic, non‐Hispanic Black, Asian, and native American), and the income‐related disparity is defined as the relative difference in population‐weighted average NO2 between the groups with ratio of income to poverty level below 1.24 (hereafter low‐income groups) and the groups with the ratio above 1.5 (hereafter high‐income groups). The left panel shows the top 20 CBSAs with the largest NO2 disparity, with numbers on the map indicating their rank. The results using the other two oversampling approaches can be found in Supporting Information S1.
Figure 5
Figure 5
(a) Difference in the racial/ethnic NO2 disparities between the top 5% polluted days and the 5‐year mean. (b) Comparison of the racial/ethnic NO2 disparities on the top 5% polluted days versus the 5‐year mean NO2 in selected CBSAs. NO2 data are oversampled with the PGO‐BG approach. The top 5% days are selected based on the daily mean TROPOMI NO2 at each core‐based statistical areas. The CBSAs are ranked by the 5‐year mean NO2 level with Los Angeles being the highest. The results using the other two oversampling approaches can be found in Supporting Information S1.
Figure 6
Figure 6
Normalized spatial gradient of NO2 in selected CBSAs: (a) New York; (b) Miami; (c) St. Louis; (d) Los Angeles and (e) Denver based on 5‐year average (top panel) versus top 5% polluted days (middle panel), calculated as the block‐group NO2 divided by the maximum NO2, using the PGO‐BG approach to oversample NO2. The bottom panel shows the percentage of white non‐Hispanic population. The extent of each map is defined based on the full extent of the corresponding core‐based statistical areas, which include the city labeled and the surrounding areas.

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