Vegetation fires can have a very large impact not only on ecosystems but also on atmospheric composition and therefore on air quality (e.g., Voulgarakis & Field, 2015) with associated adverse consequences on health (Grant & Runkle, 2022). Fires directly emit large amounts of aerosols and gases, including carbon dioxide (CO 2 ), carbon monoxide (CO), nitrogen oxides (NO x ), volatile organic compounds (VOCs) and many other species. Subsequently, photochemical processing of these emissions often leads to enhanced levels of ozone and secondary organic aerosols (SOAs) (Majdi et al., 2019;Palm et al., 2020), thereby affecting the global radiative balance (Chang et al., 2021;Jiang et al., 2016). This environmental issue is becoming more acute as the intensity and frequency of wildfires are increasing due to hotter and drier conditions (di Virgilio et al., 2019;Pausas & Keeley, 2021;Senande-Rivera et al., 2022;Xu et al., 2020). Furthermore, the large number of megafires injecting material in the upper layers of the atmosphere raises concerns on their impact on the stratospheric composition and the ozone layer in particular (Das et al., 2021;Schwartz et al., 2020;Solomon et al., 2022).Satellite measurements provide invaluable information on the global distribution of atmospheric trace gases and aerosols on a daily basis. Therefore, they are well-suited to characterize the spatial and temporal evolution of biomass burning plumes. In this context, the Tropospheric Monitoring Instrument (TROPOMI) in operation since October 2017 on board of the Sentinel-5 precursor platform (Veefkind et al., 2012) is of particular interest as it allows measuring column densities of a suite of key trace gases present during fire events, such as nitrogen dioxide (NO 2 ), carbon monoxide (CO), nitrous acid (HONO), formaldehyde (HCHO), glyoxal (CHOCHO), in addition to the absorbing aerosol index (AAI) (e.g.,