the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Large and increasing stratospheric contribution to tropospheric ozone over East Asia
Daniel J. Jacob
Xingpei Ye
Robert M. Yantosca
Kelvin H. Bates
Drew C. Pendergrass
Laura Hyesung Yang
Hong Liao
Severe surface ozone pollution in South Korea and China in May–June is due in part to an elevated background subsiding from the free troposphere (750–350 hPa). Using IAGOS commercial aircraft observations and the GEOS-Chem model, we show that free tropospheric ozone over East Asia in May–June is the highest in the world and has increased from 68 ± 3 ppb (mean and interannual standard deviation) in 2000–2004 to 78 ± 4 ppb in 2015–2019. Free tropospheric ozone over East Asia is highest when carbon monoxide (CO) is low, both in the observations and GEOS-Chem, implying a large stratospheric influence on ozone. We find from GEOS-Chem that East Asia is a global hotspot for stratospheric downwelling of ozone and that this makes a major contribution to the free tropospheric ozone over the region in May–June. Stratospheric downwelling of ozone over East Asia in GEOS-Chem increased by 40 % from 2000–2004 to 2015–2019, which can explain the observed free tropospheric ozone increase over this period. Increased stratospheric downwelling over East Asia appears to be driven by a strengthening of the jet stream. The large and increasing stratospheric contribution to the surface ozone background over East Asia is a major impediment to meeting ozone air quality standards.
- Article
(3458 KB) - Full-text XML
-
Supplement
(625 KB) - BibTeX
- EndNote
Surface ozone concentrations in China and South Korea are among the highest in the world and have risen over the past two decades (Fleming et al., 2018; Lu et al., 2018b; Wang et al., 2022b; Kim et al., 2023). Stringent emission control policies in both countries have succeeded in decreasing fine particulate matter concentrations (PM2.5) (Bae et al., 2021; Pendergrass et al., 2022; Lee et al., 2024) but not surface ozone, which routinely exceeds national air quality standards (80 ppb in China, 60 ppb in South Korea). Understanding the role of both regional emissions and background influences on surface ozone in East Asia is critical for developing adequate emission control strategies to improve air quality.
Background surface ozone for a given region is commonly defined as the ozone that would be present in the absence of anthropogenic emissions in that region. A major contribution is subsidence from the free troposphere, which caps the planetary boundary layer (PBL) at about 2 km altitude. Surface ozone in South Korea and much of China is highest in May–June (Lu et al., 2019; Oak et al., 2025). The KORUS-AQ aircraft campaign in May–June 2016 found free tropospheric ozone concentrations averaging in excess of 80 ppb over and around the Korean peninsula (Miyazaki et al., 2019; Sullivan et al., 2019, Gaubert et al., 2020; Crawford et al., 2021; Park et al., 2021). A model study by Colombi et al. (2023) found that subsidence of this elevated free tropospheric ozone drove surface background ozone in East Asia in May to exceed 50 ppb, considerably higher than the 20–40 ppb background values in North America and Europe (Fiore et al., 2003; Zhang et al., 2011; Emery et al., 2012; Jaffe et al., 2018). Ozonesondes and commercial aircraft observations also show a maximum of free tropospheric ozone over East Asia in late spring (Chen et al., 2023), particularly in May–June, that has been increasing in the last two decades (Wang et al., 2022a). This elevated background could reflect influences from the stratosphere (Ma et al., 2025; Hong et al., 2024; Luo et al., 2024), lightning (Murray, 2016; Ye et al., 2024), and pollution originating outside East Asia (Han et al., 2019; Chen et al., 2023).
Here we aim to understand the sources driving the seasonality and long-term (2000–2019) change in free tropospheric ozone over East Asia, and the implication for surface ozone concentrations. We examine seasonality and change over time of the ozone vertical distribution, putting it into context of other northern midlatitude regions. We use the relationship between ozone and carbon monoxide (CO) to separate anthropogenic and natural contributions to free tropospheric ozone. Finally, we use the GEOS-Chem global 3-D chemical transport model to attribute the sources of free tropospheric ozone and the increasing trend.
We use ozone profile data from the In-Service Aircraft for a Global Observing System (IAGOS, https://iagos.aeris-data.fr/, last access: 12 January 2025) (Petzold et al., 2015) to compare the free tropospheric ozone seasonality and trends over three northern mid-latitude regions: East Asia (30.0 to 45.0° N, 109.0 to 145.0° E), Europe (35.0 to 54.0° N, −11.0 to 30.0° E), and the United States (28.0 to 49.0° N, −124.6 to −66.8° E). The IAGOS measurements are made using a dual-beam ultraviolet absorption photometer, with an accuracy of ± 2 ppbv (Blot et al., 2021; Nédélec et al., 2015). Following the approach of Shah et al. (2024), only vertical profile observations during ascent and descent are included, and profiles are averaged into 25 hPa vertical bins. To ensure statistical robustness, we require a minimum of two profiles per month and at least eight months of valid observations at each site during the study period before aggregating to monthly means. These criteria reduce potential biases from irregular flight sampling and follow established IAGOS usage practices.
Figure 1 shows the mean ozone mixing ratio profiles for the three regions for 2000–2004 and 2015–2019 in March–April, May–June, and July–August. The numbers inset are mean column mixing ratios and standard deviations for the free tropospheric column, which we define here and elsewhere as the pressure range 750–350 hPa. While Europe and the United States show negligible change in the free troposphere over the period, East Asia shows an increase peaking in May–June. The May–June increase of 10.5 ppb (67.8 ± 2.8 to 78.3 ± 4.0 ppb) is larger than the interannual standard deviation, indicating that the observed enhancement is robust and exceeds year-to-year variability. Free tropospheric ozone in East Asia is generally higher than in Europe or the United States, with the exception of July–August when the Asian summer monsoon circulation brings clean marine tropical inflow, depresses ozone levels in the free troposphere, and increases the height of the tropopause (Zhao et al., 2010; Lau et al., 2018; Basha et al., 2020). Free tropospheric ozone during May–June 2015–2019 in East Asia is up to 15 ppb higher than in Europe or the United States.
Figure 1Mean IAGOS vertical profiles of ozone mixing ratios over East Asia (30.0 to 45.0° N, 109.0 to 145.0° E), Europe (35.0 to 54.0° N, −11.0 to 30.0° E), and the United States (28.0 to 49.0° N, −124.6 to −66.8° E) for 2000–2004 and 2015–2019. Averages and interannual standard deviations of ozone column mixing ratios in the free troposphere (750–350 hPa) are shown with numbers of profiles in italics. Horizontal bars are standard deviations for selected 25 hPa vertical pressure levels. Dashed lines are the 750 and 350 hPa pressure levels defining the free troposphere for the purpose of our work.
To investigate the specific conditions that contribute to elevated free tropospheric ozone over East Asia during May–June, we leverage the simultaneous measurements of CO from IAGOS. Collocated measurements of ozone and CO have been used extensively as an indicator for stratospheric influence, since stratospheric air is rich in ozone and low in CO (Knowland et al., 2017; Dreessen, 2019; Chen et al., 2022). Figure 2 shows mean ozone concentrations within 5 ppb CO increments in the IAGOS column data for 750–350 hPa. We find that ozone in the 2015–2019 data is highest under clean conditions (CO < 100 ppb), but not in the 2000–2004 data. This strongly suggests increasing stratospheric influence and a large contribution of the stratosphere in the 2015–2019 data. We see no enhancement of ozone under polluted conditions with high CO, which would reflect PBL venting or fire influences, and this can be simply explained by the mean free tropospheric ozone being high relative to typical ozone levels in the polluted PBL or fire plumes.
Figure 2IAGOS ozone versus CO concentrations in the free troposphere (750–350 hPa) over East Asia during May–June 2000–2004 and 2015–2019. Ozone and CO column mixing ratios are from individual vertical profiles averaged over 25 hPa pressure levels. Ozone column mixing ratios are then averaged over bins of 5 ppb CO. Only bins with 50 or more observations are included. Seasonal panels for March–August and for Europe/United States are in Fig. S1 in the Supplement, highlighting that the high-O3/low-CO regime is unique to East Asia in May–June.
Seasonal ozone-CO relationships for East Asia, Europe, and the United States (March–August) are provided in Fig. S1 in the Supplement. The distinctive association of high ozone with low CO is unique to May–June in East Asia, and absent elsewhere or in other months. This reflects the regional meteorology: East Asia is a well-established hotspot for stratosphere–troposphere exchange, with frequent tropopause folds and strong jet-related subsidence in late spring (Akritidis et al., 2019; Ma et al., 2025). These processes inject ozone-rich, CO-poor air into the free troposphere, producing the observed negative O3-CO correlation. Such events are far less frequent over Europe and the United States, consistent with the absence of this signature in those regions. To further corroborate the stratospheric attribution, we analyzed coincident measurements of ozone, CO, and nitrous oxide (N2O) from the KORUS-AQ campaign (May–June 2016; Fig. S2). Ozone is anticorrelated with N2O, a robust stratospheric tracer (Nevison et al., 2007), while CO and N2O are positively correlated. High-ozone/low-N2O/low-CO air masses thus represent stratospheric intrusions, whereas CO and N2O-rich air masses correspond to lower-ozone tropospheric regions.
Recent analyses support our interpretation of high free tropospheric ozone over East Asia in late spring and its strong stratospheric influence. Multiple datasets indicate increasing free tropospheric ozone over East Asia during the past two decades, including IAGOS/ozonesonde-based trend analyses (1995–2017) and satellite lower-FT columns, both showing positive trends despite regional NOx declines (Lee et al., 2021; Wang et al., 2022a). Independent studies across East Asia also report frequent stratospheric intrusions that episodically elevate tropospheric and even surface ozone, consistent with our attribution (Ou-Yang et al., 2022; Chen et al., 2024).
We use the GEOS-Chem chemical transport model version 13.2.1 (http://geos-chem.org, last access: 9 December 2024) to interpret the elevated free tropospheric ozone over East Asia and its trend. GEOS-Chem is driven by MERRA-2-assimilated (Modern-Era Retrospective analysis for Research and Applications) meteorological data with a horizontal resolution of 0.5° × 0.625°, degraded here to 2° × 2.5°, and 72 vertical levels from the surface to 0.1 hPa. Global anthropogenic emissions are from the Community Emissions Data System (CEDS) (Hoesly et al., 2018) and are superseded with the KORUSv5 inventory for East Asia (KORUSv5, Woo et al., 2018) and the MEIC inventory for China (Zheng et al., 2018). Natural emissions include NOxfrom lightning (Murray et al., 2012) and soil (Hudman et al., 2012), MEGANv2 biogenic volatile organic compounds (VOCs) (Guenther et al., 2012), dust (Meng et al., 2021), and sea salt (Jaeglé et al., 2011). Open-fire emissions are from the Global Fire Emissions Database version 4 (GFED4; van der Werf et al., 2017).
Version 13.2.1 of GEOS-Chem includes a detailed oxidant-aerosol chemical mechanism for the troposphere and stratosphere (Wang et al., 2021). Here we add particulate nitrate photolysis, which was implemented in GEOS- Chem version 14.2.0 following Shah et al. (2023). Particulate nitrate photolysis has been found to be important for reproducing tropospheric ozone observations in the model, offsetting the effects of halogen-catalyzed ozone loss (Lin et al., 2024) and improving the simulation of NOx in remote air (Shah et al., 2023). Including particulate nitrate photolysis, Colombi et al. (2023) found that the model was able to reproduce the observed seasonal cycle and spatial distribution of surface ozone in South Korea and China, as well as the tropospheric ozone profile and observed decadal trend in South Korea. Shah et al. (2024) and Lin et al. (2024) found that it enabled an unbiased simulation of tropospheric ozone compared to IAGOS and ozonesonde observations worldwide.
Figure 3Mean free tropospheric (750–350 hPa) ozone column mixing ratios for May–June 2016 simulated by GEOS-Chem. Ozone vertical profiles over the East Asia and northern India maxima are also shown with comparison to IAGOS aircraft observations. Mean column mixing ratios for 750–350 hPa are shown in legend.
Figure 3 shows the global distribution of mean free tropospheric ozone simulated by GEOS-Chem in May–June 2016. Values are maximum over East Asia and northern India, consistent with IAGOS vertical profiles also shown in the Figure. Over northern India in May–June 2016, the model compared to observations for individual profiles has a root-mean-square-error (RMSE) of 6.6 ppb, a normalized mean error (NME) of 7.5 %, a correlation of 0.70, and a near-zero mean bias of 0.2 ppb. Over East Asia, where free-tropospheric ozone levels are higher and more variable due to frequent stratospheric intrusions, the model achieves a correlation of 0.77, an NME of 11.6 %, and a small mean bias of −2.7 ppb, though the RMSE is larger (21.1 ppb) because the model smooths out the most extreme enhancements (>100 ppb). The high pre-monsoon ozone concentration over northern India has been reported before as due to high emissions and peak photochemical conditions (Lu et al., 2018a). We conducted a sensitivity model simulation with anthropogenic emissions zeroed out over India and found that it does not contribute significantly to the maximum over East Asia (<2 ppb in the free troposphere during May–June). We further analyzed the model maximum over East Asia using observed ozone-CO relationships from the KORUS-AQ aircraft campaign over and around the Korea peninsula up to 300 hPa in May–June 2016 (Crawford et al., 2021), as shown in Fig. 4. The PBL (surface–750 hPa) data show a generally positive correlation of ozone with CO as expected from pollution influence, though both model and observations show elevated ozone at the lowest CO concentrations consistent with subsidence from the free troposphere. Simulated CO has a low bias compared to the KORUS-AQ observations, as previously noted (Yang et al., 2023), but captures the observed O3-CO relationships. The free tropospheric observations show a negative correlation of ozone with CO, consistent with Fig. 2 and implying stratospheric origin.
Figure 4Ozone versus CO mixing ratios in the free troposphere (750–350 hPa) and PBL (surface–750 hPa) over and around the Korea peninsula during the KORUS-AQ aircraft campaign in May–June 2016. 1 min observations are averaged over 5 ppb CO mixing ratio bins and compared to the GEOS-Chem simulation sampled along the aircraft tracks. Only bins with 20 or more observations are shown.
Figure 5Annual mean vertical advective flux of ozone at 100 hPa, averaged for 2000–2004 and 2015–2019. Negative values (blue) indicate downward motion. Net downwelling rates over East Asia (30.0–45.0° N, 109.0–145.0° E) are shown inset with interannual standard deviations.
We can diagnose from GEOS-Chem the vertical advective flux of ozone at 100 hPa, a well-established indicator of stratospheric-tropospheric-exchange (Gettelman and Sobel, 2000). Fluxes in May–June are noisy and so we focus on annual means. Global annual mean ozone fluxes across 100 hPa in GEOS-Chem and interannual standard deviations are 589 ± 17 Tg a−1 for 2000–2004 and 563 ± 37 Tg a−1 for 2015–2019, consistent with the observational estimate of 550 ± 140 Tg a−1 (Hu et al., 2017). Figure 5 shows the spatial distribution of the flux in the northern hemisphere, highlighting the intense downwelling over Northeast Asia. For the box in Fig. 5 centered over Korea, the flux increases from 52 ± 13 Tg a−1 in 2000–2004 to 72 ± 11 Tg a−1 in 2015–2019, consistent with the ozone vs. CO relationships in Fig. 2.
We use the tagged ozone capability in GEOS-Chem (Wang et al., 1998; Zhang et al., 2010; Ye et al., 2024) to further diagnose the contributions from the stratosphere and tropospheric source regions to the free tropospheric ozone over East Asia in May–June 2015–2019. The tagged simulation replicates the full-chemistry ozone budget by using archived production rates and loss frequencies of odd oxygen from a standard GEOS-Chem simulation. This linear diagnostic framework tracks the transport and chemical fate of odd oxygen produced in each tagged region, while removing from the accounting the fast-cycling reactions of ozone with short-lived reservoirs (Bates and Jacob, 2020). Although ozone chemistry is highly non-linear, the archived production and loss frequency fields reproduce the local conditions from the full-chemistry run to within 1–2 ppb (Zhang et al., 2010), which allows decomposition of the contribution from different sources for these local conditions (Fiore et al., 2002; Zhang et al., 2010; Ye et al., 2024). Here we conduct the tagged ozone simulation at 0.5° × 0.625° resolution over East Asia (10.0–45.0° N, 100.0–145.0° E), nested within the global 2° × 2.5° simulation, to better capture stratospheric influence over the region.
Figure 6 shows the results of this source attribution for the mean May–June vertical ozone profile simulated by GEOS-Chem over East Asia for 2015–2019. We find that ozone produced in the stratosphere makes up 30 % of total ozone at 500 hPa, with a strong vertical gradient opposite to that from tropospheric production. Stratospheric production contributes 10 ppb of ozone in the PBL, which is higher than 2–5 ppb previously found over the United States in GEOS-Chem using the same tagging method (Fiore et al., 2003). GEOS-Chem tends to underestimate stratospheric influence and events in surface air due to stretched-flow numerical diffusion affecting the downward transport of lamina (Zhang et al., 2014). The stratospheric contribution to the PBL would also be larger if we expanded the odd oxygen family to include hydrogen oxide radicals produced from ozone photolysis as in Bates and Jacob (2020). GEOS-Chem results from Bates and Jacob (2020) show that expanding the odd oxygen family in this manner identifies an additional 10 ppb of PBL ozone over East Asia as originating from the stratosphere (Fig. S3). From the expanded odd oxygen family perspective, a larger fraction of what is diagnosed as free- tropospheric production in Fig. 6 could instead be attributed to the stratosphere. Scaling this fractional increase into the free troposphere suggests that as much as 20 %–30 % of the production attributed to the East Asian free troposphere in Fig. 6 could alternatively be considered stratospheric in origin. We therefore note that our conventional Ox definition provides a conservative lower-bound estimate of stratospheric influence.
Figure 6Source attribution of mean ozone over East Asia in May–June 2015–2019 as simulated by GEOS-Chem. Total odd oxygen is decomposed into the contributions from different source regions including the stratosphere, the free troposphere (FT, 750–350 hPa), and PBL (surface–750 hPa). PBL values are daily maximum 8 h averages (MDA8).
We further investigate the contributions of stratospheric downwelling and emissions to the increase in May–June ozone over East Asia from 2000–2004 to 2015–2019 (Fig. 1). Figure 7a shows tagged-ozone simulation results where production and loss frequencies are archived from a 2017 full-chemistry simulation, and meteorology is simulated for individual years for the 2000–2004 and 2015–2019 periods. The resulting changes in ozone are solely from meteorology. We find no change below 600 hPa but a 5 ppb increase in the free troposphere above 600 hPa that is fully explained by increased stratospheric influence. Figure 7b shows full-chemistry simulation results for meteorological year 2017 but with either 2000 or 2019 emissions. We find an emission-driven increase of ozone of 8 ppb in the PBL decreasing to 2 ppb in the free troposphere. These model increases are consistent with the observed increases in Fig. 1 and imply that the PBL increase of ozone is mainly driven by increasing emissions while the free tropospheric increase is mostly driven by increased stratospheric downwelling.
Figure 72000–2019 ozone trends simulated by GEOS-Chem over East Asia. Values are averages for May–June (MDA8 in the PBL below 750 hPa) over the domain (30.0–45.0° N, 109.0–145.0° E). The left panel shows total ozone and stratospherically produced ozone from tagged ozone simulations for meteorological years 2000–2004 and 2015–2019 all with the same ozone production rates and loss frequencies (2017 full-chemistry simulation). Shading indicates interannual standard deviations, the right panel shows full-chemistry simulations with emissions for year 2000 and 2019 and common 2017 meteorology.
Increasing stratospheric influence over East Asia from 2000–2004 to 2015–2019 can be related to strengthening of the jet stream. Figure 8 shows the 100 and 200 hPa wind vectors from MERRA-2 for the two time periods. Jet stream activity is commonly associated with tropopause folds and stratospheric downwelling of ozone (Albers et al., 2018). We find an increase of high-altitude wind speeds over East Asia, reflecting a strengthening of the jet stream. A warming climate is expected to drive a strengthening and poleward-upward shift of the jet stream (Akritidis et al., 2019; Manney and Hegglin, 2018), increasing the frequency of tropopause folding events over East Asia (Ma et al., 2025). It is also expected to amplify zonal-mean temperature gradients and wave drag in the extratropical stratosphere (Shepherd and McLandress, 2011; Neu et al., 2014), increasing the ozone reservoir in the lowermost stratosphere (LMS) which can then be transported downward to the troposphere (Hegglin and Shepherd, 2009). We find evidence from ozondesonde data for increasing LMS ozone over East Asia (Fig. S4).
We examined the sources of elevated free tropospheric ozone (750–350 hPa) over East Asia in May–June to better understand the origin of this background contributing to severe and increasing surface ozone pollution in South Korea and China.
Aircraft observations and GEOS-Chem model simulations driven by MERRA-2 meteorology show that East Asia and northern India in May–June have the highest free tropospheric ozone concentrations in the world. Mean free tropospheric ozone observed over East Asia in May–June increased from 68 ± 3 ppb in 2000–2004 to 78 ± 4 ppb in 2015–2019, in contrast to Europe and North America where there was no significant trend. Free tropospheric ozone observed over East Asia in 2015–2019 was highest under low CO conditions (<100 ppb) and this is reproduced by GEOS-Chem. The ozone vertical flux at 100 hPa in GEOS-Chem identifies Northeast Asia as a global hotspot for downwelling of stratospheric ozone, with a 40 % increase in the downwelling flux from 2000–2004 to 2015–2019.
We used the GEOS-Chem tagged ozone (odd oxygen) simulation to identify the origin of free tropospheric ozone over East Asia. We find that stratospheric production accounts for 30 % of free tropospheric ozone and 12 % of planetary boundary layer (PBL) ozone over East Asia during May–June. Stratospheric influence diagnosed by the model would be higher with an expanded definition of odd oxygen to include hydrogen oxide radicals. The observed increase in free tropospheric ozone from 2000–2004 to 2015–2019 is reproduced by GEOS-Chem and is fully explained by the increased stratospheric downwelling, while the PBL ozone trend during the same period is mostly explained by changing anthropogenic emissions. The increased stratospheric downwelling is consistent with intensification of the jet stream over East Asia from 2000–2004 to 2015–2019. Intensification of the jet stream is expected in a warming climate.
We conclude that the unusually high free tropospheric ozone over East Asia in May–June (when surface ozone is maximum) is driven by intense and increasing stratospheric influence. This influence in turn elevates the background in surface air. Because of this elevated natural background, it appears unlikely that South Korea can meet its 60 ppb ozone air quality standard by controlling emissions. However, surface ozone concentrations over South Korea in May–June are frequently over 80 ppb, pointing to leverage for improving ozone air quality by decreasing NOx and volatile organic compound (VOC) emissions (Oak et al., 2025).
The code used in this work is available upon request.
We use ozone profile data from the In-Service Aircraft for a Global Observing System (IAGOS, https://iagos.aeris-data.fr/, last access: 12 January 2025).
The supplement related to this article is available online at https://doi.org/10.5194/acp-26-2623-2026-supplement.
The original draft preparation was done by NKC, with review and editing by DJJ, XY, RMY, KHB, DCP, LHY, KL, and HL. DJJ contributed to the project conceptualization. Modeling was done by NKC, with additional support from XY, RMY, KHB, and LHY. The formal analysis was conducted by NKC with additional support from DJJ, XY, RMY, KHB, DCP, LHY, KL, and HL.
At least one of the (co-)authors is a member of the editorial board of Atmospheric Chemistry and Physics. The peer-review process was guided by an independent editor, and the authors also have no other competing interests to declare.
Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims made in the text, published maps, institutional affiliations, or any other geographical representation in this paper. While Copernicus Publications makes every effort to include appropriate place names, the final responsibility lies with the authors. Views expressed in the text are those of the authors and do not necessarily reflect the views of the publisher.
This work was funded by the Harvard–Nanjing University of Information Science & Technology (NUIST) Joint Laboratory for Air Quality and Climate (JLAQC) and by the Samsung Advanced Institute of Technology.
This paper was edited by Carl Percival and reviewed by two anonymous referees.
Akritidis, D., Pozzer, A., and Zanis, P.: On the impact of future climate change on tropopause folds and tropospheric ozone, Atmos. Chem. Phys., 19, 14387–14401, https://doi.org/10.5194/acp-19-14387-2019, 2019.
Albers, J. R., Perlwitz, J., Butler, A. H., Birner, T., Kiladis, G. N., Lawrence, Z. D., Manney, G. L., Langford, A. O., and Dias, J.: Mechanisms Governing Interannual Variability of Stratosphere-to-Troposphere Ozone Transport, Journal of Geophysical Research: Atmospheres, 123, 234–260, https://doi.org/10.1002/2017JD026890, 2018.
Basha, G., Ratnam, M. V., and Kishore, P.: Asian summer monsoon anticyclone: trends and variability, Atmos. Chem. Phys., 20, 6789–6801, https://doi.org/10.5194/acp-20-6789-2020, 2020.
Bae, M., Kim, B.-U., Kim, H. C., Kim, J., and Kim, S.: Role of emissions and meteorology in the recent PM2.5 changes in China and South Korea from 2015 to 2018, Environmental Pollution, 270, 116233, https://doi.org/10.1016/j.envpol.2020.116233, 2021.
Bates, K. H. and Jacob, D. J.: An Expanded Definition of the Odd Oxygen Family for Tropospheric Ozone Budgets: Implications for Ozone Lifetime and Stratospheric Influence, Geophysical Research Letters, 47, e2019GL084486, https://doi.org/10.1029/2019GL084486, 2020.
Blot, R., Nedelec, P., Boulanger, D., Wolff, P., Sauvage, B., Cousin, J.-M., Athier, G., Zahn, A., Obersteiner, F., Scharffe, D., Petetin, H., Bennouna, Y., Clark, H., and Thouret, V.: Internal consistency of the IAGOS ozone and carbon monoxide measurements for the last 25 years, Atmos. Meas. Tech., 14, 3935–3951, https://doi.org/10.5194/amt-14-3935-2021, 2021.
Chen, Z., Liu, J., Qie, X., Cheng, X., Shen, Y., Yang, M., Jiang, R., and Liu, X.: Transport of substantial stratospheric ozone to the surface by a dying typhoon and shallow convection, Atmos. Chem. Phys., 22, 8221–8240, https://doi.org/10.5194/acp-22-8221-2022, 2022.
Chen, Z., Liu, J., Qie, X., Cheng, X., Yang, M., Shu, L., and Zang, Z.: Stratospheric influence on surface ozone pollution in China, Nat. Commun., 15, 4064, https://doi.org/10.1038/s41467-024-48406-x, 2024.
Chen, Z., Xie, Y., Liu, J., Shen, L., Cheng, X., Han, H., Yang, M., Shen, Y., Zhao, T., and Hu, J.: Distinct seasonality in vertical variations of tropospheric ozone over coastal regions of southern China, Science of The Total Environment, 874, 162423, https://doi.org/10.1016/j.scitotenv.2023.162423, 2023.
Colombi, N. K., Jacob, D. J., Yang, L. H., Zhai, S., Shah, V., Grange, S. K., Yantosca, R. M., Kim, S., and Liao, H.: Why is ozone in South Korea and the Seoul metropolitan area so high and increasing?, Atmos. Chem. Phys., 23, 4031–4044, https://doi.org/10.5194/acp-23-4031-2023, 2023.
Crawford, J. H., Ahn, J.-Y., Al-Saadi, J., Chang, L., Emmons, L. K., Kim, J., Lee, G., Park, J.-H., Park, R. J., Woo, J. H., Song, C.-K., Hong, J.-H., Hong, Y.-D., Lefer, B. L., Lee, M., Lee, T., Kim, S., Min, K.-E., Yum, S. S., Shin, H. J., Kim, Y.-W., Choi, J.-S., Park, J.-S., Szykman, J. J., Long, R. W., Jordan, C. E., Simpson, I. J., Fried, A., Dibb, J. E., Cho, S., and Kim, Y. P.: The Korea–United States Air Quality (KORUS-AQ) field study, Elementa: Science of the Anthropocene, 9, 00163, https://doi.org/10.1525/elementa.2020.00163, 2021.
Dreessen, J.: A Sea Level Stratospheric Ozone Intrusion Event Induced within a Thunderstorm Gust Front, Bulletin of the American Meteorological Society, https://doi.org/10.1175/BAMS-D-18-0113.1, 2019.
Emery, C., Jung, J., Downey, N., Johnson, J., Jimenez, M., Yarwood, G., and Morris, R.: Regional and global modeling estimates of policy relevant background ozone over the United States, Atmospheric Environment, 47, 206–217, https://doi.org/10.1016/j.atmosenv.2011.11.012, 2012.
Fiore, A. M., Jacob, D. J., Bey, I., Yantosca, R. M., Field, B. D., Fusco, A. C., and Wilkinson, J. G.: Background ozone over the United States in summer: Origin, trend, and contribution to pollution episodes, Journal of Geophysical Research: Atmospheres, 107, ACH 11-1–ACH 11-25, https://doi.org/10.1029/2001JD000982, 2002.
Fiore, A., Jacob, D. J., Liu, H., Yantosca, R. M., Fairlie, T. D., and Li, Q.: Variability in surface ozone background over the United States: Implications for air quality policy, Journal of Geophysical Research: Atmospheres, 108, https://doi.org/10.1029/2003JD003855, 2003.
Fleming, Z. L., Doherty, R. M., von Schneidemesser, E., Malley, C. S., Cooper, O. R., Pinto, J. P., Colette, A., Xu, X., Simpson, D., Schultz, M. G., Lefohn, A. S., Hamad, S., Moolla, R., Solberg, S., and Feng, Z.: Tropospheric Ozone Assessment Report: Present-day ozone distribution and trends relevant to human health, Elementa: Science of the Anthropocene, 6, 12, https://doi.org/10.1525/elementa.273, 2018.
Gaubert, B., Emmons, L. K., Raeder, K., Tilmes, S., Miyazaki, K., Arellano Jr., A. F., Elguindi, N., Granier, C., Tang, W., Barré, J., Worden, H. M., Buchholz, R. R., Edwards, D. P., Franke, P., Anderson, J. L., Saunois, M., Schroeder, J., Woo, J.-H., Simpson, I. J., Blake, D. R., Meinardi, S., Wennberg, P. O., Crounse, J., Teng, A., Kim, M., Dickerson, R. R., He, H., Ren, X., Pusede, S. E., and Diskin, G. S.: Correcting model biases of CO in East Asia: impact on oxidant distributions during KORUS-AQ, Atmos. Chem. Phys., 20, 14617–14647, https://doi.org/10.5194/acp-20-14617-2020, 2020.
Gettelman, A. and Sobel, A. H.: Direct Diagnoses of Stratosphere–Troposphere Exchange, Journal of Atmospheric Sciences, https://doi.org/10.1175/1520-0469(2000)057<0003:DDOSTE>2.0.CO;2, 2000.
Guenther, A. B., Jiang, X., Heald, C. L., Sakulyanontvittaya, T., Duhl, T., Emmons, L. K., and Wang, X.: The Model of Emissions of Gases and Aerosols from Nature version 2.1 (MEGAN2.1): an extended and updated framework for modeling biogenic emissions, Geosci. Model Dev., 5, 1471–1492, https://doi.org/10.5194/gmd-5-1471-2012, 2012.
Han, H., Liu, J., Yuan, H., Wang, T., Zhuang, B., and Zhang, X.: Foreign influences on tropospheric ozone over East Asia through global atmospheric transport, Atmos. Chem. Phys., 19, 12495–12514, https://doi.org/10.5194/acp-19-12495-2019, 2019.
Hegglin, M. I. and Shepherd, T. G.: Large climate-induced changes in ultraviolet index and stratosphere-to-troposphere ozone flux, Nature Geosci., 2, 687–691, https://doi.org/10.1038/ngeo604, 2009.
Hoesly, R. M., Smith, S. J., Feng, L., Klimont, Z., Janssens-Maenhout, G., Pitkanen, T., Seibert, J. J., Vu, L., Andres, R. J., Bolt, R. M., Bond, T. C., Dawidowski, L., Kholod, N., Kurokawa, J.-I., Li, M., Liu, L., Lu, Z., Moura, M. C. P., O'Rourke, P. R., and Zhang, Q.: Historical (1750–2014) anthropogenic emissions of reactive gases and aerosols from the Community Emissions Data System (CEDS), Geosci. Model Dev., 11, 369–408, https://doi.org/10.5194/gmd-11-369-2018, 2018.
Hong, J., Wang, H., Wang, W., Zhu, J., Deng, H., and Wang, H.: Impacts of stratosphere-to-troposphere transport on tropospheric ozone in southeastern China: insights from ozonesonde observations, Environ. Res. Lett., 19, 064068, https://doi.org/10.1088/1748-9326/ad4ef9, 2024.
Hu, L., Jacob, D. J., Liu, X., Zhang, Y., Zhang, L., Kim, P. S., Sulprizio, M. P., and Yantosca, R. M.: Global budget of tropospheric ozone: Evaluating recent model advances with satellite (OMI), aircraft (IAGOS), and ozonesonde observations, Atmospheric Environment, 167, 323–334, https://doi.org/10.1016/j.atmosenv.2017.08.036, 2017.
Hudman, R. C., Moore, N. E., Mebust, A. K., Martin, R. V., Russell, A. R., Valin, L. C., and Cohen, R. C.: Steps towards a mechanistic model of global soil nitric oxide emissions: implementation and space based-constraints, Atmos. Chem. Phys., 12, 7779–7795, https://doi.org/10.5194/acp-12-7779-2012, 2012.
Jaeglé, L., Quinn, P. K., Bates, T. S., Alexander, B., and Lin, J.-T.: Global distribution of sea salt aerosols: new constraints from in situ and remote sensing observations, Atmos. Chem. Phys., 11, 3137–3157, https://doi.org/10.5194/acp-11-3137-2011, 2011.
Jaffe, D. A., Cooper, O. R., Fiore, A. M., Henderson, B. H., Tonnesen, G. S., Russell, A. G., Henze, D. K., Langford, A. O., Lin, M., and Moore, T.: Scientific assessment of background ozone over the U.S.: Implications for air quality management, Elementa (Wash D C), 6, 56, https://doi.org/10.1525/elementa.309, 2018.
Kim, S.-W., Kim, K.-M., Jeong, Y., Seo, S., Park, Y., and Kim, J.: Changes in surface ozone in South Korea on diurnal to decadal timescales for the period of 2001–2021, Atmos. Chem. Phys., 23, 12867–12886, https://doi.org/10.5194/acp-23-12867-2023, 2023.
Knowland, K. E., Ott, L. E., Duncan, B. N., and Wargan, K.: Stratospheric Intrusion-Influenced Ozone Air Quality Exceedances Investigated in the NASA MERRA-2 Reanalysis, Geophysical Research Letters, 44, 10691–10701, https://doi.org/10.1002/2017GL074532, 2017.
Lau, W. K. M., Yuan, C., and Li, Z.: Origin, Maintenance and Variability of the Asian Tropopause Aerosol Layer (ATAL): The Roles of Monsoon Dynamics, Sci. Rep., 8, 3960, https://doi.org/10.1038/s41598-018-22267-z, 2018.
Lee, H.-J., Chang, L.-S., Jaffe, D. A., Bak, J., Liu, X., Abad, G. G., Jo, H.-Y., Jo, Y.-J., Lee, J.-B., and Kim, C.-H.: Ozone Continues to Increase in East Asia Despite Decreasing NO2: Causes and Abatements, Remote Sensing, 13, 2177, https://doi.org/10.3390/rs13112177, 2021.
Lee, H.-M., Kim, N. K., Ahn, J., Park, S.-M., Lee, J. Y., and Kim, Y. P.: When and why PM2.5 is high in Seoul, South Korea: Interpreting long-term (2015–2021) ground observations using machine learning and a chemical transport model, Science of The Total Environment, 920, 170822, https://doi.org/10.1016/j.scitotenv.2024.170822, 2024.
Lin, H., Emmons, L. K., Lundgren, E. W., Yang, L. H., Feng, X., Dang, R., Zhai, S., Tang, Y., Kelp, M. M., Colombi, N. K., Eastham, S. D., Fritz, T. M., and Jacob, D. J.: Intercomparison of GEOS-Chem and CAM-chem tropospheric oxidant chemistry within the Community Earth System Model version 2 (CESM2), Atmos. Chem. Phys., 24, 8607–8624, https://doi.org/10.5194/acp-24-8607-2024, 2024.
Lu, X., Zhang, L., Liu, X., Gao, M., Zhao, Y., and Shao, J.: Lower tropospheric ozone over India and its linkage to the South Asian monsoon, Atmos. Chem. Phys., 18, 3101–3118, https://doi.org/10.5194/acp-18-3101-2018, 2018a.
Lu, X., Hong, J., Zhang, L., Cooper, O. R., Schultz, M. G., Xu, X., Wang, T., Gao, M., Zhao, Y., and Zhang, Y.: Severe Surface Ozone Pollution in China: A Global Perspective, Environ. Sci. Technol. Lett., 5, 487–494, https://doi.org/10.1021/acs.estlett.8b00366, 2018b.
Lu, X., Zhang, L., Chen, Y., Zhou, M., Zheng, B., Li, K., Liu, Y., Lin, J., Fu, T.-M., and Zhang, Q.: Exploring 2016–2017 surface ozone pollution over China: source contributions and meteorological influences, Atmos. Chem. Phys., 19, 8339–8361, https://doi.org/10.5194/acp-19-8339-2019, 2019.
Luo, Y., Zhao, T., Meng, K., Hu, J., Yang, Q., Bai, Y., Yang, K., Fu, W., Tan, C., Zhang, Y., Zhang, Y., and Li, Z.: A mechanism of stratospheric O3 intrusion into the atmospheric environment: a case study of the North China Plain, Atmos. Chem. Phys., 24, 7013–7026, https://doi.org/10.5194/acp-24-7013-2024, 2024.
Ma, X., Huang, J., Hegglin, M. I., Jöckel, P., and Zhao, T.: Causes of growing middle-to-upper tropospheric ozone over the northwest Pacific region, Atmos. Chem. Phys., 25, 943–958, https://doi.org/10.5194/acp-25-943-2025, 2025.
Manney, G. L. and Hegglin, M. I.: Seasonal and Regional Variations of Long-Term Changes in Upper-Tropospheric Jets from Reanalyses, American Meteorological Society Journal of Climate, https://doi.org/10.1175/JCLI-D-17-0303.1, 2018.
Meng, J., Martin, R. V., Ginoux, P., Hammer, M., Sulprizio, M. P., Ridley, D. A., and van Donkelaar, A.: Grid-independent high-resolution dust emissions (v1.0) for chemical transport models: application to GEOS-Chem (12.5.0), Geosci. Model Dev., 14, 4249–4260, https://doi.org/10.5194/gmd-14-4249-2021, 2021.
Miyazaki, K., Sekiya, T., Fu, D., Bowman, K. W., Kulawik, S. S., Sudo, K., Walker, T., Kanaya, Y., Takigawa, M., Ogochi, K., Eskes, H., Boersma, K. F., Thompson, A. M., Gaubert, B., Barre, J., and Emmons, L. K.: Balance of Emission and Dynamical Controls on Ozone During the Korea-United States Air Quality Campaign From Multiconstituent Satellite Data Assimilation, Journal of Geophysical Research: Atmospheres, 124, 387–413, https://doi.org/10.1029/2018JD028912, 2019.
Murray, L. T.: Lightning NOx and Impacts on Air Quality, Curr. Pollution Rep., 2, 115–133, https://doi.org/10.1007/s40726-016-0031-7, 2016.
Murray, L. T., Jacob, D. J., Logan, J. A., Hudman, R. C., and Koshak, W. J.: Optimized regional and interannual variability of lightning in a global chemical transport model constrained by LIS/OTD satellite data, Journal of Geophysical Research: Atmospheres, 117, https://doi.org/10.1029/2012JD017934, 2012.
Nédélec, P., Blot, R., Boulanger, D., Athier, G., Cousin, J.-M., Gautron, B., Petzold, A., Volz-Thomas, A., and Thouret, V.: Instrumentation on commercial aircraft for monitoring the atmospheric composition on a global scale: the IAGOS system, technical overview of ozone and carbon monoxide measurements, Tellus B: Chemical and Physical Meteorology, 67, https://doi.org/10.3402/tellusb.v67.27791, 2015.
Neu, J. L., Flury, T., Manney, G. L., Santee, M. L., Livesey, N. J., and Worden, J.: Tropospheric ozone variations governed by changes in stratospheric circulation, Nature Geosci., 7, 340–344, https://doi.org/10.1038/ngeo2138, 2014.
Nevison, C. D., Mahowald, N. M., Weiss, R. F., and Prinn, R. G.: Interannual and seasonal variability in atmospheric N2O, Global Biogeochemical Cycles, 21, https://doi.org/10.1029/2006GB002755, 2007.
Oak, Y. J., Jacob, D. J., Pendergrass, D. C., Dang, R., Colombi, N. K., Chong, H., Lee, S., Kuk, S. K., and Kim, J.: Air quality trends and regimes in South Korea inferred from 2015–2023 surface and satellite observations, Atmos. Chem. Phys., 25, 3233–3252, https://doi.org/10.5194/acp-25-3233-2025, 2025.
Ou-Yang, C.-F., Babu, S. R., Lee, J.-R., Yen, M.-C., Griffith, S. M., Lin, C.-C., Chang, S.-C., and Lin, N.-H.: Detection of stratospheric intrusion events and their role in ozone enhancement at a mountain background site in sub-tropical East Asia, Atmospheric Environment, 268, 118779, https://doi.org/10.1016/j.atmosenv.2021.118779, 2022.
Park, R. J., Oak, Y. J., Emmons, L. K., Kim, C.-H., Pfister, G. G., Carmichael, G. R., Saide, P. E., Cho, S.-Y., Kim, S., Woo, J.-H., Crawford, J. H., Gaubert, B., Lee, H.-J., Park, S.-Y., Jo, Y.-J., Gao, M., Tang, B., Stanier, C. O., Shin, S. S., Park, H. Y., Bae, C., and Kim, E.: Multi-model intercomparisons of air quality simulations for the KORUS-AQ campaign, Elementa: Science of the Anthropocene, 9, 00139, https://doi.org/10.1525/elementa.2021.00139, 2021.
Pendergrass, D. C., Zhai, S., Kim, J., Koo, J.-H., Lee, S., Bae, M., Kim, S., Liao, H., and Jacob, D. J.: Continuous mapping of fine particulate matter (PM2.5) air quality in East Asia at daily 6 × 6 km2 resolution by application of a random forest algorithm to 2011–2019 GOCI geostationary satellite data, Atmos. Meas. Tech., 15, 1075–1091, https://doi.org/10.5194/amt-15-1075-2022, 2022.
Petzold, A., Thouret, V., Gerbig, C., Zahn, A., Brenninkmeijer, C. A. M., Gallagher, M., Hermann, M., Pontaud, M., Ziereis, H., Boulanger, D., Marshall, J., Nédélec, P., Smit, H. G. J., Friess, U., Flaud, J.-M., Wahner, A., Cammas, J.-P., Volz-Thomas, A., and Team, I.: Global-scale atmosphere monitoring by in-service aircraft – current achievements and future prospects of the European Research Infrastructure IAGOS, Tellus B: Chemical and Physical Meteorology, 67, https://doi.org/10.3402/tellusb.v67.28452, 2015.
Shah, V., Jacob, D. J., Dang, R., Lamsal, L. N., Strode, S. A., Steenrod, S. D., Boersma, K. F., Eastham, S. D., Fritz, T. M., Thompson, C., Peischl, J., Bourgeois, I., Pollack, I. B., Nault, B. A., Cohen, R. C., Campuzano-Jost, P., Jimenez, J. L., Andersen, S. T., Carpenter, L. J., Sherwen, T., and Evans, M. J.: Nitrogen oxides in the free troposphere: implications for tropospheric oxidants and the interpretation of satellite NO2 measurements, Atmos. Chem. Phys., 23, 1227–1257, https://doi.org/10.5194/acp-23-1227-2023, 2023.
Shah, V., Keller, C. A., Knowland, K. E., Christiansen, A., Hu, L., Wang, H., Lu, X., Alexander, B., and Jacob, D. J.: Particulate Nitrate Photolysis as a Possible Driver of Rising Tropospheric Ozone, Geophysical Research Letters, 51, e2023GL107980, https://doi.org/10.1029/2023GL107980, 2024.
Shepherd, T. G. and McLandress, C.: A Robust Mechanism for Strengthening of the Brewer–Dobson Circulation in Response to Climate Change: Critical-Layer Control of Subtropical Wave Breaking, 68, https://doi.org/10.1175/2010JAS3608.1, 2011.
Sullivan, J. T., McGee, T. J., Stauffer, R. M., Thompson, A. M., Weinheimer, A., Knote, C., Janz, S., Wisthaler, A., Long, R., Szykman, J., Park, J., Lee, Y., Kim, S., Jeong, D., Sanchez, D., Twigg, L., Sumnicht, G., Knepp, T., and Schroeder, J. R.: Taehwa Research Forest: a receptor site for severe domestic pollution events in Korea during 2016, Atmos. Chem. Phys., 19, 5051–5067, https://doi.org/10.5194/acp-19-5051-2019, 2019.
van der Werf, G. R., Randerson, J. T., Giglio, L., van Leeuwen, T. T., Chen, Y., Rogers, B. M., Mu, M., van Marle, M. J. E., Morton, D. C., Collatz, G. J., Yokelson, R. J., and Kasibhatla, P. S.: Global fire emissions estimates during 1997–2016, Earth Syst. Sci. Data, 9, 697–720, https://doi.org/10.5194/essd-9-697-2017, 2017.
Wang, H., Lu, X., Jacob, D. J., Cooper, O. R., Chang, K.-L., Li, K., Gao, M., Liu, Y., Sheng, B., Wu, K., Wu, T., Zhang, J., Sauvage, B., Nédélec, P., Blot, R., and Fan, S.: Global tropospheric ozone trends, attributions, and radiative impacts in 1995–2017: an integrated analysis using aircraft (IAGOS) observations, ozonesonde, and multi-decadal chemical model simulations, Atmos. Chem. Phys., 22, 13753–13782, https://doi.org/10.5194/acp-22-13753-2022, 2022a.
Wang, W., Parrish, D. D., Wang, S., Bao, F., Ni, R., Li, X., Yang, S., Wang, H., Cheng, Y., and Su, H.: Long-term trend of ozone pollution in China during 2014–2020: distinct seasonal and spatial characteristics and ozone sensitivity, Atmos. Chem. Phys., 22, 8935–8949, https://doi.org/10.5194/acp-22-8935-2022, 2022b.
Wang, X., Jacob, D. J., Downs, W., Zhai, S., Zhu, L., Shah, V., Holmes, C. D., Sherwen, T., Alexander, B., Evans, M. J., Eastham, S. D., Neuman, J. A., Veres, P. R., Koenig, T. K., Volkamer, R., Huey, L. G., Bannan, T. J., Percival, C. J., Lee, B. H., and Thornton, J. A.: Global tropospheric halogen (Cl, Br, I) chemistry and its impact on oxidants, Atmos. Chem. Phys., 21, 13973–13996, https://doi.org/10.5194/acp-21-13973-2021, 2021.
Wang, Y., Logan, J. A., and Jacob, D. J.: Global simulation of tropospheric O3-NOx-hydrocarbon chemistry: 2. Model evaluation and global ozone budget, Journal of Geophysical Research: Atmospheres, 103, 10727–10755, https://doi.org/10.1029/98JD00157, 1998.
Woo, J. H., Kim, Y., Kim, J., Jang, Y., Park, M., Choi, Y., Lee, E., Park, H., Park, R., Choi, Y., Simpson, I. J., Emmons, L. K., Crawford, J. H., Nault, B., Fried, A., Goldberg, D. L., and Streets, D. G.: Improving Bottom-up Emissions Information Based on Air Quality Measurement and Modeling Feedbacks – The KORUS Emissions Inventory, AGU Fall Meeting Abstracts 2018, A31B-07 Bibcode 2018AGUFM.A31B..07W, 2018.
Ye, X., Zhang, L., Wang, X., Lu, X., Jiang, Z., Lu, N., Li, D., and Xu, J.: Spatial and temporal variations of surface background ozone in China analyzed with the grid-stretching capability of GEOS-Chem High Performance, Science of The Total Environment, 914, 169909, https://doi.org/10.1016/j.scitotenv.2024.169909, 2024.
Yang, L. H., Jacob, D. J., Colombi, N. K., Zhai, S., Bates, K. H., Shah, V., Beaudry, E., Yantosca, R. M., Lin, H., Brewer, J. F., Chong, H., Travis, K. R., Crawford, J. H., Lamsal, L. N., Koo, J.-H., and Kim, J.: Tropospheric NO2 vertical profiles over South Korea and their relation to oxidant chemistry: implications for geostationary satellite retrievals and the observation of NO2 diurnal variation from space, Atmos. Chem. Phys., 23, 2465–2481, https://doi.org/10.5194/acp-23-2465-2023, 2023.
Zhang, L., Jacob, D. J., Liu, X., Logan, J. A., Chance, K., Eldering, A., and Bojkov, B. R.: Intercomparison methods for satellite measurements of atmospheric composition: application to tropospheric ozone from TES and OMI, Atmos. Chem. Phys., 10, 4725–4739, https://doi.org/10.5194/acp-10-4725-2010, 2010.
Zhang, L., Jacob, D. J., Downey, N. V., Wood, D. A., Blewitt, D., Carouge, C. C., van Donkelaar, A., Jones, D. B. A., Murray, L. T., and Wang, Y.: Improved estimate of the policy-relevant background ozone in the United States using the GEOS-Chem global model with ° × ° horizontal resolution over North America, Atmospheric Environment, 45, 6769–6776, https://doi.org/10.1016/j.atmosenv.2011.07.054, 2011.
Zhang, L., Jacob, D. J., Yue, X., Downey, N. V., Wood, D. A., and Blewitt, D.: Sources contributing to background surface ozone in the US Intermountain West, Atmos. Chem. Phys., 14, 5295–5309, https://doi.org/10.5194/acp-14-5295-2014, 2014.
Zhao, C., Wang, Y., Yang, Q., Fu, R., Cunnold, D., and Choi, Y.: Impact of East Asian summer monsoon on the air quality over China: View from space, Journal of Geophysical Research: Atmospheres, 115, https://doi.org/10.1029/2009JD012745, 2010.
Zheng, B., Tong, D., Li, M., Liu, F., Hong, C., Geng, G., Li, H., Li, X., Peng, L., Qi, J., Yan, L., Zhang, Y., Zhao, H., Zheng, Y., He, K., and Zhang, Q.: Trends in China's anthropogenic emissions since 2010 as the consequence of clean air actions, Atmos. Chem. Phys., 18, 14095–14111, https://doi.org/10.5194/acp-18-14095-2018, 2018.
- Abstract
- Introduction
- Observed free tropospheric ozone seasonality, trend, and relationship with CO
- GEOS-Chem simulation
- Attribution of the free tropospheric ozone maximum over East Asia
- Conclusions
- Code availability
- Data availability
- Author contributions
- Competing interests
- Disclaimer
- Financial support
- Review statement
- References
- Supplement
- Abstract
- Introduction
- Observed free tropospheric ozone seasonality, trend, and relationship with CO
- GEOS-Chem simulation
- Attribution of the free tropospheric ozone maximum over East Asia
- Conclusions
- Code availability
- Data availability
- Author contributions
- Competing interests
- Disclaimer
- Financial support
- Review statement
- References
- Supplement