the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Vertically Resolved Formation Mechanisms of Fine Particulate Nitrate in Asian Megacities: Synergistic Lidar-Aircraft Observations and Process-Based Analysis
Abstract. The vertical distribution of particulate nitrate is crucial for understanding its formation mechanisms and developing urban haze reduction strategies. This study uses advanced technologies to collect continuous vertical data on nitrate concentrations in Beijing for 2021, providing a seasonal analysis of their distribution and influencing factors. Spring exhibits the highest nitrate concentration below 2 km (8.29 ± 3.14 μg/m³), followed by winter (7.34 ± 2.78 μg/m³), autumn (6.65 ± 2.11 μg/m³), and summer (2.23 ± 0.82 μg/m³). Below 300 m, nitrate formation in spring and summer is primarily driven by thermodynamic factors; relative humidity (RH) correlates at 0.64, while temperature (T) correlates at -0.76. In winter, both atmospheric oxidizing capacity (AOC, r = 0.52) and thermodynamic factors (r = 0.68) significantly influence nitrate formation. Between 0.8 km and 2 km, dynamic drivers such as turbulent kinetic energy (TKE, r = -0.41) and vertical wind speed (r = -0.43) dominate in spring and autumn. In contrast, photochemical factors, including AOC (r = 0.58) and ozone (r = 0.60), influence winter and summer. High nitrate levels are observed at the boundary layer top, peaking at 118.11 μg/m³ in late autumn, closely linked to photochemical processes and dynamic drivers. In winter, nitrate concentrations exhibit distinct diurnal variations, peaking at 13:00, 18:00, and 22:00, with variations and peak concentrations increasing with altitude due to the accumulation of photochemical products and enhanced AOC at night. These findings provide actionable insights for urban air quality management.
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Status: final response (author comments only)
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RC1: 'Comment on egusphere-2025-898', Anonymous Referee #2, 11 Jun 2025
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AC1: 'Reply on RC1', Ting Yang, 04 Jul 2025
The comment was uploaded in the form of a supplement: https://egusphere.copernicus.org/preprints/2025/egusphere-2025-898/egusphere-2025-898-AC1-supplement.pdf
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AC1: 'Reply on RC1', Ting Yang, 04 Jul 2025
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RC2: 'Comment on egusphere-2025-898', Anonymous Referee #3, 15 Jul 2025
This work comprehensively investigated the vertical distribution, seasonal variation, and formation mechanisms of nitrate pollution at different altitudes in urban Beijing, and thus is important. There are some comments which require to be addressed before it can be accepted.
- The title showed aircraft observation, however there is no any description in the main text. Add necessary related description or remove the aircraft from the title.
- Line 20, provide the specific height or height range for “the boundary layer top”.
- Line 23, what policy suggestion for the “actionable insights”?
- Line 49, “Therefore, the nitrate formation processes in the atmosphere are complex and challenging to elaborate” can be moved to the end of this paragraph.
- Line 56, for the “Despite a global decrease in nitrate radicals (NO3)”, is there any evidence and reference?
- Line 69, For the description “nitrate concentrations tend to increase with altitude”, please supplement the condition of this phenomenon, such as within boundary layer or lower boundary layer.
- Line 80, add “and” before “coefficient analyses”.
- Line 81, “managing nitrate pollution” can be “mitigating nitrate pollution”.
- Line 112, pay attention to the subscript for NO2.
- Line 95-96, how about the consistence between the ACSM measurements and the retrieval data at the lowest level? Simplify describe the comparison result.
- Line 115-117, how about the consistence between the ground NO2 measurements at the Beijing Olympic Sports Center and the ground-level data from CAMS?
- Line 170, it needs to clarify that NO2 are finally converted into nitric acid, nitrate, and organic nitrates.
- Line 171-172, show the correlation coefficient for the “weak correlation”.
- Line 190-192, show the correlation coefficients and the p values.
- Line 201-202, “the negative correlation between RH and nitrate” cannot conclude the nitrate decomposition at high humidity condition. Correct the explanation.
- Fig. 2, it seems that the extremely polluted cases in Fig. 6, Fig. 8, and Fig. 9 were not clearly shown in Fig. 2. Double check or explain it.
- Fig. 5, Thermodynamics processes generally also include the thermal decomposition of particulate nitrate. In addition, there may be some problem in the color of the correlation coefficient for TKE and w, because very low values also show red or light red color.
- Fig. 6, show the p values for the linear correlations in Fig. 6 a-h. Same suggestion for Fig. 8 and Fig. 9.
Citation: https://doi.org/10.5194/egusphere-2025-898-RC2 -
AC2: 'Reply on RC2', Ting Yang, 25 Jul 2025
The comment was uploaded in the form of a supplement: https://egusphere.copernicus.org/preprints/2025/egusphere-2025-898/egusphere-2025-898-AC2-supplement.pdf
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The manuscript addresses an important environmental issue, vertical formation mechanism of nitrates in Asian megacities. It is overall well written, providing important progress through vertically continuous observations and comprehensive data analysis. My specific comments are as follows: