the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Measurement report: Three-year characteristics of sulfuric acid in urban Beijing and derivation of daytime sulfuric acid proxies applicable to various sites
Abstract. Sulfuric acid (H2SO4) is a key precursor in atmospheric new particle formation and cluster early growth. However, long-term measurement of it remains scarce due to technical challenges. Although several proxies for estimating H2SO4 concentration have been proposed, they are always site-specific. Therefore, both reliable H2SO4 measurement and proxies with wider application are highly needed. Here, we conducted a long-term H2SO4 measurement in urban Beijing during 2019–2021, and derived three H2SO4 proxies based entirely on its formation and loss pathways (OH-CS, UVB-CS and UVB-PM2.5 based proxies). Results show that daytime H2SO4 concentration is 2.0–7.4×106 molec cm-3 and shows an overall decline with an average annual decrease of 14 %. This decline is mainly due to the ongoing SO2 emission controls. Daytime H2SO4 shows a clear seasonal variation that tracks UVB. Nighttime H2SO4 concentration is 1.6–6.3×105 molec cm-3, with higher levels in warmer seasons due to stronger sources and lower condensation sink. The diurnal variations of H2SO4 across seasons follow those of photo-oxidation-related parameters, such as UVB, OH radical, and J(NO2). All of the three proxies can reproduce H2SO4 concentration during 10:00–14:00. Importantly, they can estimate H2SO4 concentration at a boreal forest site in Hyytiälä, Finland, suggesting their applicability to sites with diverse environments. Furthermore, the parameters used in UVB-PM2.5 based proxy are available at most observational sites. Further application of this proxy could provide H2SO4 concentrations covering many regions worldwide, which may further facilitate research on atmospheric nucleation and secondary aerosol growth of these sites.
- Preprint
(2371 KB) - Metadata XML
-
Supplement
(5735 KB) - BibTeX
- EndNote
Status: open (until 21 Nov 2025)
- RC1: 'Comment on egusphere-2025-4309', Dongjie Shang, 30 Oct 2025 reply
-
RC2: 'Comment on egusphere-2025-4309', Jie Zhang, 04 Nov 2025
reply
This study presents long-term measurements of sulfuric acid (H₂SO₄) in urban Beijing (2019–2021) and develops three formation- and loss-based proxies (OH–CS, UVB–CS, and UVB–PM₂.₅). All three proxies reproduced observed concentrations well, and the UVB–PM₂.₅ proxy was successfully applied to a boreal forest site, indicating its potential for broader global application in studying atmospheric nucleation and aerosol growth. This paper presents innovative and valuable findings; however, some revisions are needed to improve clarity before publication.
Major Comments
-
The manuscript would benefit from improved organization. It currently appears to have been written by two different contributors (modeling and observation parts), resulting in inconsistent flow and style. The overall readability should be improved by polishing the language and avoiding vague expressions.
-
The modeled concentrations of key pollutants should be evaluated against available observations (e.g., O₃, SO₂, and other relevant species) to validate model performance and strengthen the credibility of the results.
Minor Comments
-
Please avoid vague wording such as “scarce.”
-
Abbreviations (e.g., OH–CS, UVB–CS, UVB–PM₂.₅) and variables (e.g., J(NO₂)) in the abstract should be spelled out at first mention for clarity.
-
Lines 101–109: Please present each equation on a separate line and number them sequentially.
-
Line 139: Ensure that all equations in the manuscript are numbered consistently and in order.
-
Line 174: Revise the sentence to remove the repeated name in parentheses — it should read: “The modelling domain was the same as in Zheng et al. (2020).”
-
Line 197: In the sentence “Thus, the yearly decline of sulfuric acid is mainly attributed to the decrease of SO₂ (by ~25% per year),” please provide appropriate references to support this statement.
Citation: https://doi.org/10.5194/egusphere-2025-4309-RC2 -
Data sets
Measurement report: Three-year characteristics of sulfuric acid in urban Beijing and derivation of daytime sulfuric acid proxies applicable to various sites Y. Guo et al. https://doi.org/10.5281/zenodo.17216660
Viewed
| HTML | XML | Total | Supplement | BibTeX | EndNote | |
|---|---|---|---|---|---|---|
| 444 | 51 | 13 | 508 | 30 | 9 | 9 |
- HTML: 444
- PDF: 51
- XML: 13
- Total: 508
- Supplement: 30
- BibTeX: 9
- EndNote: 9
Viewed (geographical distribution)
| Country | # | Views | % |
|---|
| Total: | 0 |
| HTML: | 0 |
| PDF: | 0 |
| XML: | 0 |
- 1
Remarks to the Author:
Guo et al. present a comprehensive analysis of a three-year sulfuric acid concentration dataset at an urban site and put forward three daytime concentration proxies. Compared to proxies presented in earlier research, the three proxies in this study exhibit better results in reproducing the daytime sulfuric acid concentration. Furthermore, the authors discuss the possibility of applying the three proxies in this study to other environments.
In the atmospheric chemistry research area, especially for atmospheric new particle formation research, sulfuric acid is a critical substance as it is the major oxidation product from sulfur dioxide and possesses non-volatile characteristics. However, measurement of sulfuric acid based on mass spectrometer instruments is not yet wide and continuous enough for us to generate a big picture of new particle formation in different environments and periods.
The study from Guo et al. not only makes a valuable complement to the current sulfuric acid concentration dataset but also gives an attempt on sulfuric acid concentration estimation based on the work of predecessors. I think once the questions listed below are addressed, this paper is adequate to be published.
--1. I do not agree with the “applicable to various sites” description in the title. The three proxies in this study only consider the source of sulfur dioxide oxidation by OH radical and the authors only verify these proxies against the dataset in Hyytiälä. As mentioned in the introduction, for example, sulfuric acid may arise from dimethyl disulfide or dimethyl sulfide oxidation in coastal areas, and this has caused pronounced underestimation using a similar proxy (k [SO2] [OH]/CS).
--2. According to Fig 1C, Fig S2, Fig 6 and Fig S10, the current sulfur dioxide concentration is relatively low in Beijing (e.g., the median concentration from May to Nov. is all close to or lower than 0.5 ppb in 2021 even without precipitation data (Fig 1C and Fig S2), which can also be seen from the frequency plot of sulfur dioxide concentration in Fig 6 and Fig S10). While the three proxies in this study exhibit negative bias when sulfur dioxide concentration lies in this range (Fig 6 and Fig S10).
As far as I know, new particle formation events (NPF) often correspond to scavenging conditions in polluted urban environments, which means that NPF are most likely to stay in the low CS and low sulfur dioxide concentration range. Despite the aforementioned negative bias in the low sulfur dioxide concentration range, the three proxies in this study still behave well for the lowest CS bin which corresponds to scavenging conditions. So, this present method confused me when it comes to how well these proxies work exactly during NPF since the authors highlight the importance of these proxies for NPF analysis.
If you could break the individual bins in the frequency plot into accumulated columns classified by NPF and non-NPF, I think the plot will be more straightforward and valuable for others. Or you can find other ways to sort out the inherent co-occurrence relationship between these parameters (UVB, SO2 concentration, CS, RH).
--3. In Fig 5, as the dataset becomes larger, more points fall into the measured sulfuric acid concentration >> proxy calculated sulfuric acid concentration regime. What is the parameter condition of these deviated points? Does the parameter condition of these deviated points match the results you found “When OH radical, UVB and SO2 are too low, when CS and PM2.5 are too high, or when RH exceeds 60%, estimated sulfuric acid concentration may deviate from the actual concentration to a larger extent”? And why are there fewer points deviating into the measured sulfuric acid concentration << proxy calculated sulfuric acid concentration regime?
--4. In equation (6), why is there no term (T/300)-0.7 anymore?
--5. Some details in writing. For example, in Table 3, there is no parameter “f” in the ProxyLu et al.. Please check again.