the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Mercury dataset over the Third Pole
Abstract. The Tibetan Plateau and its surrounding regions, collectively known as the Third Pole, constitute one of Earth’s largest topographic and cryospheric features, playing a pivotal role in the cycling of trace elements at both regional and global scales. Mercury (Hg), a toxic heavy metal of global concern, has garnered increasing attention due to its detrimental effects on environmental and human health. Large-scale atmospheric circulation facilitates the long-range transport of atmospheric Hg pollutants, which can subsequently be deposited across the Third Pole. Over recent decades, the Atmospheric Pollution and Cryospheric Change (APCC) program has established and sustained an integrated monitoring network throughout this region to systematically examine the interactions between Hg biogeochemical cycling and cryospheric changes. This paper presents a comprehensive Hg dataset encompassing air (2 stations), aerosols (9 stations), precipitation (16 stations), glaciers (12 glaciers; including snowpit, surface snow, and cryoconite samples), soils (50 sites), surface waters (53 locations; including river, lake, and glacial meltwater), glacier ice cores (1 core), and lake sediment cores (8 cores) collected across the Third Pole. The data were acquired through both in situ (online) monitoring and laboratory analyses. High-resolution atmospheric Hg concentrations were measured using a Tekran 2537B analyzer at the Nam Co and Tanggula stations. Spatial and temporal distributions of Hg in aerosols, precipitation, glaciers, soils, and sediment cores revealed distinct patterns and trends across different sectors of the Third Pole, influenced significantly by emission sources, transport pathways, and environmental processes. Depositional chronologies derived from glacier ice and lake sediment cores reflect anthropogenic perturbations in the historical Hg record since the Industrial Revolution. Stable Hg isotope compositions from aerosols, soils, and lake sediments provide evidence for transboundary transport of Hg pollution and its northward incursion into the interior Tibetan Plateau from South Asia. This updated dataset is made publicly available to support interdisciplinary research linking the cryosphere, atmosphere, soils, and hydrology. The data are archived in standardized Excel format and accessible through the institutional repository of the State Key Laboratory of Cryospheric Science and Frozen Soil Engineering, Northwest Institute of Eco-Environment and Resources, Chinese Academy of Sciences, Lanzhou (Kang et al., 2024).
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Status: open (until 16 May 2026)
- RC1: 'Comment on essd-2025-551', Anonymous Referee #1, 10 Apr 2026 reply
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RC2: 'Comment on essd-2025-551', Anonymous Referee #2, 14 Apr 2026
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The comment was uploaded in the form of a supplement: https://essd.copernicus.org/preprints/essd-2025-551/essd-2025-551-RC2-supplement.pdf
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RC3: 'Comment on essd-2025-551', Anonymous Referee #3, 15 Apr 2026
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This manuscript presents a comprehensive mercury dataset comprising air, aerosols, precipitation, glaciers, soils, surface waters, glacier ice cores, and lake sediment cores collected across the Third Pole. The authors have made a commendable effort to establish the integrated monitoring network through the Atmospheric Pollution and Cryospheric Change (APCC) program, thereby making it accessible to collect samples from harsh environments across the Tibetan Plateau and its surrounding regions. The data are publicly available. I believe this dataset will be of high interest to the Earth system science community, particularly for improving predictions of mercury cycling in cryosphere environments and evaluating its impact under rapid climate warming and cryosphere ablation on the Third Pole. My comments are as follows:
1. Section 2. Observation site descriptions and section 3. Field sampling and measurement methods share a similar structure for introducing various environmental matrices. Is it possible to combine these two sections?
2. Observation site descriptions: 1) L152: format error for Huang et al., 4.
3. Field sampling and measurement methods: 1) Vegetation is a useful environmental compartment to explore mercury cycling between the atmosphere and terrestrial ecosystem. Why didn’t the authors collect vegetation samples? 2) L237: HgP is not defined. 3) L305: If the same analytical procedures were applied as for aerosol and cryoconite samples, these analytical details should be presented above when you describe the aerosol and cryoconite samples. 4) L317: What is MOS-grade? 5) L336-338: The authors did not specify which samples were processed for isotope analysis. For aerosol samples, aqua regia digestion cannot eliminate the influence of interfering elements remaining in samples, which may cause the lower recovery of samples and have an impact on the accuracy of mercury isotope analysis. The authors need to point out this limitation.
4. Data descriptions. 1) There are no mercury isotope data from other matrices, why? 2) L352: Do you mean yearly TGM rather than monthly TGM? 3) L410: There is no MeHg in Fig. 3b. 3) L440: here and elsewhere, is the difference significant? 4) L457-463: The expression of “n” is not consistent. 5) L531-536: There is no description of lake sediment core δ202Hg values. Based on Δ199Hg, I think it cannot illustrate the rising anthropogenic Hg emissions originating from South Asia, especially for the Tanglha Lake sediment, mercury photochemical reactions can also lead to the positive Δ199Hg value. Anthropogenic Hg emission signal may be modified by the atmospheric redox before deposition into the lake sediment. The last sentence, “The dataset offers empirical constraints on Hg distribution, with an emphasis on observational evidence rather than source attribution”, looks strange in the current context. 6) There is no further discussion about the mercury isotope data of aerosols and soils. (7) I think many of the Hg isotope data from the third pole, including air and vegetation, are not included.
5. Dataset limitations and applications: The discussion about potential applications is very broad and vague. Please try to be more specific.
Figures: Fig. 4 is not referred to in the main text. Fig. 7 only shows the sampling location. Is it possible to add THg concentrations like other figures? Fig. 9 only shows the lakes from the northern slopes. Why not show the data from the southern slopes?
Tables: The information in tables doesn’t match well with the main text. The authors need to carefully check all the details.Citation: https://doi.org/10.5194/essd-2025-551-RC3
Data sets
Hg dataset over the Third Pole Shichang Kang, Jie Huang, Qianggong Zhang, Junming Guo, Xiufeng Yin, Shiwei Sun, and Xuejun Sun https://www.doi.org/10.12072/ncdc.qzkk.db6654.2024
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The authors have conducted long-term, high-altitude field observations across the Third Pole under extremely challenging conditions. The resulting comprehensive mercury dataset-covering air, aerosols, precipitation, glaciers, soils, waters, ice cores, and sediment cores-represents a remarkable logistical and scientific achievement. Given the outstanding observational efforts and the overall good quality of the data presented, the manuscript is promising. The clarity of the writing and the value of the dataset are commendable. I recommend acceptance after a moderate revision, as this dataset will serve as a valuable resource for the cryospheric and environmental geochemistry community.
Major concerns
As a data paper, the manuscript lacks critical QA/QC metadata, including detection limits, analytical precision, blank corrections, and reference material results for each measurement matrix (air, aerosols, precipitation, snow, soils, waters, ice cores, sediment cores, and Hg isotopes). A comprehensive QA/QC table should be provided to ensure data transparency and reusability.
The dataset spans a vast and heterogeneous region yet relies on only two air monitoring stations, one ice core, and limited spatial coverage for several media. The authors should add a concise statement in the data description acknowledging these spatial limitations, discuss how the existing data still support the main conclusions, and clarify which findings are regionally robust versus site‑specific. This is essential for proper use of the dataset by the community.
Specific concerns