Abstract
An industrial-era decline in Greenland ice-core methanesulfonic acid is thought to herald a collapse in North Atlantic marine phytoplankton stocks related to a weakening of the Atlantic meridional overturning circulation. By contrast, stable levels of total marine biogenic sulfur contradict this interpretation and point to changes in atmospheric oxidation as a potential cause of the methanesulfonic acid decline. However, the impact of oxidation on methanesulfonic acid production has not been quantified, nor has this hypothesis been rigorously tested. Here we present a multi-century methanesulfonic acid record from the Denali, Alaska, ice core, which shows a methanesulfonic acid decline similar in magnitude but delayed by 93 years relative to the Greenland record. Box-model results using updated dimethyl sulfide oxidation pathways indicate that oxidation by pollution-driven nitrate radicals has suppressed atmospheric methanesulfonic acid production, explaining most, if not all, of Denali’s and Greenland’s methanesulfonic acid declines without requiring a change in phytoplankton production. The delayed timing of the North Pacific methanesulfonic acid decline, relative to the North Atlantic, reflects the distinct history of industrialization in upwind regions and is consistent with the Denali and Greenland ice-core nitrate records. These results demonstrate that multidecadal trends in industrial-era Arctic ice-core methanesulfonic acid reflect rising anthropogenic pollution rather than declining marine primary production.
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Data availability
Denali ice-core (DEN13A and DEN13B) MSA data are available from the Arctic Data Center (https://doi.org/10.18739/A2Q814T9K). The Greenland MSA composite record is available from ref. 10, and Summit07 MSA data are available from ref. 22. Denali NO3– is available at the National Oceanic and Atmospheric Administration (NOAA) palaeoclimatology database (https://doi.org/10.25921/6cpm-kr44), and Summit07 NO3– is available from ref. 49. GEOS-Chem output is from ref. 54. CEDS emissions data used in this study are from ref. 30. All data shown in the Main and Extended Data Figures are available at the preceding references or can be recreated following the Code Availability Statement.
Code availability
The F0AM source code can be downloaded from https://github.com/AirChem/F0AM. Gas-phase MSA mechanisms were implemented following reactions listed in Supplementary Tables 1–4. GEOS-Chem source code can be downloaded from https://github.com/geoschem/geos-chem/tree/13.2.1. Code for Bayesian changepoint analysis was modified from the BEAST package (MATLAB version), which can be downloaded from https://github.com/zhaokg/Rbeast.
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Acknowledgements
Retrieval and analysis of the Denali ice core is supported by the National Science Foundation (NSF) Paleo Perspectives on Climate Change Program (P2C2), grants AGS-1204035 (E.C.O.), AGS-1203838 (K.J.K.) and AGS-1203863 (C.P.W.). Denali National Park and Preserve, Polar Field Services and Talkeetna Air Taxi provided aircraft support and field logistical assistance. We thank M. Waszkiewicz, S. Campbell, B. Markle, E. Burakowski, D. Silverstone and T. Godaire for field assistance, and over 25 students for their assistance sampling and analysing the Denali ice cores in the Dartmouth Ice, Climate, and Environment Laboratory. The Denali ice cores were processed at the NSF Ice Core Facility in Denver, Colorado. J.I.C. acknowledges travel support from the Dartmouth Dickey Center. NSF grants PLR-1904128 (B.A.), PLR-2230350 (B.A.) and AGS-2202287 (B.A.) supported analysis of the Summit07 ice core.
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J.I.C. and U.A.J. conceived of and carried out this study. E.C.O., B.G.K. and B.A. provided critical guidance and input throughout. E.C.O., K.J.K. and C.P.W. wrote the initial proposal to drill and chemically analyse the Denali ice core. D.G.F. melted the core and, with D.A.W. and E.C.O., developed the timescale. J.C.-D. obtained funding to drill and measure major ions, including MSA and NO3–, in the Summit07 ice core. K.S. and B.G.K. developed a set of initial hypotheses for MSA decline, and K.S. and D.J.P. investigated linkages between Denali MSA and North Pacific production. J.I.C. wrote the paper with input from E.C.O., B.G.K. and U.A.J. All authors discussed the results and reviewed the manuscript.
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Nature Geoscience thanks Alex Archibald, M. Anwar Khan and the other, anonymous, reviewer(s) for their contribution to the peer review of this work. Primary Handling Editor: Xujia Jiang, in collaboration with the Nature Geoscience team.
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Extended data
Extended Data Fig. 1 Ice core MSA records with changepoint probability.
(a) Denali MSA changepoint probability, based on an irregular Bayesian changepoint analysis (see Methods). The likeliest changepoint year (1962) indicated by a vertical dark orange dashed line. (b) Denali MSA. (c) The Greenland composite MSA records, with the record’s 50th percentile (dark blue) and 95% confidence interval (light blue) given10. (d) Greenland MSA changepoint probability, with the three likeliest changepoint years (1854, 1869, and 1953) indicated by vertical dark blue dashed lines.
Extended Data Fig. 2 F0AM box model results, including Ross Sea, Antarctica.
(a) The PI–IE percent change in MSA under several F0AM model runs, using atmospheric oxidant concentrations from the Denali source region (orange), the Greenland source region (blue), and the Ross Sea, Antarctica (green). The shapes represent the different DMS oxidation mechanisms we used. The APC (leftmost) column shows the change in MSA when all oxidants and temperature (that is, ‘parameters’) change from the PI to the IE. The columns to the right show the change when one parameter is held constant from the PI to the IE and the rest are allowed to change (CNSTp). (b) The MSA-impact score, which is the fraction change between CNSTp and APC. The magnitude of the MSA-impact score represents the oxidative effect of the increase of each parameter from the PI to the IE. Note that the impacts of O3 and OH in the Ross Sea is unusually high because the Ross Sea APC is close to 0. (c) An alternative calculation of MSA impact (MSA-delta), calculated by the difference between CNSTp and APC, which corrects the unusually high Ross Sea MSA-impact score in (b).
Extended Data Fig. 3 Denali MSA from cores 1 and 2.
The MSA record from Denali core 2 (orange; this study) and core 1 (red). Core 1 was only analyzed to 1866 and its raw record contains anomalous dips to near 0, leading to an overall lower annual average than core 2. Despite the data issues, core 1 contains a mean decline in MSA of 1.79 ppb from 1962–2011 compared with 1866–1961. Core 2, likewise, contains a mean drop of 1.77 ppb over the same period.
Extended Data Fig. 4 F0AM model parameter sensitivity testing of the Denali source region.
These are model runs in which all parameters (that is, oxidant concentrations and temperature) change from PI to IE, using the Fung mechanism. The red markers indicate the mean modeled changes for the Denali source region. Each panel shows the sensitivity of the model to different selections of the labeled parameter. See Methods for details.
Extended Data Fig. 5 F0AM model parameter sensitivity testing of the Greenland source region.
As with Extended Data Fig. 4, but with the Greenland MSA source region.
Supplementary information
Supplementary Information
Supplementary Figs. 1–4, Tables 1–5, discussion and references.
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Chalif, J.I., Jongebloed, U.A., Osterberg, E.C. et al. Pollution drives multidecadal decline in subarctic methanesulfonic acid. Nat. Geosci. (2024). https://doi.org/10.1038/s41561-024-01543-w
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DOI: https://doi.org/10.1038/s41561-024-01543-w