Atmospheric mercury uptake to foliage using in situ and transplanted lichens at the New Almaden Mining District, California, United States

Contaminated soils at former mercury (Hg) mines release Hg into the atmosphere that can be absorbed by the surrounding foliage and potentially contribute to inputs of Hg to downstream reservoirs and the food chain. Information on Hg re-emissions and atmospheric transport at the New Almaden Mining Di...

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Main Authors: Peter Weiss-Penzias, Brittney Straw, Michelle Rothman, Belle Zheng, Mark Seelos, Edwin Rivas Meraz, Peggy A. O’Day
Format: Article
Language:English
Published: Frontiers Media S.A. 2025-04-01
Series:Frontiers in Environmental Chemistry
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Online Access:https://www.frontiersin.org/articles/10.3389/fenvc.2025.1568188/full
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author Peter Weiss-Penzias
Brittney Straw
Michelle Rothman
Belle Zheng
Mark Seelos
Edwin Rivas Meraz
Peggy A. O’Day
author_facet Peter Weiss-Penzias
Brittney Straw
Michelle Rothman
Belle Zheng
Mark Seelos
Edwin Rivas Meraz
Peggy A. O’Day
author_sort Peter Weiss-Penzias
collection DOAJ
description Contaminated soils at former mercury (Hg) mines release Hg into the atmosphere that can be absorbed by the surrounding foliage and potentially contribute to inputs of Hg to downstream reservoirs and the food chain. Information on Hg re-emissions and atmospheric transport at the New Almaden Mining District (NAMD) in California’s Coast Range is lacking, despite the wealth of previous research at the site. This study addressed knowledge gaps regarding the locations of the highest Hg re-emissions using in-situ and transplanted lichens. High total Hg (THg) concentrations in lichen (up to 20 μg g−1) were found where ore-processing occurred pre-1900 and where the largest mines were. Mean background concentration of THg in lichen (156.3 ± 48.2 ng g−1) was observed >7.8 km away from the most contaminated site. Lichen THg was significantly higher than the background by 93–171 ng g−1 at locations along the shorelines of three small reservoirs in the NAMD. By transplanting lichens from background areas to three sites in the NAMD, statistically significant first-order rate constants of Hg uptake (0.0011–0.0036 days−1) were found. The trend in uptake rate constants matched the trend in THg concentrations in non-transplanted lichen and atmospheric concentrations monitored by Hg passive samplers. There was no trend in the control transplants nor in release rates. Speciation analysis of lichen samples collected from sites of highest contamination using Hg High Energy Resolution Fluorescence Detection (HERFD) XANES showed the dominance of α-HgS (cinnabar) in spectra, likely present as nanoparticles, in addition to variable Hg coordination by dithiol, sulfide, and chloride ligands at the micrometer scale. These results indicate that the majority of Hg in lichen is associated with non-volatile phases and/or organic species and suggest that a relatively small fraction of Hg exchanges with the atmosphere, in agreement with relatively low uptake rates. Overall, study results show that THg concentrations in lichen surveys have merit across gradients of contamination and indicate that Hg deposited to lichens is likely sequestered for many years before entering the soil as litterfall.
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spelling doaj-art-4021726388784bc68a14e0ce2c0ce4ef2025-08-20T02:17:14ZengFrontiers Media S.A.Frontiers in Environmental Chemistry2673-44862025-04-01610.3389/fenvc.2025.15681881568188Atmospheric mercury uptake to foliage using in situ and transplanted lichens at the New Almaden Mining District, California, United StatesPeter Weiss-Penzias0Brittney Straw1Michelle Rothman2Belle Zheng3Mark Seelos4Edwin Rivas Meraz5Peggy A. O’Day6Department of Microbiology and Environmental Toxicology, University of California, Santa Cruz, Santa Cruz, CA, United StatesDepartment of Microbiology and Environmental Toxicology, University of California, Santa Cruz, Santa Cruz, CA, United StatesDepartment of Microbiology and Environmental Toxicology, University of California, Santa Cruz, Santa Cruz, CA, United StatesDepartment of Microbiology and Environmental Toxicology, University of California, Santa Cruz, Santa Cruz, CA, United StatesSanta Clara Valley Water District, San Jose, CA, United StatesEnvironmental Systems Graduate Group, University of California, Merced, CA, United StatesDepartment of Life and Environmental Sciences and Environmental Systems Graduate Group, University of California, Merced, CA, United StatesContaminated soils at former mercury (Hg) mines release Hg into the atmosphere that can be absorbed by the surrounding foliage and potentially contribute to inputs of Hg to downstream reservoirs and the food chain. Information on Hg re-emissions and atmospheric transport at the New Almaden Mining District (NAMD) in California’s Coast Range is lacking, despite the wealth of previous research at the site. This study addressed knowledge gaps regarding the locations of the highest Hg re-emissions using in-situ and transplanted lichens. High total Hg (THg) concentrations in lichen (up to 20 μg g−1) were found where ore-processing occurred pre-1900 and where the largest mines were. Mean background concentration of THg in lichen (156.3 ± 48.2 ng g−1) was observed >7.8 km away from the most contaminated site. Lichen THg was significantly higher than the background by 93–171 ng g−1 at locations along the shorelines of three small reservoirs in the NAMD. By transplanting lichens from background areas to three sites in the NAMD, statistically significant first-order rate constants of Hg uptake (0.0011–0.0036 days−1) were found. The trend in uptake rate constants matched the trend in THg concentrations in non-transplanted lichen and atmospheric concentrations monitored by Hg passive samplers. There was no trend in the control transplants nor in release rates. Speciation analysis of lichen samples collected from sites of highest contamination using Hg High Energy Resolution Fluorescence Detection (HERFD) XANES showed the dominance of α-HgS (cinnabar) in spectra, likely present as nanoparticles, in addition to variable Hg coordination by dithiol, sulfide, and chloride ligands at the micrometer scale. These results indicate that the majority of Hg in lichen is associated with non-volatile phases and/or organic species and suggest that a relatively small fraction of Hg exchanges with the atmosphere, in agreement with relatively low uptake rates. Overall, study results show that THg concentrations in lichen surveys have merit across gradients of contamination and indicate that Hg deposited to lichens is likely sequestered for many years before entering the soil as litterfall.https://www.frontiersin.org/articles/10.3389/fenvc.2025.1568188/fullmercurylichenbioindicatormercury minewatershedHERFD XANES (X-ray absorption near edge structure)
spellingShingle Peter Weiss-Penzias
Brittney Straw
Michelle Rothman
Belle Zheng
Mark Seelos
Edwin Rivas Meraz
Peggy A. O’Day
Atmospheric mercury uptake to foliage using in situ and transplanted lichens at the New Almaden Mining District, California, United States
Frontiers in Environmental Chemistry
mercury
lichen
bioindicator
mercury mine
watershed
HERFD XANES (X-ray absorption near edge structure)
title Atmospheric mercury uptake to foliage using in situ and transplanted lichens at the New Almaden Mining District, California, United States
title_full Atmospheric mercury uptake to foliage using in situ and transplanted lichens at the New Almaden Mining District, California, United States
title_fullStr Atmospheric mercury uptake to foliage using in situ and transplanted lichens at the New Almaden Mining District, California, United States
title_full_unstemmed Atmospheric mercury uptake to foliage using in situ and transplanted lichens at the New Almaden Mining District, California, United States
title_short Atmospheric mercury uptake to foliage using in situ and transplanted lichens at the New Almaden Mining District, California, United States
title_sort atmospheric mercury uptake to foliage using in situ and transplanted lichens at the new almaden mining district california united states
topic mercury
lichen
bioindicator
mercury mine
watershed
HERFD XANES (X-ray absorption near edge structure)
url https://www.frontiersin.org/articles/10.3389/fenvc.2025.1568188/full
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