Abstract. The tundra plays a pivotal role in the Arctic mercury(Hg) cycle by storing atmospheric Hg deposition and shuttling it to theArctic Ocean. A recent study revealed that 70 % of the atmospheric Hgdeposition to the tundra occurs through gaseous elemental mercury (GEM or Hg(0))uptake by vegetation and soils. Processes controlling land–atmosphereexchange of Hg(0) in the Arctic tundra are central, but remainunderstudied. Here, we combine Hg stable isotope analysis of Hg(0) in theatmosphere, interstitial snow air, and soil pore air, with Hg(0) fluxmeasurements in a tundra ecosystem at Toolik Field Station in northernAlaska (USA). In the dark winter months, planetary boundary layer (PBL)conditions and Hg(0) concentrations were generally stable throughout the dayand small Hg(0) net deposition occurred. In spring, halogen-inducedatmospheric mercury depletion events (AMDEs) occurred, with the fastre-emission of Hg(0) after AMDEs resulting in net emission fluxes of Hg(0).During the short snow-free growing season in summer, vegetation uptake ofatmospheric Hg(0) enhanced atmospheric Hg(0) net deposition to the Arctictundra. At night, when PBL conditions were stable, ecosystem uptake ofatmospheric Hg(0) led to a depletion of atmospheric Hg(0). The night-timedecline of atmospheric Hg(0) was concomitant with a depletion of lighterHg(0) isotopes in the atmospheric Hg pool. The enrichment factor,ε202Hgvegetationuptake=-4.2 ‰ (±1.0 ‰) was consistentwith the preferential uptake of light Hg(0) isotopes by vegetation. Hg(0)flux measurements indicated a partial re-emission of Hg(0) during daytime,when solar radiation was strongest. Hg(0) concentrations in soil pore airwere depleted relative to atmospheric Hg(0) concentrations, concomitant withan enrichment of lighter Hg(0) isotopes in the soil pore air, ε202Hgsoilair-atmosphere=-1.00 ‰(±0.25 ‰) and E199Hgsoilair-atmosphere=0.07 ‰ (±0.04 ‰). Thesefirst Hg stable isotope measurements of Hg(0) in soil pore air areconsistent with the fractionation previously observed during Hg(0) oxidationby natural humic acids, suggesting abiotic oxidation as a cause for observedsoil Hg(0) uptake. The combination of Hg stable isotope fingerprints withHg(0) flux measurements and PBL stability assessment confirmed a dominantrole of Hg(0) uptake by vegetation in the terrestrial–atmosphere exchange ofHg(0) in the Arctic tundra.
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Atmosphere-terrestrial exchange of gaseous elemental mercury: parameterization improvement through direct comparison with measured ecosystem fluxes
To simulate global mercury (Hg) dynamics in chemical transport models (CTMs), surface-atmosphere exchange of gaseous elemental mercury, Hg 0 , is often parameterized based on resistance-based dry deposition schemes coupled with a re-emission function, mainly from soils. Despite extensive use of this approach, direct evaluations of this implementation against field observations of net Hg 0 exchange are lacking. In this study, we evaluate an existing net exchange parameterization (referred to here as the base model) by comparing modeled fluxes of Hg 0 to fluxes measured in the field using micrometeorological techniques. Comparisons were performed in two terrestrial ecosystems: a grassland site in Switzerland and an Arctic tundra site in Alaska, U.S., each including summer and winter seasons. The base model included the dry deposition and soil re-emission parameterizations from Zhang et al. (2003) and the global CTM GEOS-Chem, respectively. Comparisons of modeled and measured Hg 0 fluxes showed large discrepancies, particularly in the summer months when the base model overestimated daytime net deposition by approximately 9 and 2 ng m −2 h −1 at the grassland and tundra sites, respectively. In addition, the base model was unable to capture a measured nighttime net Hg 0 deposition and wintertime deposition. We conducted a series of sensitivity analyses and recommend that Hg simulations using CTMs: (i) reduce stomatal uptake of Hg 0 over grassland and tundra in models by a factor 5–7; (ii) increase nighttime net Hg 0 deposition, e.g. , by increasing ground and cuticular uptake by reducing the respective resistance terms by factors of 3–4 and 2–4, respectively; and (iii) implement a new soil re-emission parameterization to produce larger daytime emissions and lower nighttime emissions. We also compared leaf Hg 0 uptake over the growing season estimated by the dry deposition model against foliar Hg measurements, which revealed good agreement with the measured leaf Hg concentrations after adjusting the base model as suggested above. We conclude that the use of resistance-based models combined with the new soil re-emission flux parameterization is able to reproduce observed diel and seasonal patterns of Hg 0 exchange in these ecosystems. This approach can be used to improve model parameterizations for other ecosystems if flux measurements become available.
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- Award ID(s):
- 1848212
- PAR ID:
- 10126417
- Date Published:
- Journal Name:
- Environmental Science: Processes & Impacts
- Volume:
- 21
- Issue:
- 10
- ISSN:
- 2050-7887
- Page Range / eLocation ID:
- 1699 to 1712
- Format(s):
- Medium: X
- Sponsoring Org:
- National Science Foundation
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