Solid–gas–water
phase partitioning of mercury (Hg)
and the processes governing its diffusivity within soils are poorly
studied. In this study, landscape and forest species dependences of
gaseous elemental Hg (Hg(0)) in soil profiles (0–50 cm) were
investigated over four seasons in eight subtropical (130 days) and
temperate (96 days) forest plots. The vertical soil pore Hg(0) concentrations
differed between subtropical (Masson pine, broad-leaved forest, and
open field) and temperate (Chinese pine, larch, mixed broad-leaf forests,
and open field) catchments, with annual averages ranging from 6.73
to 15.8 and 0.95 to 2.08 ng m–3, respectively. The
highest Hg(0) concentrations in soil gas consistently occurred in
the upper mineral or organic horizons, indicating immobilization of
Hg(0) in mineral soils. A strongly positive relationship between pore
Hg(0) concentrations and ratios of Hg to organic matter (SOM) in soils
suggests that the vertical distribution of Hg(0) is related to soil
Hg(0) formation by Hg(II) reduction and sorption to SOM. Temperature
was also an important driver of Hg(0) production in soil pores. Based
on measurements of soil–air Hg(0) exchange, diffusion coefficients
(D
s) of Hg(0) between soil and atmosphere
were calculated for field sites, providing a foundation for future
development and validation of terrestrial Hg models.