Soot
and mercury (Hg) are two notorious air pollutants, and the
fate and transport of Hg may be affected by soot at various scales
in the environment as soot may be both a carrier and a reactant for
active Hg species. This study was designed to quantify photoreduction
of Hg(II) in the presence of soot and the associated Hg isotope fractionation
under both atmospheric aerosol and aqueous conditions (water-saturated).
Photoreduction experiments were conducted with diesel soot particulate
matter under controlled temperature and relative humidity (RH) conditions
using a flow-through semibatch reactor system. Mass-dependent fractionation
resulted in the enrichment of heavier Hg isotopes in the remaining
Hg(II) with enrichment factors (ε202Hg) of 1.48 ±
0.02‰ (±2 standard deviation) to 1.75 ± 0.05‰
for aerosol-phase reactions (RH 28–68%) and from 1.26 ±
0.11 to 1.50 ± 0.04‰ for aqueous-phase reactions. Positive
odd mass-independent fractionation (MIF) was observed in aqueous-phase
reactions, resulting in Δ199Hg values for reactant
Hg(II) as high as 5.29‰, but negative odd-MIF occurred in aerosol-phase
reactions, in which Δ199Hg values of reactant Hg(II)
varied from −1.02 to 0‰. The average ratio of Δ199Hg/Δ201Hg (1.1) indicated that under all
conditions, MIF was dominated by magnetic isotope effects during photoreduction
of Hg(II). Increasing RH resulted in higher reduction rates but lower
extents of negative MIF in the aerosol-phase experiments, suggesting
that the reduction of soot particle-bound Hg(II) was responsible for
the observed negative odd-MIF. Our results suggest that mass-independent
Hg isotope fractionation during Hg(II) photoreduction varies with
soot aerosol water content and that Hg-stable isotope ratios may be
used to understand the transformational histories of aerosol-bound
Hg(II) in the environment.