The oxidative dissolution rate of metacinnabar by dissolved O-2 was measure
d at pH similar to5 in batch and column reactors. In the batch reactors, th
e dissolution rate varied from 3.15 (+/-0.40) to 5.87 (+/-0.39) x 10(-2) mu
mol/m(2)/day (I = 0.01 M, 23 degreesC) and increased with stirring speed,
a characteristic normally associated with a transport-controlled reaction.
However, theoretical calculations, a measured activation energy of 77 (+/-8
) kJ/mol (I = 0.01 M), and the mineral dissolution literature indicate reac
tion rates this slow are unlikely to be transport controlled. This phenomen
on was attributed to the tendency of the hydrophobic source powder to aggre
gate and minimize the effective outer surface area. However, in a column ex
periment, the steady-state dissolution rate ranged from 1.34 (+/-0.11) to 2
.27 (+/-0.11) x 10(-2) mu mol/m(2)/day (I = 0.01 M, 23 degreesC) and was al
so influenced by flow rate, suggesting hydrodynamic conditions may influenc
e weathering rates observed in the field. The rate of Hg release to solutio
n, under a range of hydrogeochemical conditions that more closely approxima
ted those in the subsurface, was I to 3 orders of magnitude lower than the
dissolution rate due to the adsorption of released Hg(II) to the metacinnab
ar surface. The measured dissolution rates under all conditions were slow c
ompared to the dissolution rates of minerals typically considered stable in
the environment, and the adsorption of Hg(II) to the metacinnabar surface
further lowered the Hg release rate. (C) 2001 Elsevier Science Ltd. All rig
hts reserved.