The planned restoration of the mineral nutrient balance in forest soils by
recycling wood ashes has led to environmental concern. The objective of thi
s study was to determine whether treatment of forest soil with granulated w
ood ash and dolomite led to changes in the export of total mercury (TotHg)
and methyl mercury (MeHg) in run-off, and to determine whether any observed
changes could be correlated to changes in dissolved organic carbon (DOC) a
nd/or H+ concentration. Three catchments in central Sweden were investigate
d: one treated with wood ash, one with dolomite and one control. Samples of
run-off water from the three catchments were taken weekly or monthly durin
g 1 yr with the higher sampling frequency during high water flow periods. T
otHg, MeHg, pH and DOC were measured in all samples. MeHg and TotHg as well
as H+ and DOC in run-off water were lower in the limed area in comparison
to the other two areas. TotHg varied between 1 and 10 ng l(-1) in all three
areas. The average concentration in run-off from the limed area was 67% of
that from the reference catchment. TotHg in the ashed and reference areas
were not significantly different (p > 0.1). TotHg covaried with DOC and wat
er supply (both run-off and rainfall) and inversely with pH. TotHg concentr
ations in run-off were determined by the leaching of Hg-containing DOG. Dec
reased pH probably increased the leakage of Hg-loaded DOC from the soils. M
eHg was 0.1-0.3 ng l(-1) in the limed area and 0.2-112 ng l(-1) in the othe
r two areas. The average concentration in the limed area was 31% of the ave
rage in the reference area. MeHg covaried with DOC and temperature, indicat
ing that microbial activity was the most important factor determining MeHg
in run-off.