Abstract. Plant foliage plays an essential role in accumulating mercury (Hg) from the
atmosphere and transferring it to soils in terrestrial ecosystems, and
many studies have focused on forested ecosystems. Hg input from plants to
northern peatland peat soils has not been nearly as well studied and is
likely equally important from a mass balance perspective. In this study, we
investigated the accumulation of atmospheric Hg by the dominant plant
species, few-seeded sedge (Carex oligosperma Michx.), wire sedge (Carex lasiocarpa Ehrh), tussock sedge (Carex stricta
Lamb.), and sweet gale (Myrica gale L.), in a boreal sedge-dominated peatland. Foliar Hg
concentrations decreased early in the growing season due to growth dilution,
and after that they were subsequently positively correlated with leaf age (time).
Hg concentrations were 1.4–1.7 times higher in sweet gale than in sedges. A
leaching experiment showed that sweet gale leached less Hg but more
bioaccessible dissolved organic matter (DOM) by mass than sedges. Leaching
of Hg was positively related to the aromaticity of DOM in leachate,
suggesting the importance of DOM with higher aromaticity in controlling Hg
mobility. Annual inputs of Hg through senesced leaf material to peat soils
were 9.88, 1.62, and 8.29 mg ha−1 yr−1 for sweet gale, tussock
sedge, and few-seeded sedge and wire sedge, respectively. Future investigations
into foliar Hg accumulation and input from other plant species to the
sedge-dominated peatland are needed to estimate the annual Hg inputs
precisely.