Sorption characteristics of inorganic, methyl and elemental mercury on lichens and mosses: Implication in biogeochemical cycling of mercury

The sorption studies of Hg2+, CH3Hg+ and elemental mercury (Hg-0) were carried out on lichen (Parmelia sulcata) and moss (Funaria hygrometrica) samples under laboratory conditions. Desorption studies with HCl indicate that inorganic mercury (Hg+2) and methyl mercury could be completely desorbed with 1 M HCl and 0.5 M HCl, respectively. Samples loaded with elemental kmercury, however, needed 4-5 M HCl concentration for complete desorption of the adsorbed elemental mercury. When similar desorption studies were carried out with field samples collected around a thermometer factory with elevated levels of mercury (similar to8 mg/kg), it was found that only about 10-15% of total mercury was desorbed with 1M HCl, while 4-5 M acid was required for complete desorption. We have tried to correlate this information to understand the transformations of mercury species that may occur either in the atmosphere or on the biomonitors. The results indicated that the elemental mercury, the principal form of mercury contamination around the thermometer factory, is converted into a strongly held form by some chemical binding agents on the surface of lichen/moss, or elemental mercury could diffuse into the cells of the lichen/moss, which then needs the stronger acid to release it. Sorption capacity studies suggest that the lichens and mosses can also be used as sorbent material for the decontamination of inorganic and methyl mercury from aqueous solutions.