Abstract
Inorganic and organic mercury forms (203HgCl2 and CH3 203HgCl) were added to a natural sediment maintained in dilute suspension under oxic conditions, and partitioning was followed over time with the aid of phase separation techniques (centrifugation–filtration) and chemical extractions (1 N HCl; 0.1 N NaOH; 30% H202). Sorption of inorganic Hg onto the suspended sediment was essentially complete (>99% of the added HgCl2 was associated with the sediment particles) and very rapid (t1/2>> 1 d). The nature of the Hg-particle association, as probed by partial extractions with HCl or NaOH, showed no discernible time trend (t = 1, 3, 8, 16, 32 d). Partitioning of CH3 203HgCl also favoured the particulate phase, but the relative amounts present in the dissolved phase (3–5%) and in the HCl extract were higher than with HgCl2. Results obtained with hydrogen peroxide, a reagent often used in the past to oxidize sedimentary organic matter and solubilize the Hg associated with this sink, proved unreliable. Under the extraction conditions the H2O2 acts not only as an oxidizing agent for the organic matter, but also as a reducing agent for the mercury. leading to volatilization and loss of the metal, presumably as Hg°.