Radiochemical partitioning experiments using 203Hg
have been undertaken with mixtures of river, seawater and sediment samples
taken from three geochemically contrasting UK estuaries: the Plym, Beaulieu
and Mersey. Species of dissolved Hg were determined using reversed-phase
C18 chelating columns and particulate species were determined by
sequential leaching with 1 M NH4OAc and 1 M HCl.
Mercury had a high particle reactivity with partition coefficients, KDs,
ranging from 104 to 5 × 105 ml g−1,
depending on salinity, the chemical composition of the end-member waters,
and on the physico-chemical characteristics of the sediment. Dissolved
organic matter present in the waters (humic substances and/or anthropogenic
compounds) was found to be the main factor governing the forms of dissolved
Hg and their reactivity. From the spiked 203Hg, up to 95%
of the dissolved metal was retained on the C18 columns for the
Mersey waters, whereas this fraction was <60% in the Plym and Beaulieu
waters. Quasi-irreversible adsorption of Hg onto particles from each estuary
was observed over a time-scale of a few hours and <20% of total
particulate Hg was released by the sequential leach. In this paper, physico-chemical
processes are proposed to explain the estuarine behaviour of Hg and the results
are discussed in terms of Hg availability in estuarine systems.