Abstract

A survey of the reactive and total Hg concentrations in surface waters and of the quantity of particulate organic carbon (POC) and dissolved organic carbon (DOC), were performed along a transect from the major rivers mouths and mangrove dominated areas to the open bay waters of Sepetiba Bay, SE Brazil. The objective of the survey was to evaluate changes in Hg reactivity during the transport along the estuarine gradient. Reactive Hg concentrations were lowest in open bay waters, (0.09 ± 0.06 ng L-1), followed by river influenced waters (0.19 ± 0.06 ng L-1), and mangrove (0.29 ± 0.02 ng L-1). Total Hg concentrations were lowest in open bay (0.38 ± 0.20 ng L-1), followed by mangrove waters (0.56 ± 0.01 ng L-1), and river influenced waters (0.99 ± 0.29 ng L-1). The percentages of reactive Hg relative to the total Hg concentrations were lowest in river influenced waters, (20.7%), followed by open bay waters (31.2%), and mangrove waters (53.2%). The percent of reactive Hg to the total Hg concentrations showed a significant negative correlation with the total Hg concentrations following a potential equation. No relationship between reactive Hg concentrations and POC, salinity or pH were found, however, reactive Hg correlates significantly with DOC, suggesting that organo-complexes, rather than chloro-complexes, are the major controllers of Hg reactivity, and eventually bioavailability in Sepetiba Bay.

Highlights

  • Mercury presents a non-conservative behavior during estuarine mixing, due to its high reactivity

  • The objective of the survey was to evaluate changes in Hg reactivity and organic matter characteristics during the transport along the estuarine gradient, from river mouths and from mangrove, to open bay waters, and eventually explain the results found on fish Hg concentrations[12]

  • Reactive Hg concentrations were lowest in open bay waters, ranging from 0.04 to 0.22 ng L-1, followed by river influenced waters, ranging from 0.13 to 0.26 ng L-1

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Summary

Introduction

Mercury presents a non-conservative behavior during estuarine mixing, due to its high reactivity. Hg may undergo strong speciation changes, resulting in different biovailability[1,2]. The study of Hg concentrations and of its variability in coastal waters has received large attention due to its direct relationship with fish. Hg availability to biota may change due to changes in salinity regime[3], redox potential and sulfide concentration[4], properties of the dissolved organic matter[5], photochemical reactions[6], and sediment ressuspen-sion[7]. Previous studies on the partitioning of Hg in surface estuarine waters have shown that from 50% to 80% of

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