Thermal release analysis of mercury species in contaminated soils was
performed by temperature controlled continuous heating of the samples
in a furnace coupled to an Atomic Absorption Spectrophotometer (AAS).
It was shown that this method allows the identification of different r
edox states of Hg-species through their characteristic releasing tempe
rature ranges. The method was applied to Hg-contaminated samples from
an inactive chlor-alkali production plant in former East Germany (GER)
, and from a gold mining area in Pocone, Mate Grosso, Brazil (BRA), as
well as synthetic soil samples obtained by spiking pre-heated soil ma
trices (GER and BRA) with the following mercury species: Hg-0, Hg2Cl2,
HgCl2, HgO and HgS. The samples GER, in general, frequently showed th
e presence of Hg2+ probably bound to humic substances, in the case of
samples with higher total carbon content. Only in highly contaminated
samples (>3000 ppm of mercury) was HgO the predominant species. The sa
mples BRA more frequently showed the presence of mercury species in th
e lower oxidation states, i.e. Hg1+ in combination with Hg-0. The meth
od allows observing changes in Hg-speciation in the samples with time,
mainly changes among the oxidation states Hg-0, Hg1+ and Hg2+. The tr
eated GER matrix showed a stronger tendency to oxidise Hg-species than
the BRA treated matrix, in which only added HgO is partially oxidised
to Hg1+ and Hg2+. In contrast, the BRA matrix showed a pronounced ten
dency to reduce spiked Hg2+ to Hg1+. This may be the reason for the pr
esence of Hg1+ in the majority of original BRA samples. The method app
ears to be very useful to study speciation of mercury and its dynamics
. It can be used as a tool for monitoring mercury oxidation states and
/or reactions of mercury in soils.