A simple field method to determine mercury volatilization from soils.
BACKGROUND
Estimations of gaseous mercury volatilization from soils are often complex, stationary and expensive. Our objective was to develop a mobile and more simple, easy to handle and more cost-effective field method allowing rapid estimates of potential Hg emissions from soils.


METHODS
The study site is located in Germany, about 100 kilometers south-westerly of Berlin and influenced by the river Elbe and its tributary Saale river. The site is representative for a lot of other floodplain locations at the river Elbe and highly polluted with Hg and other heavy metals. For our study we developed a system consisting of a glass chamber gas, two gold traps, a battery operated pump and a gas meter. Adsorbed total gaseous mercury (TGM) in the gold traps was determined by use of atomic absorption spectrometry (AAS).


CONCLUSIONS
In contrast to the common used flux chambers we designed a chamber without inlet and named it gas suck up chamber (GSC). TGM fluxes determined with the GSC showed a very close linear correlation (r = 0.993) between the TGM content in the gold traps and the corresponding pumped gas volume. The TGM adsorbed, increased proportional with increasing gas volume indicating homogenous concentrations of gaseous mercury in the soil air sucked. In contrast to the commonly used dynamic flux chamber with the aim of precisely measuring actual fluxes of Hg from a defined soil area, we focused on developing of a measurement system which will allow rapid estimates of potential Hg emissions of a site. Earlier research at the study site indicated a high potential for releasing volatile Hg from the soil to the atmosphere. Indeed, due to the high Hg content of the soil significant amounts of TGM could be detected and no shortage was reached.


CONCLUSIONS
Our initial measurements are still too few in number neither to generalize the achieved results nor discuss controlling factors and processes. However, we are pleased to communicate that the developed GSC is well suited to become an effective sampling set up to rapidly estimate the magnitude of Hg volatilization from soils.


CONCLUSIONS
Further measurements at other polluted locations are necessary to verify the GSC method. In addition the use of a mercury analyzer instead of gold traps is planned for faster risk assessments.
Böhme
Frank
F
UFZ Centre for Environmental Research Leipzig-Halle, Department of Soil Science, Theodor-Lieser-Strasse 4, 06120 Halle/Saale, Germany. frank.boehme@ufz.de
Rinklebe
Jörg
J
Stärk
Hans-Joachim
HJ
Wennrich
Rainer
R
Mothes
Sibylle
S
Neue
Heinz-Ulrich
HU
D004784:Environmental Monitoring / Q000379:methods*; D005740:Gases; D008628:Mercury / Q000032:analysis* / Q000737:chemistry; D012680:Sensitivity and Specificity; D012989:Soil Pollutants / Q000032:analysis*; D014835:Volatilization
D005740:Gases; D012989:Soil Pollutants; D008628:Mercury