Antimony retention and release from drained and waterlogged shooting range soil under field conditions

[Display omitted] •Sb in leachate from drained and waterlogged lysimeters was monitored for >2.5years.•Sb concentrations under drained conditions showed a strong seasonal fluctuation.•With the onset of waterlogging, Sb(V) was reduced to Sb(III).•This caused Sb in leachate to decrease from ∼80μgL−...

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Published inChemosphere (Oxford) Vol. 134; pp. 536 - 543
Main Authors Hockmann, Kerstin, Tandy, Susan, Lenz, Markus, Reiser, René, Conesa, Héctor M., Keller, Martin, Studer, Björn, Schulin, Rainer
Format Journal Article
LanguageEnglish
Published England Elsevier Ltd 01.09.2015
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Summary:[Display omitted] •Sb in leachate from drained and waterlogged lysimeters was monitored for >2.5years.•Sb concentrations under drained conditions showed a strong seasonal fluctuation.•With the onset of waterlogging, Sb(V) was reduced to Sb(III).•This caused Sb in leachate to decrease from ∼80μgL−1 to <5μgL−1. Many soils polluted by antimony (Sb) are subject to fluctuating waterlogging conditions; yet, little is known about how these affect the mobility of this toxic element under field conditions. Here, we compared Sb leaching from a calcareous shooting range soil under drained and waterlogged conditions using four large outdoor lysimeters. After monitoring the leachate samples taken at bi-weekly intervals for >1.5years under drained conditions, two of the lysimeters were subjected to waterlogging with a water table fluctuating according to natural rainfall water infiltration. Antimony leachate concentrations under drained conditions showed a strong seasonal fluctuation between 110μgL−1 in summer and <40μgL−1 in winter, which closely correlated with fluctuations in dissolved organic carbon (DOC) concentrations. With the development of anaerobic conditions upon waterlogging, Sb in leachate decreased to 2–5μgL−1 Sb and remained stable at this level. Antimony speciation measurements in soil solution indicated that this decrease in Sb(V) concentrations was attributable to the reduction of Sb(V) to Sb(III) and the stronger sorption affinity of the latter to iron (Fe) (hydr)oxide phases. Our results demonstrate the importance of considering seasonal and waterlogging effects in the assessment of the risks from Sb-contaminated sites.
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ISSN:0045-6535
1879-1298
1879-1298
DOI:10.1016/j.chemosphere.2014.12.020