4.7 Article

Study on antimony mobility in a contaminated shallow lake sediment using the diffusive gradients in thin films technique

Journal

CHEMOSPHERE
Volume 267, Issue -, Pages -

Publisher

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.chemosphere.2020.128913

Keywords

Antimony; Mobility; Lake sediment; DGT

Funding

  1. National Water Pollution Control and Management Technology Major Projects of China [2017ZX07206]
  2. Edanz Group China

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The study revealed that under the influence of pollutants discharged by textile plants, the concentrations of antimony compounds in the sediment of shallow lakes are relatively high. Antimony was found to be immobile in the oxygen-rich layer, but released along with other elements in the anoxic environment, depending on the redox conditions and the labile antimony content in the sediment. The mobility of antimony in shallow lakes and wetland sediments should be carefully considered when assessing the potential ecological risks.
Antimony is a priority environmental contaminant. Increasing attention is being paid to the behaviors and mobilities of the various Sb species in the environment. Sb speciation in the environment and the mobilities of Sb species at mining sites have been studied well, but Sb speciation and mobility in shallow lakes requires further study. Here, we studied Sb behavior in sediment of a shallow lake in the plain rivers network in Taihu Basin that suffers continual Sb inputs from textile plants. The diffusive gradients in thin films techniques (DGT) made of zirconium oxide based binding resin gel (ZrO-Chelex), agarose diffusive gel and polyvinylidene fluoride filter were deployed in water and sediment to obtain a high-resolution record in situ. The results indicated that (1) pollutants released by textile plants caused relatively high Sb(III), Sb(V) and organoantimony concentrations in the eutrophic shallow lake, (2) Sb was seldomly mobile in the oxic layer where Sb(III) was sorbed on Fe(III) oxides and gradually formed Fe-Sb complexes in the sediment, but in the anoxic environment (oxidation-reduction potential: 366 - -344 mv) Sb(V), Fe(II) and P (V) were simultaneously released to resupply the porewater, (3) the release of Sb from solid phase is decided by the redox condition, and the rate of release is dependent on the labile Sb content of the sediment. The mobility of Sb should be given sufficient attention when the potential ecological risk of metal(loid)s in shallow lakes and wetlands sediment are evaluated. (C) 2020 Elsevier Ltd. All rights reserved.

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