4.7 Article

Soil cadmium mobilisation by dissolved organic matter from soil amendments

Journal

CHEMOSPHERE
Volume 271, Issue -, Pages -

Publisher

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.chemosphere.2021.129536

Keywords

Cadmium mobility; Dissolved organic matter quality; Soils; Organic matter amendments; Colloids; Speciation

Funding

  1. New Zealand Ministry of Business Innovation and Employment (Smart Ideas) [UOWX1804]
  2. Lincoln University Doctoral Scholarship
  3. New Zealand Ministry of Business, Innovation & Employment (MBIE) [UOWX1804] Funding Source: New Zealand Ministry of Business, Innovation & Employment (MBIE)

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The release of dissolved organic matter (DOM) from Cd contaminated soils is linked to the mobilisation of Cd-DOM complexes, with organic matter-rich soil amendments exacerbating this process. The quantity and quality of DOM determine the proportion of dissolved Cd that forms mobile complexes, affecting Cd transport from contaminated soils. Structural properties of DOM play a key role in the mobilisation of Cd from contaminated soils, as observed in this study.
Dissolved organic matter (DOM) release from Cd contaminated soils been linked to mobilisation of the metal as Cd-DOM complexes and this may be exacerbated by organic matter-rich soil amendments. The quantity and quality of the DOM can determine the proportion of dissolved Cd that partitions to mobile complexes and their stability and, thus, the potential for Cd transport from contaminated soils. The aim of this work was to examine differences in Cd mobilisation from soils to which different types of soil amendments/conditioners have been applied and the importance of DOM characteristics in determining the extent to which this can happen. Three soils were spiked with Cd to 2 mg kg(-1), allowed to equilibrate and then treated with compost and peat. These soils and an untreated subsample of each soil were then adjusted to three different pHs: 5.6, 6.4 and 7.4, using lime. The amount of Cd mobilised from each soil was tested using a column leaching experiment. Ultrafiltration and speciation modelling were used to determine amounts of Cd as DOM-complexed, truly dissolved (< 5 kDa) and colloidal species, while DOM quality was assessed using UV-Vis and fluorescence spectroscopy. Most colloidal Cd was mobilised from the compost treated soils (50%-60%), followed by the peat treated soils (20-44%). The relationships between colloidal Cd, DOC concentration and soil pH, together with the spectroscopic and modelling results showed that structural properties of DOM are an important factor in mobilising Cd from contaminated soils. (C) 2021 Elsevier Ltd. All rights reserved.

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