1997
DOI: 10.1016/s0269-7491(97)00014-6
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Organism-induced accumulation of iron, zinc and arsenic in wetland soils

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Cited by 212 publications
(72 citation statements)
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“…Other plant-mediated processes of arsenic immobilisation at the soil-root interface involve pH reduction and oxidation of the root environment by O 2 released from roots. Doyle & Otte (1997) found accumulation of arsenic on iron plaque in the oxidised rhizosphere of salt marsh plants that may provide effective immobilization and detoxification mechanism. d) Phytovolatilization -Phytovolatilization is the use of plants to volatilize pollutants and has been demonstrated for Hg and Se.…”
Section: Phytoremediationmentioning
confidence: 99%
“…Other plant-mediated processes of arsenic immobilisation at the soil-root interface involve pH reduction and oxidation of the root environment by O 2 released from roots. Doyle & Otte (1997) found accumulation of arsenic on iron plaque in the oxidised rhizosphere of salt marsh plants that may provide effective immobilization and detoxification mechanism. d) Phytovolatilization -Phytovolatilization is the use of plants to volatilize pollutants and has been demonstrated for Hg and Se.…”
Section: Phytoremediationmentioning
confidence: 99%
“…Salt marshes are natural deposits of heavy metals in an estuarine system (Caçador et al 1996;Doyle and Otte 1997). When located near polluted areas, these ecosystems receive large amounts of pollutants from industrial and urban wastes, which either drift downstream with the river flow or are dumped directly from nearby industrial and urban areas (Reboreda and Caçador 2007).…”
Section: Introductionmentioning
confidence: 99%
“…The bioturbation of sediments by large benthic invertebrates alters sediment redox chemistry by mixing pre-stratified zones in the sediment, and increasing the penetration of electron acceptors such as dissolved O 2 , NO 3 -and SO 4 2-into anoxic sediments (Aller et al, 2001;Granéli, 1979;Matisoff et al, 1985;Pischedda et al, 2008; Volkenborn et al, 2010). Redox changes can alter metal binding affinities between the solid and dissolved phases, significantly modifying the speciation and bioavailability of most metals in sediments (De Jonge et al, 2012;Doyle and Otte, 1997;Granberg et al, 2008). The concentration of AVS has a major influence on metal bioavailability, and for sediments containing a molar excess of acid volatile sulfide (AVS) over simultaneously extractable metals (SEM, ΣCd, Cu, Ni, Pb, Zn), it is predicted that the porewater concentrations of these metals will be negligible and should not cause direct toxicity to benthic organisms Hansen et al, 2005;Lawrence et al, 1982).…”
mentioning
confidence: 99%