4.7 Article

Role of Fe dynamic in release of metals at Rio Doce estuary: Unfolding of a mining disaster

期刊

MARINE POLLUTION BULLETIN
卷 166, 期 -, 页码 -

出版社

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.marpolbul.2021.112267

关键词

Samarco mining disaster; Redox processes; Trace metals; Environmental contamination; Fe oxides

资金

  1. Fundacao de Amparo do Espirito Santo (FAPES Rio Doce) [77683544/2017]
  2. Coordenacao de Aperfeicoamento de Pessoal de Nivel Superior CAPES [001]
  3. CNPq [AFB: 301161/2017-8, 305996/2018-5]
  4. Sao Paulo Research Foundation (FAPESP) [2018/04259-2, 2019/17413-2, 2019/02855-0, 2019/19987-6, 2018/08408-2]
  5. Fundacao Carlos Chagas Filho de Amparo a Pesquisa do Estado do Rio de Janeiro (GNN, JCNE Grant) [E-26/202.757/2019]
  6. Xunta de GaliciaConselleria de Educacion e Ordeancion Universitaria de Galicia (consolidation of competitive groups of investigation) [GRC GI 1574]
  7. CRETUS strategic group [AGRUP2015/02]
  8. USDA NIFA Hatch Project [CA-R-ENS-5151-H]
  9. Fulbright Award - J. William Fulbright Commission

向作者/读者索取更多资源

The dynamic role of Fe oxyhydroxides on metal bioavailability in the Rio Doce estuary was studied after the largest mining disaster in the world in 2015. Results showed that Fe oxyhydroxides in estuarine soils underwent reductive dissolution due to organic matter inputs from plant colonization on deposited tailings, leading to significant decreases in Fe and total metal contents in the soil. This suggests a potential chronic contamination in the estuary and highlights the aggravating scenario for the following years due to the increasing dominance of poorly crystalline Fe oxyhydroxides.
The role of Fe oxyhydroxides dynamic on metal bioavailability was studied in the Rio Doce estuary after the largest mining disaster in the world. Soon after the disaster in 2015, metals were associated with Fe oxyhydroxides under a redox-active estuarine environment. Our results indicate that organic matter inputs from plant colonization on deposited tailings over estuarine soils led to a reductive dissolution of Fe oxyhydroxides within two years. Soil pseudo-total Fe content decreased by 70% between 2015 and 2017, while the total metal contents (Cr, Cu, Ni, Pb, and Zn) decreased by 79% in the soil. The losses of Fe and metals coupled to changes in Fe oxides crystallinity reveal a future ephemeral control of Fe oxyhydroxides over metal immobilization. Our results suggest a potential chronic contamination at the estuary and points to an aggravating scenario for the following years due to the increasing dominance of poorly crystalline Fe oxyhydroxides.

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