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TitreEffect of pH and environmental ligands on accumulation and toxicity of Ni2+ to Lemna minor
AuteurGopalapillai, Y; Vigneault, B; Hale, B
SourceEnvironmental Chemistry vol. 9, no. 6, 2012 p. 547-557, https://doi.org/10.1071/EN12078
Année2012
Séries alt.Secteur des sciences de la Terre, Contribution externe 20120326
ÉditeurCSIRO
Documentpublication en série
Lang.anglais
DOIhttps://doi.org/10.1071/EN12078
Mediapapier; numérique; en ligne
Formatspdf
Sujetsvégétation; analyse environnementales; etudes de l'environnement; effets sur l'environnement; acidité; réseaux de pH; contamination des métaux lourds; substances polluantes; pollution; pollution de l'eau souterraine; nickel; géologie de l'environnement
Illustrationsgraphs; tables; plots
ProgrammeGestion du programme, Géosciences de l'environnement
Résumé(disponible en anglais seulement)
Effects of water chemistry and metal speciation on metal uptake and toxicity to aquatic plants such as Lemna minor are not fully understood. The present study examined the effect of pH and environmental ligands (dissolved organic carbon (DOC) and mining related flotation ligands diethylenetriamine (DETA), triethylenetetramine (TETA), sodium isopropyl xanthate), on Ni toxicity to L. minor. Exposure and tissue residue toxicity thresholds were assessed to validate the use of a Biotic Ligand Model (BLM) or a Tissue Residue Approach (TRA) as a framework for predicting Ni toxicity. An increase in the activity of H+ non-linearly decreased the toxicity of free Ni ion activity, whereas Ni accumulation kinetics indicated that the mechanism of Ni2+ and H+ interaction was not competitive inhibition as expected by the BLM framework. The effect of DOC on the toxicity of total Ni concentration was relatively small (toxicity decreased by less than a factor of 2) and was explained solely by the complexation of Ni2+ by DOC. Alternatively, the protective effect of flotation ligands (DETA and TETA) was much less than expected based on estimated Ni complexation. Overall, a TRA model was directly applicable in the presence of organic ligands but not to varying pH, whereas a BLM-type model was applicable with changes in pH and DOC but not in the presence of the lesser studied flotation ligands. Such mechanistic information is essential for the development of reliable Ni toxicity models that would aid in risk assessment and regulation of Ni in the environment, particularly in mining-affected regions.
GEOSCAN ID292077