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Modeling cadmium and nickel toxicity to earthworms with the free ion approach
Author(s) -
Qiu Hao,
Vijver Martina G.,
van Gestel Cornelis A.M.,
He Erkai,
Peijnenburg Willie J.G.M.
Publication year - 2014
Publication title -
environmental toxicology and chemistry
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.1
H-Index - 171
eISSN - 1552-8618
pISSN - 0730-7268
DOI - 10.1002/etc.2454
Subject(s) - lumbricus rubellus , earthworm , toxicity , chemistry , cadmium , environmental chemistry , biotic ligand model , eisenia andrei , soil water , ion , toxicology , ecotoxicology , biology , ecology , organic chemistry
The use of the free ion approach to quantify the toxic effects of Cd and Ni to the earthworms Lumbricus rubellus and Aporrectodea longa exposed in soils of different types was explored. Median lethal concentration (LC50) of Cd (expressed as the total concentration in soil) varied by approximately 11‐fold and 28‐fold for L. rubellus and A. longa , respectively. For Ni, these values were 50‐fold and 38‐fold, respectively. For the 2 earthworm species, no significant influence of cations (H + , Ca 2+ , Mg 2+ , K + , and Na + ) on Cd 2+ toxicity was observed, while Mg 2+ was found to significantly alleviate Ni 2+ toxicity. The free ion activity model, which is a special case of the free ion approach with no impact of cations, sufficiently described the variability in Cd 2+ toxicity across soils but failed in predicting Ni 2+ toxicity. The free ion approach, in which the protective effects of Mg 2+ were included, explained 89% and 84% of the variations in LC50{Ni 2+ } (expressed as free ion activity) for L. rubellus (log LC50{Ni 2+ } = 1.18log{Mg 2+ }−0.52) and A. longa (log LC50{Ni 2+ } = 0.51log{Mg 2+ }−2.16), respectively. Prediction error was within a factor of 2 for both Cd 2+ and Ni 2+ toxicity, indicating the applicability of the free ion approach for predicting toxicity of these 2 metals. Although extrapolation of the free ion approach across metals still needs more research efforts, this approach, as an alternative to the biotic ligand model, provides a feasible framework for site‐specific risk assessment. Environ Toxicol Chem 2014;33:438–446. © 2013 SETAC