ESTIMATING THE POTENTIAL FOR REES TO IMPACT AQUATIC ORGANISMS. James McGeer1, Alex Loveridge1, O. Vukov1, Che Lu1, J. Ford1, H. Leonard1, A. Carvajal2 and D Scott Smith2 1 Dept of Biology; 2 Dept. of Chemistry and Biochemistry Wilfrid Laurier University, Waterloo, ON. ABSTRACT The toxicological understanding of rare earth elements (REEs) in the aquatic environment is very limited. This can result in excessively conservative approaches when establishing discharge objectives and water quality guidelines/criteria. There currently are no water quality guidelines or criteria for REEs. The overall objectives of this research are to contribute towards the understanding of the potential impacts of REEs in aquatic environments and to determine the influence of water chemistry on toxicological responses. In this particular project the toxicity modifying influences of cationic competition (Ca, Mg and Na) and dissolved organic matter (DOM) on the toxicity of Ce, Sm, Dy and Tm to fish (e.g. rainbow trout) and sensitive invertebrates (e.g. Hyalella azteca and Daphnia pulex) was assessed with the goal of developing toxicity prediction models. Standard methods (Environment Canada) were used for culture and testing which was done in intermediate hardness waters (60 mg/L CaCO 3, pH 7.2, Ca 0.5 mM, Mg 0.15 mM). The protective effect of cationic competition was tested with Ca (0.1 to 2.0 mM), Mg (0.03 to 0.5 mM) and Na (0.1 to 2.0 mM) and in general Ca and sometimes Na mitigated the impact of REEs but Mg generally did not. As well, DOM reduced toxicity of all the elements tested. The pH of test solutions had a significant influence on toxicity with low pH resulting reduced Dy toxicity. Geochemical equilibrium modeling approaches such as the biotic ligand model were applied to simultaneously estimate toxicity under different water chemistry conditions. This research was funded by NSERC and Environment Canada via the Strategic Grants Program. 50 60 (B) (A) 50 LC50 Dy3+ (nM) LC50 Dy3+ (nM) 40 30 20 10 40 30 20 10 0 0 0 200 400 600 800 1000 1200 1400 1600 Ca2+ 0 500 1000 Na+ (µM) 1500 2000 2500 (µM) Figure 1 – Effect of Ca2+ (left) and Na+ (right) concentration on the acute toxicity of Dy3+ to the aquatic invertebrate Hyalella azteca. Symbols show the 96 h LC50 value (the Dy3+ concentration that induced 70 5000 50% Dy3+ concentrations were estimated from (C) lethality over 96 h) with 95% confidence intervals. (D) measured 60 dissolved Dy concentrations using the Windermere Humic Aqueous Model (WHAM ver 7.02). 4000 50 LC50 Dy3+ (nM) LC50 Dy3+ (nM) KEYWORDS REEs, aquatic, toxicity, water quality, biotic ligand model 3000 40 30 20 2000 1000 10 0 0 0 100 200 Mg2+ 300 (µM) 400 500 0 50 100 150 H+ 200 (µM) 250 300 350