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Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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esulted in 91.7% survival (Horne and Dunson, 1995a). Exposure to Pb at high pH and low<br />

water hardness or low pH and high water hardness resulted in 75 and 41.7% survival,<br />

respectively (Horne and Dunson, 1995a). Similar results were reported <strong>for</strong> Jefferson<br />

salamanders during a 7-day exposure and wood frogs during 7- and 28-day exposures (Horne<br />

and Dunson, 1995c). In some cases, water hardness and pH in the absence <strong>of</strong> Pb have been<br />

shown to affect survival adversely. Mean acute survival <strong>of</strong> wood frogs and Jefferson<br />

salamanders exposed to low pH and low water hardness, in the absence <strong>of</strong> Pb, was 83.3 and<br />

91.7%, respectively. Mean chronic survival <strong>of</strong> wood frogs and Jefferson salamanders exposed to<br />

low pH and low water hardness, in the absence <strong>of</strong> Pb, was 79.2 and 41.7%, respectively (Horne<br />

and Dunson, 1995c).<br />

High Ca 2+ concentrations have been shown to protect against the toxic effects <strong>of</strong> Pb<br />

(Sayer et al., 1989; MacDonald et al., 2002; Hassler et al., 2004; Rogers and Wood, 2004).<br />

Calcium affects the permeability and integrity <strong>of</strong> cell membranes and intracellular contents<br />

(Sayer et al., 1989). As Ca 2+ concentrations decrease, the passive flux <strong>of</strong> ions (e.g., Pb) and<br />

water increases. At the lowest waterborne Ca 2+ concentration (150 µmol/L), Pb accumulation in<br />

juvenile rainbow trout (Oncorhynchus mykiss) branchials significantly increased as Pb<br />

concentration in water increased (Rogers and Wood, 2004). At higher Ca 2+ concentrations, Pb<br />

accumulation did not significantly increase with Pb concentration in water. This result<br />

demonstrates the protective effects <strong>of</strong> waterborne Ca 2+ and supports the suggestion that the Ca 2+<br />

component <strong>of</strong> water hardness determines the toxicity <strong>of</strong> Pb to fish (Rogers and Wood, 2004).<br />

Rogers and Wood (2004) reported that the uptake <strong>of</strong> Ca 2+ and Pb 2+ involves competitive<br />

inhibition <strong>of</strong> apical entry at lanthanum-sensitive Ca 2+ channels and interference with the function<br />

<strong>of</strong> the ATP-driven baso-lateral Ca 2+ pump. High mortality was reported in brown trout (Salmo<br />

trutta) fry exposed to Pb at a waterborne Ca 2+ concentration <strong>of</strong> 20 µmol/L, while negligible<br />

mortality was reported at the same Pb concentration but at a waterborne Ca 2+ concentration <strong>of</strong><br />

200 µmol/L (Sayer et al., 1989). Adverse effects to mineral uptake and skeletal development<br />

were observed in the latter test group (Sayer et al., 1989).<br />

The bioavailability <strong>of</strong> Pb and other metals that can be simultaneously extracted in<br />

sediments may be modified through the role <strong>of</strong> acid volatile sulfide (AVS) under anoxic<br />

conditions (Tessier and Campbell, 1987; Di Toro et al., 1992; Casas and Crecelius, 1994). The<br />

term AVS (iron sulfide is an example) refers to the fraction <strong>of</strong> the sediment that consists <strong>of</strong> a<br />

AX7-168

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