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

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and partitioning experiments. This technique has been particularly useful <strong>for</strong> quantifying the Kd,<br />

or partitioning ratio <strong>of</strong> Pb in the solid-to-liquid phase (Kd = [total solid-phase metal in mg kg Γ1 ] /<br />

[dissolved metal in mg L !1 ]). While the exact Kd value is a function <strong>of</strong> pH, organic matter<br />

content, substrate type, total metal burden, and concentrations <strong>of</strong> competing ligands, such studies<br />

typically show that Pb has very strong solid-phase partitioning. Partitioning ratios determined by<br />

DPASV generally range from 10 3 to 10 6 in soils in the typical pH range (Sauvé et al., 2000b).<br />

Aualiitia and Pickering (1987) used thin film ASV to compare the relative affinity <strong>of</strong> Pb <strong>for</strong><br />

different inorganic particulates. They reported that Mn(IV) oxides completely adsorbed the Pb,<br />

regardless <strong>of</strong> pH in the range <strong>of</strong> 3 to 9, and had the highest affinity <strong>for</strong> Pb in their study. The<br />

adsorption <strong>of</strong> Pb to pedogenic Fe-oxides, Al-hydroxides, clay minerals, and Fe ores was reported<br />

to be pH-dependent. Sauvé et al. (1998) used DPASV to study the effects <strong>of</strong> organic matter and<br />

pH on Pb adsorption in an orchard soil. They demonstrated that Pb complexation to dissolved<br />

organic matter (DOM) increased Pb solubility, and that 30 to 50% <strong>of</strong> the dissolved Pb was bound<br />

to DOM at pH 3 to 4, while >80% <strong>of</strong> the dissolved Pb was bound to DOM at neutral pH. They<br />

concluded that in most soils, Pb in solution would not be found as Pb 2+ but as bound to DOM.<br />

Sauvé et al. (2000a) compared the relative affinity <strong>of</strong> Pb 2+ <strong>for</strong> synthetic ferrihydrite, leaf<br />

compost, and secondary oxide minerals collected from soils. They reported that the inorganic<br />

mineral phases were more efficient at lowering the amount <strong>of</strong> Pb 2+ that was available in solution<br />

than the leaf compost. Glover et al. (2002) used DPASV in studying the effects <strong>of</strong> time and<br />

organic acids on Pb adsorption to goethite. They found that Pb adsorption to geothite was very<br />

rapid, and remained unchanged after a period <strong>of</strong> about 4 h. <strong>Lead</strong> desorption was found to be<br />

much slower. The presence <strong>of</strong> salicylate appeared to increase the amount <strong>of</strong> Pb that desorbed<br />

from goethite more so than oxalate.<br />

AX7.1.2.2 Tracing the Fate <strong>of</strong> Atmospherically-delivered <strong>Lead</strong> in Terrestrial Ecosystems<br />

Radiogenic Pb isotopes <strong>of</strong>fer a powerful tool <strong>for</strong> separating anthropogenic Pb from natural<br />

Pb derived from mineral weathering (Erel and Patterson, 1994; Erel et al., 1997; Semlali et al.,<br />

2001). This has been particularly useful <strong>for</strong> studying Pb in mineral soil, where geogenic Pb<br />

<strong>of</strong>ten dominates. The three radiogenic stable Pb isotopes ( 206 Pb, 207 Pb, and 208 Pb) have a<br />

heterogeneous distribution in the earth’s crust primarily because <strong>of</strong> the differences in the halflives<br />

<strong>of</strong> their respective parents ( 238 U, T1/2 = 4.7 × 10 9 year; 235 U, T1/2 = 0.7 × 10 9 year; 232 Th,<br />

AX7-31

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