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

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Source<br />

Although the source <strong>of</strong> a metal is not directly related to bioavailability, it plays an<br />

important role in risk assessment with the evaluation <strong>of</strong> metal (1) pathways, (2) background,<br />

and (3) apportionment. It is important to understand a metal’s pathway be<strong>for</strong>e any remedial<br />

action can be taken; otherwise, recontamination <strong>of</strong> the primary pathway and reexposure can<br />

occur. Knowledge <strong>of</strong> background is important, as an action level cannot be established below<br />

natural background levels.<br />

Plants<br />

When considering the bioavailability <strong>of</strong> a metal to plants from soils and sediments, it is<br />

generally assumed that both the kinetic rate <strong>of</strong> supply and the speciation <strong>of</strong> the metal to either the<br />

root or shoot are highly important. In soils and sediments generally, only a small volume <strong>of</strong><br />

water is in contact with the chemical <strong>for</strong>m, and although the proportion <strong>of</strong> a metal’s<br />

concentration in this pore water to the bulk soil/sediment concentration is small, it is this phase<br />

that is directly available to plants. There<strong>for</strong>e, pore water chemistry (i.e., metal concentration as<br />

simple inorganic species, organic complexes, or colloid complexes) is most important.<br />

Tools currently used <strong>for</strong> metal speciation <strong>for</strong> plants include (1) in-situ measurements<br />

using selective electrodes (Gundersen et al., 1992; Archer et al., 1989; Wehrli et al., 1994);<br />

(2) in-situ collection techniques using diffusive equilibrium thin films (DET) and diffusive<br />

gradient thin films (DGT) followed by laboratory analyses (Davison et al., 1991, 1994; Davison<br />

and Zhang, 1994; Zhang et al., 1995); and (3) equilibrium models ( SOILCHEM) (Sposito and<br />

Coves, 1988).<br />

AX7.1.1.3 Tools <strong>for</strong> Bulk <strong>Lead</strong> Quantification and Speciation<br />

Bulk Quantification<br />

The major analytical methods most commonly used <strong>for</strong> bulk analyses outlined in the 1986<br />

<strong>Lead</strong> ACQD included:<br />

• Atomic Absorption Spectrometry (AAS)<br />

• Emission Spectrometry (Inductively coupled plasma/atomic emission spectrometry)<br />

• X-ray Fluorescence (XRF)<br />

• Isotope Dilution Mass Spectrometry (ID/MS)<br />

AX7-9

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