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

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AX7. CHAPTER 7 ANNEX - ENVIRONMENTAL<br />

EFFECTS OF LEAD<br />

AX7.1 TERRESTRIAL ECOSYSTEMS<br />

AX7.1.1 Methodologies Used in Terrestrial Ecosystems Research<br />

The distribution <strong>of</strong> Pb throughout the terrestrial ecosystem, via aerial deposition, has been<br />

discussed throughout this document. Its further impacts on soil, sediment, and water provide<br />

numerous pathways that may promote unacceptable risk to all levels <strong>of</strong> biota. Stable isotopes <strong>of</strong><br />

Pb have been found useful in identifying sources and apportionment to various sources. One <strong>of</strong><br />

the key factors affecting assessment <strong>of</strong> risk is an understanding, and perhaps quantification, <strong>of</strong><br />

bioavailability. There<strong>for</strong>e, the bioavailability <strong>of</strong> Pb is a key issue to the development <strong>of</strong><br />

NAAQS. However, the discussion <strong>of</strong> all methods used in characterizing bioavailability is<br />

beyond the scope <strong>of</strong> this chapter. The following topics are discussed in this chapter.<br />

• <strong>Lead</strong> Isotopes and Apportionment<br />

• Methodologies to determine Pb speciation<br />

• <strong>Lead</strong> and the Biotic Ligand Model (BLM)<br />

• In situ methods to reduce Pb bioavailability<br />

AX7.1.1.1 <strong>Lead</strong> Isotopes and Apportionment<br />

Determination <strong>of</strong> the extent <strong>of</strong> Pb contamination from an individual source(s) and its<br />

impact are <strong>of</strong> primary importance in risk assessment. The identification <strong>of</strong> exposure pathway(s)<br />

is fundamental to the risk analysis and critical in the planning <strong>of</strong> remediation scenarios.<br />

Although societies have been consuming Pb <strong>for</strong> nearly 9,000 years, production <strong>of</strong> Pb in<br />

the United States peaked in 1910 and 1972, at approximately 750 and 620 kt/year, respectively<br />

(Rabinowitz, 2005). The diversity <strong>of</strong> potential Pb sources (fossil fuel burning, paint pigments,<br />

gasoline additives, solders, ceramics, batteries) and associated production facilities (mining,<br />

milling, smelting-refining) make fingerprinting <strong>of</strong> sources difficult. (See Chapter 2 and its<br />

Annex <strong>for</strong> additional in<strong>for</strong>mation on sources.) There<strong>for</strong>e, dealing with multiple sources (point<br />

and nonpoint), a reliable and specific fingerprinting technique is required. It has been well<br />

established (Sturges and Barrie, 1987; Rabinowitz, 1995) that the stable isotope composition <strong>of</strong><br />

AX7-1

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