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

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

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Sopper, 1989). The history is complicated, however, by the land use history <strong>of</strong> the area.<br />

Logging and fire in the early 20th century may also have played a role in the changes in the<br />

terrestrial ecosystems (Jordan, 1975). Extensive logging occurred after the smelters began<br />

operation, suggesting that some <strong>of</strong> the logging may have been salvage logging in affected areas.<br />

Regardless, the smelter emissions appear to have inhibited the regrowth <strong>of</strong> ecosystems compared<br />

to those in nearby unaffected areas. As in Anaconda, MT, the changes in the structure and<br />

function <strong>of</strong> the Palmerton ecosystem changed its suitability as a habitat <strong>for</strong> fauna that would<br />

normally inhabit the area. Storm et al. (1994) did not find amphibians or common invertebrates<br />

in two study sites nearest to the smelters. In the larger study area, they documented elevated<br />

concentrations <strong>of</strong> Pb, Cd, Cu, and Zn in tissues <strong>of</strong> species ranging in size from red-backed<br />

salamanders (Pletheron cenereus) to white-tailed deer (Odocoilius virginianus).<br />

Metal pollution around a Pb-Zn smelter near Bristol, England has not resulted in the loss<br />

<strong>of</strong> oak woodlands within 3 km <strong>of</strong> the smelter, despite significant accumulation <strong>of</strong> Pb, Cd, Cu,<br />

and Zn in soils and vegetation (Martin and Bullock, 1994). However, the high metal<br />

concentrations have favored the growth <strong>of</strong> metal-tolerant species in the woodland.<br />

The effects <strong>of</strong> Pb and other chemical emissions on terrestrial ecosystems near smelters<br />

and other industrial sites decrease downwind from the source. Several studies using the soil<br />

burden as an indicator have shown that much <strong>of</strong> the contamination occurs within a radius <strong>of</strong><br />

20 to 50 km around the emission source (Miller and McFee, 1983; Martin and Bullock, 1994;<br />

Galbraith et al., 1995; Spurgeon and Hopkin, 1996a; see also Section AX7.1.2). For example,<br />

the concentration <strong>of</strong> Pb in <strong>for</strong>est litter declined downwind from a Pb-Zn smelter near Bristol,<br />

UK, from 2330 to 3050 ppm in a stand 2.9 km from the smelter to 45 to 110 ppm in a stand<br />

23 km from the smelter (Martin and Bullock, 1994). Thus, while sites near point sources <strong>of</strong> Pb<br />

may experience pr<strong>of</strong>ound effects on ecosystem structure and function, the extent <strong>of</strong> those effects<br />

is limited spatially. Elevated metal concentrations around smelters have been found to persist<br />

despite significant reductions in emissions (Hrsak et al., 2000). Most terrestrial ecosystems are<br />

far enough from point sources that long-range Pb transport is the primary mechanism <strong>for</strong> Pb<br />

inputs.<br />

AX7-97

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