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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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there is little evidence that Pb accumulated in soils at these sites represents a threat to<br />

groundwaters or surface water supplies.<br />

The highest environmental risk <strong>for</strong> Pb in terrestrial ecosystems exists at sites within about<br />

50 km <strong>of</strong> smelters and other Pb-emitting industrial sites. Assessing the risks specifically<br />

associated with Pb is difficult, because these sites also experience elevated concentrations <strong>of</strong><br />

other metals and because <strong>of</strong> effects related to SO2 emissions. The concentrations <strong>of</strong> Pb in soils,<br />

vegetation, and fauna at these sites can be two to three orders <strong>of</strong> magnitude higher than in<br />

reference areas (see Sections AX7.1.2 and AX7.1.4.2). In the most extreme cases, near smelter<br />

sites, the death <strong>of</strong> vegetation causes a near-complete collapse <strong>of</strong> the detrital food web, creating a<br />

terrestrial ecosystem in which energy and nutrient flows are minimal. More commonly, stress in<br />

soil microorganisms and detritivores can cause reductions in the rate <strong>of</strong> decomposition <strong>of</strong> detrital<br />

organic matter. Although there is little evidence <strong>of</strong> significant bioaccumulation <strong>of</strong> Pb in natural<br />

terrestrial ecosystems, reductions in microbial and detritivorous populations can affect the<br />

success <strong>of</strong> their predators. Thus, at present, industrial point sources represent the greatest Pbrelated<br />

threat to the maintenance <strong>of</strong> sustainable, healthy, diverse, and high-functioning terrestrial<br />

ecosystems in the United States.<br />

AX7.2 AQUATIC ECOSYSTEMS<br />

AX7.2.1 Methodologies Used in Aquatic Ecosystem Research<br />

As discussed in previous sections, aerial deposition is one source <strong>of</strong> Pb deposition to<br />

aquatic systems. Consequently, to develop air quality criteria <strong>for</strong> Pb, consideration must be<br />

given to not only the environmental fate <strong>of</strong> Pb, but also to the environmental effects <strong>of</strong> Pb in the<br />

aquatic environment through consideration <strong>of</strong> laboratory toxicity studies and field evaluations.<br />

Perhaps the most straight<strong>for</strong>ward approach <strong>for</strong> evaluating the effects <strong>of</strong> Pb is to consider extant<br />

criteria <strong>for</strong> Pb in aquatic ecosystems, i.e., water and sediment quality criteria. A key issue in<br />

developing Pb water and sediment criteria that are broadly applicable to a range <strong>of</strong> water bodies<br />

is properly accounting <strong>for</strong> Pb bioavailability and the range in species sensitivities. This section<br />

summarizes how these criteria are derived, the types <strong>of</strong> toxicity studies considered, and key<br />

factors that influence the bioavailability <strong>of</strong> Pb in surface water and sediment to aquatic life.<br />

Because Pb in the aquatic environment is <strong>of</strong>ten associated with other metals (e.g., cadmium,<br />

AX7-106

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