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

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TRV. The toxicity data that were reviewed to develop the TRV are presented in the following<br />

subsections.<br />

Representative avian and mammalian wildlife species were selected <strong>for</strong> modeling Pb<br />

exposures to wildlife with different diets and calculating the Eco-SSL. The avian species<br />

selected were dove (herbivore), woodcock (insectivore), and hawk (carnivore). The mammalian<br />

species selected were vole (herbivore), shrew (insectivore), and weasel (carnivore). The lowest<br />

<strong>of</strong> the three back-calculated soil concentrations, which resulted in an HQ = 1, was selected as the<br />

Eco-SSL. For Pb, the lowest values were <strong>for</strong> the insectivorous species <strong>of</strong> bird and mammal.<br />

Avian Consumers<br />

Effects on birds observed in studies conducted since the 1986 <strong>Lead</strong> AQCD (U.S.<br />

Environmental Protection Agency, 1986a) are similar to those reported previously: mortality,<br />

changes in juvenile growth rate and weight gain, effects on various reproductive measures, and<br />

changes in behavior (U.S. Environmental Protection Agency, 2005b). Reproductive effects<br />

following Pb exposure included declines in clutch size, number <strong>of</strong> young hatched, and number <strong>of</strong><br />

young fledged as well as decreased fertility or eggshell thickness. Few significant reproductive<br />

effects have been reported in birds at Pb concentrations below 100 mg/kg in the diet<br />

(Scheuhammer, 1987).<br />

The literature search completed <strong>for</strong> Eco-SSL development identified 2,429 papers <strong>for</strong><br />

detailed review <strong>for</strong> either avian or mammalian species, <strong>of</strong> which 54 met the minimum criteria <strong>for</strong><br />

further consideration <strong>for</strong> avian Eco-SSL development (U.S. Environmental Protection Agency,<br />

2005b). The 106 toxicological data points <strong>for</strong> birds that were further evaluated included<br />

biochemical, behavioral, physiological, pathological, reproductive, growth, and survival effects.<br />

Growth and reproduction data were used to derive the Eco-SSL (Table AX7-1.3.3;<br />

Figure AX7-1.3.1). The geometric mean <strong>of</strong> the NOAELs was calculated as 10.9 mg/kg-day,<br />

which was higher than the lowest bounded LOAEL (the term “bounded” means that both a<br />

NOAEL and LOAEL were obtained from the same study). There<strong>for</strong>e, the highest bounded<br />

NOAEL that was lower than the lowest bounded LOAEL <strong>for</strong> survival, growth, or reproduction<br />

(1.63 mg Pb/kg bw-day) was used as the TRV (U.S. Environmental Protection Agency, 2005b).<br />

The TRV was used to back-calculate the Eco-SSL <strong>of</strong> 11 mg/kg soil <strong>for</strong> avian species (U.S.<br />

AX7-65

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