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Surrogate<br />

Receptor Group<br />

Mammalian<br />

herbivore (vole)<br />

Mammalian ground<br />

insectivore (shrew)<br />

Mammalian<br />

carnivore (weasel)<br />

TRV for<br />

Lead<br />

(mg dw/kg<br />

bw/d) 1<br />

Table 6.2 Calculation of the Mammalian Eco-SSLs for Lead<br />

Food Ingestion<br />

Rate (FIR) 2<br />

(kg dw/kg bw/d)<br />

Soil Ingestion as<br />

Proportion of<br />

Diet (P s) 2<br />

4.70 0.0875 0.032<br />

4.70 0.209 0.030<br />

4.70 0.130 0.043<br />

Concentration of<br />

Lead in Biota Type<br />

(i) 2,3<br />

(B i)<br />

(mg/kg dw)<br />

ln(B i) = 0.561 *<br />

ln(Soil j) - 1.328<br />

where i = plants<br />

ln(B i) = 0.807 *<br />

ln(Soil j) - 0.218<br />

where i = earthworms<br />

ln(B i) = 0.4422 *<br />

ln(Soil j) + 0.0761<br />

where i = mammals<br />

Eco-SSL<br />

(mg/kg dw) 4<br />

1 The process for derivation of wildlife TRVs is described in Attachment 4-5 of U.S. EPA (2003).<br />

2<br />

Parameters (FIR, Ps, Bi values, regressions) are provided in U.S. EPA (2003) Attachment 4-1 (revised February 2005).<br />

3<br />

Bi = Concentration in biota type (i) which represents 100% of the diet for the respective receptor.<br />

4 HQ = FIR * (Soilj * Ps + Bi) / TRV) solved for HQ=1 where Soilj = Eco-SSL (Equation 4-2; U.S. EPA, 2003).<br />

NA = Not Applicable<br />

Eco-SSL for Lead 19<br />

March 2005<br />

1200<br />

56<br />

460

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