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Chromium - The Risk Assessment Information System

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Surrogate<br />

Receptor Group<br />

Avian herbivore<br />

(dove)<br />

Avian ground<br />

insectivore<br />

(woodcock)<br />

Avian carnivore<br />

(hawk)<br />

Table 5.2 Calculation of the Avian Eco-SSLs for Trivalent <strong>Chromium</strong><br />

TRV for Trivalent<br />

<strong>Chromium</strong><br />

(mg dw/kg bw/d) 1<br />

Food Ingestion<br />

Rate (FIR) 2<br />

(kg dw/kg<br />

bw/d)<br />

Soil Ingestion<br />

as Proportion<br />

of Diet (P s) 2<br />

2.66 0.190 0.139<br />

2.66 0.214 0.164<br />

2.66 0.0353 0.057<br />

Concentration of<br />

<strong>Chromium</strong> in Biota<br />

Type (i) 2,3<br />

(B i)<br />

(mg/kg dw)<br />

B i = 0.041 * Soil j<br />

where i = plants<br />

B i = 0.306 * Soil j<br />

where i = earthworms<br />

ln(B i) = 0.7338 *<br />

ln(Soil j) - 1.4599<br />

where i = mammals<br />

Eco-SSL<br />

(mg/kg dw) 4<br />

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

2 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 <strong>Chromium</strong> 9<br />

April 2008<br />

78<br />

26<br />

780

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