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in<strong>for</strong>mation summarized in USEPA (1986). The NDEP has chosen to utilize <strong>the</strong> more recent<br />

methodology <strong>for</strong> assessing ARR proposed in Berman <strong>and</strong> Crump (2003) <strong>and</strong> fully described in<br />

<strong>the</strong> guidance <strong>document</strong>.<br />

Cadmium<br />

Because IRIS provides different oral RfDs <strong>for</strong> cadmium in water <strong>and</strong> in foods, <strong>the</strong> BCL <strong>for</strong><br />

cadmium in water is based on <strong>the</strong> oral RfD <strong>for</strong> water, <strong>and</strong> <strong>the</strong> BCL <strong>for</strong> soil ingestion is based on<br />

<strong>the</strong> RfD <strong>for</strong> food.<br />

4,4-Dichlorobenzil<br />

In <strong>the</strong> absence of 4,4-dichlorobenzil toxicity criteria from st<strong>and</strong>ard hierarchy of sources, NDEP<br />

has provided interim guidance on this chemical (NDEP, 2009b). This guidance may be found at<br />

http://ndep.nv.gov/bmi/docs/090115_dichlorobenzil.pdf <strong>and</strong> provides an interim RfD <strong>for</strong><br />

dichlorobenzil of 3.0 x 10 -4 mg/kg-d.<br />

Hexachlorocyclohexane (HCH)<br />

The NDEP has adopted a threshold dose value <strong>for</strong> alpha-, beta-, <strong>and</strong> gamma-HCH <strong>for</strong> use in<br />

quantifying potential human health risks at <strong>the</strong> BMI Complex (Integral 2011a, b, <strong>and</strong> c). The<br />

criteria <strong>document</strong>s supporting this decision are provided on <strong>the</strong> NDEP BMI Complex website<br />

(http://ndep.nv.gov/bmi/<strong>technical</strong>.htm). These toxicity values have been incorporated into <strong>the</strong><br />

BCLs <strong>for</strong> <strong>the</strong>se compounds.<br />

Essential Nutrients; Specifically Calcium, Potassium, <strong>and</strong> Sodium<br />

Calcium, potassium, <strong>and</strong> sodium are essentially nutrients <strong>and</strong> are on <strong>the</strong> Generally Recognized<br />

As Safe (GRAS) list of <strong>the</strong> Food <strong>and</strong> Drug Administration (FDA, 2011).<br />

“GRAS exemptions are granted <strong>for</strong> substances that are generally recognized, among<br />

experts qualified by scientific training <strong>and</strong> experience to evaluate <strong>the</strong>ir safety, as having<br />

been adequately shown through scientific procedures …to be safe under <strong>the</strong> conditions of<br />

<strong>the</strong>ir intended use.” FDA, 2011<br />

“There is no evidence in <strong>the</strong> available in<strong>for</strong>mation on [substance] that demonstrates, or<br />

suggests reasonable grounds to suspect, a hazard to <strong>the</strong> public when <strong>the</strong>y are used at<br />

levels that are now current or might reasonably be expected in <strong>the</strong> future.” FDA, 2011<br />

There<strong>for</strong>e, <strong>the</strong>se three elements do not need to be included in a risk assessment <strong>for</strong> potential<br />

human health impacts unless <strong>the</strong>y are present in a compound that is a regulated chemical agent<br />

<strong>and</strong>/or in compounds present at concentrations that may create a health hazard through<br />

physical/chemical properties (e.g., extremely low or high pH having caustic potential).<br />

Lead<br />

The residential soil value <strong>for</strong> lead is based on <strong>the</strong> Integrated Exposure Uptake Biokinetic<br />

(IEUBK) Model <strong>for</strong> lead in children developed using default parameters (USEPA, 1994). More<br />

in<strong>for</strong>mation on this model <strong>and</strong> o<strong>the</strong>r lead risk assessment guidance can be found at<br />

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