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Guidance for Conducting Risk Assessments and Related Risk ...

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• document the magnitude of risk <strong>and</strong> the primary causes of that risk, <strong>and</strong><br />

• define Remedial Goal Options (RGOs).<br />

Note: During the preparation of the baseline human health risk assessment, newly acquired data will be<br />

incorporated in the watershed database <strong>and</strong> the modified data set will again be compared to risk-based<br />

PRGs. This comparison may result in the identification of early actions (including removals <strong>and</strong> interim<br />

actions) in order to reduce risks <strong>and</strong>/or accelerate the clean-up process.<br />

Figure 2<br />

Scoping Workshop<br />

Site Characterization<br />

Establish Remedial<br />

Goal Options (RGOs)<br />

Figure 4<br />

2.2.3 Feasibility Study<br />

Early Action<br />

(e.g. removal,<br />

interim action<br />

The Project Scoping Workshop <strong>and</strong> <strong>Risk</strong> Assessment<br />

• compile existing data,<br />

• develop a conceptual site model,<br />

• develop risk-based PRGs <strong>and</strong> screen data to identify early,<br />

actions <strong>and</strong> chemicals of potential concern,<br />

• develop RI/FS data quality objectives,<br />

• focus additional sampling <strong>and</strong> anlaysis ef<strong>for</strong>ts of chemicals of<br />

potential concern, <strong>and</strong><br />

• provide justification <strong>for</strong> no further action.<br />

Site Characterization <strong>and</strong> <strong>Risk</strong> Assessment<br />

• help determine whether additional response action is necessary,<br />

• provide evaluations of the effectiveness of actions (where appropriate),<br />

• document the magnitude of risk <strong>and</strong> the primary causes of that risk, <strong>and</strong><br />

• define uncertainties.<br />

No Further<br />

Action<br />

Remedial Goal Options <strong>and</strong> <strong>Risk</strong> Assessment<br />

• incorporate results of baseline risk assessment,<br />

• calculate RGOs <strong>for</strong> contaminants of concern by media, using site-specific exposure parameters, &<br />

• identify ARARs.<br />

Figure 3. Site characterization <strong>and</strong> risk assessment<br />

The selection of an appropriate remedial action begins with a screening of potential alternatives<br />

during the initial scoping workshop. This is conducted prior to the development of the RI work plan<br />

(Fig. 4). The preliminary screening of alternatives is refined as more in<strong>for</strong>mation becomes available <strong>and</strong><br />

the results of the baseline ecological <strong>and</strong> human health risk assessments determine the chemicals <strong>and</strong><br />

pathways of concern. During the selection of remedial actions, short-term <strong>and</strong> long-term risks must be<br />

considered. The analysis of short-term risks focuses on the potential adverse effects on human health <strong>and</strong><br />

the environment from implementation of the remedial action. The analysis of long-term risks focuses on<br />

the risk that will remain after remedial action has been taken (this level of remaining risk is termed<br />

residual risk). These analyses may be either qualitative or quantitative, depending on site conditions. For<br />

more in<strong>for</strong>mation, refer to page 14 of <strong>Risk</strong> Assessment <strong>Guidance</strong> <strong>for</strong> Superfund, Part C (EPA 1991b).<br />

14

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