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DISCLAIMER <br /> Preliminary remediation goals (PRGs) focus on common exposure pathways and may <br /> not consider all exposure pathways encountered at CERCLA / RCRA sites (Exhibit 1-1). <br /> s do not consider impact to groundwatetior address ecological concerns. PRGs are <br /> specifically not intended as a (1) stand-alone decision-making tool, (2) as a substitute for <br /> EPA guidance for preparing baseline risk assessments, or (3) a rule to determine if a <br /> waste is hazardous under RCRA. <br /> The guidance set out in this document is not final Agency action. It is not intended, nor <br /> can it be relied upon to create any rights enforceable by any party in litigation with the <br /> United States. EPA officials may decide to follow the guidance provided herein, or act <br /> at variance with the guidance, based on an analysis of specific circumstances. The <br /> Agency also reserves the right to change this guidance at any time without public notice. <br /> 1.0 INTRODUCTION <br /> The Region 9 PRG table combines current EPA toxicity values with "standard" exposure <br /> factors to estimate contaminant concentrations in environmental media (soil, air, and water) <br /> that are protective of humans, including sensitive groups, over a lifetime. Chemical <br /> concentrations above these levels would not automatically designate a site as "dirty" or trigger <br /> a response astion. However, exceeding a PRG suggests that further evaluation of the <br /> potential risks that may be posed by site contaminants is appropriate. Further evaluation may <br /> include additional sampling, consideration of ambient levels in the environment, or a <br /> reassessment of the assumptions contained in these screening-level estimates (e.g. <br /> appropriateness of route-to-route extrapolations). <br /> The PRG concentrations presented in the table can be used to screen pollutants in <br /> environmental media, trigger further investigation, and provide an initial cleanup goal if <br /> applicable. When considering PRGs as preliminary goals, residential concentrations should be <br /> used for maximum beneficial uses of a property. Industrial concentrations are included in <br /> the table as an alternative cleanup goal for soils, but it is not recommended that industrial <br /> concentrations be used for screening sites. 4 <br /> Before applying PRGs as screening tools or initial goals, the user of the table should consider <br /> whether the exposure pathways and exposure scenarios at the site are fully accounted for in <br /> the PRG calculation. Region 9 PRG concentrations are based on exposure pathways for <br /> which generally accepted methods, models, and assumptions have been developed (i.e. <br /> ingestion, dermal contact, and inhalation) for specific land-use conditions and do not consider <br /> impact to groundwater or ecological receptors (see Developing a Conceptual Site Model <br /> below). <br /> 2 <br />