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BALE®BVFLDER <br /> Bright People.Right Solutio— <br /> DISCUSSION OF FINDINGS CONCLUSIONS AND RECOMMENDATIONS <br /> The following conclusions and recommendations are based upon analytical results and <br /> Kleinfelder's findings. <br /> The soil analytical results were compared (as applicable) to three published regulatory <br /> screening levels (SLs) including California Human Health Screening Levels (CHHSLs), <br /> Environmental Screening Levels (ESLs) and Regional Screening Levels (RSLs). The <br /> CHHSLs were developed by the Office of Environmental Health Hazard Assessment <br /> (OEHHA) on behalf of the California Environmental Protection Agency (Cal/EPA) in a <br /> document dated November 2004 and revised January 2005. ESLs were developed by the <br /> California Regional Water Quality Control Board, San Francisco Bay Region, dated May <br /> 2013. RSLs, formerly known as PRGs, were developed using risk assessment guidance <br /> from the EPA Superfund program with reference tables dated May 2013. <br /> These various screening levels (SLs) are similar in that they were developed to assist in <br /> evaluating sites impacted by releases of hazardous chemicals. The various screening <br /> levels are risk assessment tools which include conservative values for commonly detected <br /> contaminants, but are not regulatory limits or cleanup standards, although regulatory <br /> agencies may and have chosen some of these values as such. Some of these screening <br /> levels, such as the ESLs also take into consideration leaching potential to groundwater. <br /> The presence of a chemical at concentrations in excess of a screening level does not <br /> necessarily indicate that adverse impacts to human health or the environment are <br /> occurring; but does indicate that additional evaluation may be warranted. <br /> Kleinfelder compared analytical results for soil samples collected in the UST excavation <br /> and from stockpiled soil (Tables 2 and 3) to SLs associated with commercial/industrial land <br /> use given that the soil is within the French Camp Road right of way and is anticipated to be <br /> re-used on the larger roadway project and not for residential land use. Results from Table <br /> 1 were not compared to SLs as this soil and the UST have been disposed of offsite under <br /> hazardous waste manifest and the concentrations in Table 1 are from soil within the tank <br /> and are not representative to remaining onsite soil. <br /> The following table is a summary of concentration ranges for the two analytes detected <br /> from the requested analyses with comparison to,the noted SLs: <br /> 125819.E01/ST013RO732 Page 6 of 10 December 11, 2013 <br /> Copyright 2013 Kleinfelder <br />