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Mr. Ron Rowe <br /> March 15, 1999 <br /> Page 2 <br /> 4. As noted, the backfill material shall be of low permeability to reduce the potential for a <br /> hydraulic head to develop over a high permeability sink, which could push residual <br /> contamination to the aquifer and off-site. Quarry sources are being contacted for <br /> availability and samples in order to determine permeability of available fill sufficient to <br /> restore excavation to grade. To stabilize saturated soil and bridge any standing <br /> groundwater in the excavation, the bottom of the excavation will be filled with crushed <br /> rock. Low permeability soil will be layered above the crushed rock in one-foot lifts and <br /> compacted with a sheeps-foot roller attached to the excavator. The backfill will be tested <br /> to assure that it achieves the required 90 percent compaction rate. <br /> 5. As noted, a Flame Ionization Detector(FID) shall be utilized during field activities to <br /> screen and segregate soils. <br /> 6. As noted,the soil stockpile will be characterized by collecting two soil samples every 50 <br /> cubic yards for laboratory composite and analysis. <br /> 7. Any post-remediation monitoring will be complicated by the future construction and <br /> highway interchange development at the site. Prior to re-development, the existing <br /> monitoring wells will be re-sampled to evaluate any immediate impact of the excavation <br /> and dewatering efforts. Since the planned development encompasses the entire site, all <br /> existing groundwater monitoring wells and the on-site domestic well will be properly <br /> sealed and abandoned. To protect the nearby municipal well, at least one"sentry" <br /> monitoring well cluster will be installed between the site and the municipal well. The <br /> well cluster will consist of two individual wells screened across the groundwater table <br /> and a deeper groundwater-bearing zone. Once the municipal well is operational, the well <br /> cluster will be sampled on a quarterly basis for at least six months to evaluate any <br /> possible migration of impacted groundwater into the municipal well cone of depression. <br /> Upon approval of this conceptual post-remediation monitoring strategy, a detailed work <br /> plan will be prepared for regulatory review. <br /> Additional comments to the work plan were provided by Caltrans in their memorandum, <br /> dated March 12, 1999. These three comments are resolved as follows: <br /> 1. Given that diesel hydrocarbons are not readily soluble in water, significant removal of <br /> diesel is not expected during the,de-watering activities. De-watering is expected to <br /> facilitate the excavation of heavily-impacted soil from below the groundwater table and <br /> to remove any separate-phase hydrocarbons on the water table surface. Once the de- <br /> watering effort has been completed, any separate-phase hydrocarbons will be removed <br /> from the surface of the contained water and measured. Water samples will then be <br /> collected to determine the amount of dissolved-phase contaminants removed and to <br /> determine filtration requirements for water discharge. <br />