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Mr. Mike Desso - 2 - 4 December 2006 <br /> 2. Nestle's evaluation should include the horizontal and vertical extent of TCE vapor migration in <br /> the vicinity of borings SG-2 through SG-5, and the areas west and south of 320 Stockton <br /> Avenue. <br /> 3. Also, Nestle's evaluation of the horizontal and vertical extent of TCE vapor migration should <br /> include the residential areas northwest, west, and south of 519 S. Stockton Avenue. <br /> 4. Concentrations of TCE in soil vapor may present a future risk to human health if currently <br /> vacant properties near the Former Facility are developed. Nestle should notify the City of <br /> Ripon Building Department about this potential risk to human health, allowing the City to take <br /> appropriate interim administrative measures. <br /> 5. Until VOCs in soil gas near the Former Facility (i.e. soil boring SG-1 location) have been <br /> remediated to risk-appropriate concentrations for current and future buildings, Nestle should <br /> implement soil gas monitoring. This will require completion of several soil gas monitor <br /> wells/piezometers that will allow for periodic collection of samples from the same locations. <br /> Specific Comments on the Draft Report <br /> The following comments address specific issues within the Draft Report that Regional Water Board <br /> staff identified. <br /> 6. Sampling procedures utilized by Nestle for collecting soil vapor samples from 5 feet below <br /> ground surface (bgs) deviated from the procedures presented in the revised work plan dated <br /> September 15, 2006. The first four feet of each boring was advanced with a hand auger. The <br /> boring was then backfilled with the cuttings and the sampling probe was pushed through the <br /> cuttings and through one foot of soil where it was stopped at 5 feet bgs. Hand augering was <br /> apparently done to avoid puncturing subsurface utilities. When sampling probes are advanced <br /> in this manner, the soil vapor sample should be collected after 48 hours to allow time for soil <br /> vapor to equilibrate. However, Nestle collected the 5-foot soil vapor sample after only 20 <br /> minutes. The twenty-minute equilibration time was only appropriate for the samples collected <br /> at 10, 15, and 20 feet bgs. <br /> 7. The method used by Nestle to advance the soil vapor sample probe to 5 feet bgs should be <br /> described in more detail. If the probe was advanced by the drilling subcontractor, that should <br /> be indicated. <br /> 8. The first paragraph of Section 4, page 3 of the Draft Report indicates that the field notes are <br /> presented in Appendix B. However, they are not presented. They should be presented in the <br /> Final Report. <br /> 9. The results of leak testing with isopropyl alcohol, including photo ionization detector (PID) <br /> readings and PID calibration methods are not included in the Draft Report. They should be <br /> presented in the Final Report. The laboratory analyses specified for soil vapor samples did not <br /> include isopropyl alcohol. Laboratory analyses for isopropyl alcohol should be included in the <br /> Final Report. <br /> 10.The Draft Report indicates that the PID detection limit was 10 parts per million-volume (ppmv). <br /> The Regional Water Board staff notes that the Department of Toxic Substances Control <br /> document, entitled Advisory—Active Soil Gas Investigations, January 28, 2003 (Reference 5 of <br />