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Dolly Madi3on/Langendorf Rakery - 2 - 18 June 2008 <br /> 1426 S. Lincoln St., Stocker <br /> PIER Addendum <br /> The PIER,4ddend includes the fieldwork and analytical results for repaired vapor extraction well VW-1 <br /> (now used as a monitoring well due to a rising water table) and a new monitoring well MW-3 (enclosed <br /> Figure 2), which was located in S. Lincoln St. The PIER Addend states soil vapor wells SGW-1 and <br /> SGW-2 were also installed and sampled, and all wells (old and new) were professionally surveyed to a <br /> common datum. The PIER Addend updates the PIER Hydrogeology section by adding site specific <br /> groundwater flow directions and gradients to the PIER evaluation of the hydrogeology at neighboring <br /> USTs sites. The PIER Addend also includes site specific groundwater elevation contour maps of the <br /> shallow, mini, and deep water bearing zones. Site geology consists of"...interfingered beds of <br /> permeable sands and gravels mixed with lesser permeable silts and low permeable clays..." (enclosed <br /> cross sectic,n Figure 4), which does not appear to retard contaminant transport from the shallow to the <br /> deeper aqu fer zones. In fact, while an argument has been proposed that groundwater pollution is the <br /> result of an off-site petroleum hydrocarbon source, the PIER Addend demonstrates that there is also <br /> evidence for a USTs release at the Site, which is several orders of magnitude greater in concentrations <br /> than any pctential offsite source. <br /> The PIER Addend concludes that petroleum hydrocarbons were not detected in soil samples collected <br /> for installation of MW-3. However, on 26 March 2008 (first quarter 2008) methyl tert-butyl ether (MTBE, <br /> 38 micrograms per Liter or ug/L) was detected in groundwater sampled from MW-3. By email received <br /> on 4 June 2008, Stratus informed me that the analytical results for the second quarter 2008 groundwater <br /> monitoring event reported MW-3 as non-detect for MTBE at a detection limit of 0.5 ug/L. The PIER <br /> Addend als:) stated that all soil gas sampling results did not exceed the San Francisco Bay Regional <br /> Board Environmental Screening Levels. <br /> Pilot Test/FS <br /> The Pilot Test section of the Pilot Test/FS provides the results of air sparging and soil vapor extraction <br /> (AS/SVE) tests conducted on 11/12 March 2008 using portable test equipment and remediation wells <br /> VW-2, VW-3, and AS-1. The effective radii of influence (ROI) for the SVE wells (VW-2 and VW-3) were <br /> calculated at approximately 15 feet. Dissolved oxygen content in groundwater also increased from <br /> 0.12 milligrams per Liter (mg/L) up to 4.0 mg/L during the AS portion of the test. Petroleum <br /> hydrocarbons detected by Photo-ionization Detector in the SVE air stream increased from 2 parts per <br /> million by volume (ppmv) at startup to 390 ppmv just prior to the end of the test. Total petroleum <br /> hydrocarbons as gasoline (TPHg) laboratory analytical results increased in extracted soil vapor from <br /> 640 milligrams per cubic centimeter (mg/m3) at startup of the SVE system to 3,200 mg/m3 approximately <br /> 30 minutes before the end of the test. Based on these results, Stratus calculated that TPHg removal <br /> would be approximately 2.5 pounds per day (ppd) from soil vapor extraction well VW-2 alone, and <br /> 14.5 ppd of TPHg from soil vapor extraction well VW-2 when combined with injecting air into air sparge <br /> well AS-1. Extracting soil vapor from VW-3 alone reported 96 ppd of TPHg removal, while combined <br /> use of VW-3 and AS-1 showed 17 ppd. Using just VW-2 and VW-3 resulted in removal of 24.5 ppd of <br /> TPHg; while use of all of the remediation wells, VW-2, VW-3, and AS-1, resulted in a calculated removal <br /> rate of 28.E ppd of TPHg. <br />