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t <br /> ' reading was from the test sample after purging one-sampling train volume. Therefore, the <br /> subsequent samples were collected after removing one purge volume from each soil gas <br /> sampling location. The calculations for the purge volumes are presented on the Soil Gas <br /> ' Purge Volume Calculation Table in Appendix D. <br /> PSC performed a 10-minute leak check on the sampling manifold prior to purging or <br /> collecting the soil gas sample for each location. The guidelines do not specifically indicate <br /> how much of a vacuum drop is considered acceptable. After 10 minutes had passed upon <br /> charging the vacuum gauge among the seven primary sampling trains, two sample locations <br /> had vacuum drops greater than 2 inches of mercury. PSC deemed a drop of 2 inches or less to <br /> be acceptable. Sample location SG-2 had incurred a 4-inch drop and SG-4 had incurred a <br /> 12-inch drop. <br /> For sample SG-2, the environmental technician retightened the compression fittings and <br /> proceeded with the vapor purge. Sample SG-2 did not decrease vacuum pressure after <br /> allowing the appropriate time to purge the sample train. This indicated that the sampling train <br /> 1 did not have a leak. Rather upon further investigation,it was determined that the compression <br /> fitting was over tightened and pinched closed the opening to the sample tubing. PSC refit the <br /> compression fitting, performed an additional 5-minute leak check, a successful purge, and <br /> then collected a successful soil gas sample. <br /> PSC did not record a successful leak test for sample SG-4. It was determined that the leak <br /> may have been with the connection of the manifold to the purge canister. PSC retightened the <br /> manifold compression fittings. The purge appeared successful. However, the sample volume <br /> collected for soil gas sample SG-4 was not sufficient. The field sampler recorded the final <br /> SUMMA canister vacuum reading at 22 inches after allowing the appropriate sample <br /> collection time. However, the canister should have had only 5 inches of vacuum remaining. <br /> The sampler stopped collecting the sample at 22 inches assuming that the gauge was <br /> incorrect. However, the laboratory confirmed that the actual vacuum remaining in the SG-4 <br /> canister was 21 inches. Therefore, it appears as though only 250 mLs was actually collected <br /> instead of approximately 900 mLs. The unusually slow sample collection may have been due <br /> to the over-tightened/pinched tubing or to less permeable conditions in the sampling zone. <br /> The laboratory had to pressurize the canister to 21 inches of mercury (well beyond the normal <br /> 5 inches) in order to analyze the sample. This resulted in a dilution factor approximately three <br /> times greater than the other samples. Analysis of this diluted sample produced results that <br /> were biased high. The reporting limits were approximately three times greater than the other <br /> samples due to sample dilution. Therefore, the sample results are not representative and thus <br /> unusable. This rejected sample does not disqualify the overall soil vapor intrusion survey. <br /> The remaining five exterior samples and the one interior sample indicate with a high level of <br /> confidence that the risk of soil vapor intrusion does not exist for the facility. <br /> ' 2.5 Soil Gas Analytical Results <br /> The analytical results of the soil gas samples collected and submitted for analysis have been <br /> tabulated and are presented on Tables 1 and 2 and on figure 4. A copy of the analytical data is <br /> included in Appendix F. A detailed discussion of the analytical results are presented as <br /> follows. <br /> Vapor Intrusion Survey <br /> Soil Gas Sampling Report <br /> ' Prepared For:Sara Lee Bakery Group,Inc. Prepared By:PSC Industrial Outsourcing,LP <br /> Sam Lee—Lincoln Street\2009_03_31-Soil Gas Sampling Raport.doc March 31,2009 <br /> 10 <br />