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1 <br /> r,_;i it Phase II Field <br /> ' Investigation and LNAPL <br /> Mobility Evaluation Report <br /> Union Pacific Railroad Company <br /> ' Former Maintenance Facility <br /> Tracy, California <br /> MW-06A because it was thought the observed increase in product may increase <br /> t the product yield enough to make a skimmer system affective. The skimmer system <br /> removed only 6.1 gallons of product between August 1992 and May 1996,when it was <br /> removed and replaced with two bilge bags (ERM 2006). Passive diesel product <br /> ' recovery using bilge bags and absorbent socks was conducted until August 2007. <br /> During that time, only a limited volume of product(approximately 32 gallons)was <br /> recovered and passive product recovery was discontinued in August 2007. Based on <br /> ' this information,the skimmer system was not effective for removing LNAPL. <br /> The dual-phase extraction system operated from December 2000 to July 2002. UPRR <br /> ' shut down the dual-phase extraction system to evaluate rebound of VOCs and TEPH-d <br /> concentrations in soil vapor and groundwater. The results of this study were presented <br /> in ERM's report titled Rebound and Remediation Effectiveness Evaluation(ERM <br /> ' 2003). As concluded in the rebound evaluation report, the dual-phase extraction <br /> system was not effective for remediation of residual VOCs and diesel product <br /> remaining in the source area,therefore, the dual-phase extraction system continues to <br /> ' be maintained in shutdown mode. The dual-phase extraction system removed <br /> approximately 53 gallons (380 pounds)of free-phase product. <br /> t2. Hydrogeology <br /> Groundwater has been designated into three zones (the A-, B-, and C-Zones)based <br /> ' on depth below ground surface(bgs). Shallow groundwater(referred to as the A-Zone), <br /> occurring at approximately 10 to 25 feet bgs,was the focus of this investigation. <br /> Relatively low COC concentrations have historically been detected in samples <br /> ' collected from the B-and C-Zones. Groundwater generally flows toward the north- <br /> northeast. <br /> ' Soil at the Site,to a depth of approximately 100 feet bgs, is composed primarily of clay <br /> and silt with varying amounts of sand and fine gravel.A more permeable sand layer <br /> was identified in most of the Phase II field investigation CPT logs from 10 to 15 feet <br /> ' bgs. This sand layer was not identified at locations to the north and northeast(i.e., <br /> HP-2, HP-3, HP-4, HP-7, HP-20, HP-21, HP-23, HP-24, and HP-27). Copies of CPT <br /> and LIF boring logs from this investigation are included in Appendix A. <br /> Table 2 presents the depth-to-groundwater measurements and groundwater elevations <br /> from 2005 to the present. A March 2010 groundwater elevation contour map for the A- <br /> ' Zone is presented on Figure 3. The March 2010 data indicated the gradient in the A- <br /> Zone is toward the northeast. Depth to groundwater ranges from 8 to 17 feet bgs <br /> 1 <br /> mwpmesov.mapi m.'Wll 2x2010)d c 5 <br />