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Contingency Work Plan For Excavation of Soil @ Chevron Station #9-3232 <br /> January 21 1999 <br /> characterization . Should the backfill material be sand or soil it will be stockpiled separately <br /> onsite and the appropriate samples collected and analyzed for characterization . Depending on <br /> sample results Chevron may elect to re-use the material onsite as backfill. If necessary, the sand <br /> or soil may be aerated onsite and then re-used as backfill material . Should the soil be aerated <br /> onsite, the appropriate permits will be obtained from the San Joaquin Unified Air Pollution <br /> Control District (SJUAPCD). Concurrence will be obtained from SJCPHS prior to re-using any <br /> sand or soil as backfill onsite. In the event the sand or soil backfill material is not re-used <br /> onsite, Chevron will arrange for proper transportation to a licensed landfill for disposal . <br /> Task 3. Soil Borings <br /> Upon receiving the analytical results from the compliance soil sampling and the excavations (if <br /> necessary), GR proposes to drill soil borings to delineate the lateral and vertical extent of onsite . <br /> impacted soil. An addendum to this work plan will be prepared depicting the boring locations <br /> with a permit application and appropriate fee. <br /> We anticipate that one boring will be drilled near the source of impact to approximately 70 feet <br /> bsg (historical low depth to groundwater) to delineate the vertical extent of impacted soil. j <br /> Additional onsite borings will be drilled to approximately 40 feet bsg to delineate the lateral j <br /> extent of soil impact as necessary. Drilling will be performed by Bay Area Exploration, Inc. <br /> (C57 #522125). A GR geologist will monitor the drilling activities and prepare a log of each <br /> boring. Soil samples for description and possible chemical analysis will be obtained from each <br /> boring at five-foot intervals, as a minimum . Sample handling procedures are described in <br /> Appendix A. Although the actual number of samples submitted for chemical analysis will <br /> depend on site conditions and field screening data, we anticipate a minimum of three soil <br /> samples collected from above groundwater in each boring will be submitted for chemical <br /> analysis as described below. Two saturated samples will also be collected from the boring <br /> drilled below groundwater. Borings will be drilled with 8-inch-diameter hollow-stem augers <br /> and will be backfilled to ground surface with neat cement containing approximately 5 % <br /> bentonite powder upon completion of drilling. Neat cement will be placed using atremie pipe. <br /> Soil from each sampled interval will be screened in the field for the presence of volatile organic <br /> compounds using a photoionization detector (PID). These data will be collected for <br /> reconnaissance purposes only, and will not be used as verification of the presence or absence <br /> of petroleum hydrocarbons . Screening data will be recorded on the boring logs. <br /> Drill cuttings will be stored at the site pending receipt of chemical analytical data for disposal. <br /> The drill cuttings will be stockpiled on and covered with plastic sheeting. Soil samples from <br /> the drill cuttings will be collected for disposal characterization as described below. Steam <br /> cleaning rinsate wastewater will be transported bylmegrated WastestreamManagement (IWM) <br /> to McKittrick Waste Management in McKittrick, California. <br /> CH93232.WP2 3 346463 .02 <br />