Laserfiche WebLink
. Updated Corrective Action Plan—Tosco(76)Service Station No 11192, Stockton, California <br /> June 26 2002 <br /> 3.0 CORRECTIVE ACTION PLAN COMPONENTS <br /> 3 1 Irn act Assessment <br /> 1. The physical and Chemical characteristics of the hazardous substance or its constituents, <br /> including their toxicity, persistence, and potential for migration in water, soil, and air: <br /> Based on the analytical results for both soil and groundwater samples collected to date, the primary <br /> contaminant appears to be gasoline (BTEX constituents and MtBE) Material Safety Data Sheets <br /> (MSDS) for unleaded gasolines are attached to this CAP in Appendix A The MSDS sheets describe <br /> the physical and chemical characteristics of gasoline and its components <br /> The analytical results of the groundwater samples collected from the monitoring wells at and in the <br /> vicinity of the site indicate that dissolved concentrations of petroleum hydrocarbons are present in the <br /> wells Free product has never been detected at the site It is GR's understanding that as of January 1, <br /> 2001, Tosco no longer delivers fuel containing MtBE to service stations in northern California <br /> The shallow MtBE plume beneath the site is predominantly defined Previous investigations at the site <br /> indicate that the plume is largely confined to the site,although detections of petroleum hydrocarbons in <br /> the onsite deep well and offsite Geoprobes indicate that additional vertical and lateral delineation is <br /> necessary in the downgradient direction The extent of the hydrocarbon impact to the deeper water <br /> bearing zone has not been fully delineated, additional deep monitoring wells are needed to complete the <br /> delineation GR proposes to install four double-cased monitoring wells to delineate the deeper <br /> hydrocarbon plume (see Section 4 0) Iso-concentration maps for TPHg,benzene, MtBE and TBA in <br /> shallow groundwater are presented on Figures 5 through S Isoconcentration maps for the deeper <br /> aquifer were not prepared due to insufficient data (only one data point in deeper aquifer) Historical <br /> tables of soil and groundwater data are attached in Appendix C Also included in Appendix C are <br /> figures showing the sample locations for the tabulated soil data <br /> GR prepared hydrocarbon mass calculations in groundwater for TPHg, benzene, MtBE and TBA The <br /> calculations are presented in Appendix D Results of the calculations indicate a very low residual mass <br /> of TPHg(0 18 lbs),benzene(0 01 lbs)and MtBE(3 69 lbs) Apparently the mass of MtBE previously <br /> present beneath the site has degraded to TBA, as the calculation for TBA mass equaled 929 lbs <br /> According to information provided by Tosco,current MtBE degradation experiments seem to indicate <br /> that dissolved oxygen is the controlling factor in the breakdown of MtBE to TBA Current theory holds <br /> that if enough dissolved oxygen is present in the groundwater, MtBE will degrade to TBA, and <br /> ultimately to carbon dioxide If the supply of dissolved oxygen is limited during this degradation <br /> sequence,then the process appears to halt In December of 2001,a DPE event was conducted at the site <br /> (see section 2 2) The groundwater sampling event conducted immediately after the DPE event revealed <br /> the apparent mass transformation of MtBE to TBA GR believes that the DPE event may have <br /> mobilized sufficient oxygen into the saturated zone to accelerate the degradation of MtBE to TBA,but <br /> • not enough oxygen to allow the TBA to be fully degraded It is expected that the introduction of <br /> 14024508 5 <br /> 4 <br /> a <br />