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Ripona Market October 28,2004 <br /> Corrective Action Plan <br /> 4.0 MITIGATION ALTERNATIVES <br /> Preliminary fate and transport modeling of benzene therimary contaminate of <br /> cnc� <br /> oinder of two possible mitigation sic—enari <br /> os using the A model <br /> "Bioscreen4 " The modeling was based on average values and site conditions but <br /> without site specific biodegradation indicators The corrective action scenario for <br /> low risk closure (no action) was modeled <br /> Model input parameters for "Bioscreen4" and-belie glass balance calculations <br /> are presented in Appendix B, Bioscreen Input Parameters Hydrogeologic, <br /> dispersion, absorption, and biodegradation parameters were provided from onsite <br /> groundwater monitoring data and published values The model is limited in the <br /> soluble mass value that can be used in the model An estimate of the contaminant <br /> mass balance is presented in Appendix B Approximately 0 3 kilograms of MTBE <br /> are estimated to present at the site The minimum value that can be used in the <br /> model is 1 kilogram which greatly over estimates the magnitude and potential <br /> extent of the plume migration <br /> Model runs were evaluated to determine the maximum extent of plume migration <br /> and remaining contamination at plume stabilization or end of modeled time <br /> period Model results are presented in Appendix C <br /> • The model was calibrated for existing conditions using recent monitoring data <br /> Groundwater flow directions have remained consistently to the northeast The <br /> plume appears to be stable and under going degradation / dispersion along the <br /> expected pattern for a first order decay pattern with long solute half life as <br /> expected with MTBE The source contaminant concentrations have dropped from Y-1117Upf s f L <br /> 6300 to 450 in 4 years for an estimated source half life of 1 year �ol�te yd hk, <br /> Under existing conditions the plume is predicted to degrade to an MTBE <br /> concentration of 0 ug/l in 18 years from a current concentration of 450 ug/1 , at the <br /> identified receptor at 1000 feet down gradient Assuming no degradation, it is <br /> estimated that simple dilution and attenuation will reduce the plume to 10 ug/1 at <br /> 1000 feet <br /> 4.1 Low Risk Closure <br /> The mitigation strategy consists of the evaluation of the site to confirm the low <br /> I risk nature of the site as determined by the State Waters Resources Control Board <br /> (SWRCB) Policy of December 1995 Monitoring of the site monitoring wells and <br /> domestic wells is conducted to verify the natural breakdown of the contamination <br /> I plume <br /> I <br /> 9 <br />