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Tri-Regional Recommendations Page 14 of 24 <br /> Appendix A <br /> 3. Hydrographs and plots of chemical con- <br /> centrations versus time for each monitor- Investigations and characterization activities are <br /> ing well that has had detectable levels of to be presented accurately in the PAR, and <br /> contaminants. should include the following minimum informa- <br /> tion: <br /> 4. An estimate of the quantity of contami- <br /> nants remaining in soil and groundwater. • The depth and extent of free product <br /> found, including an estimate of volume <br /> 5. The anticipated date for completion of removed and volume remaining. <br /> cleanup activities. <br /> • Figures delineating lateral and vertical ex- <br /> 6. An identification of any data gaps and po- tent of soil contamination, groundwater <br /> tential deficiencies/redundancies in the degradation plume(s), and vapor plumes <br /> monitoring system or reporting program. as appropriate. <br /> 7. A proposal and rationale for any neces- • Tables summarizing analytical data such <br /> sary revisions to the groundwater sam- as compound concentrations found in soil <br /> pling plan and/or list of analytes. and groundwater, and sample depth. <br /> • An evaluation of the physical and chemi- <br /> 4.0 CORRECTIVE ACTION PLAN (CAP) cal characteristics of the hazardous sub- <br /> _ 2725 stance or its constituents,including its <br /> toxicity,persistence and potential for mi- <br /> Once the lateral and vertical extent of soil and gration in water, soil, and air. <br /> groundwater degradation is defined,the dis- <br /> charger is to proceed with the CAP. The CAP is • An estimate of the mass of contaminants <br /> separated into the Problem Assessment Report remaining in soil and groundwater. <br /> (PAR),the Feasibility Study(FS), and the Final <br /> Remediation Plan(FRP). At every step of the • Identification of applicable cleanup levels <br /> CAP,the lead regulatory agency will review for affected or threatened groundwater <br /> submitted documentation, and direct the dis- and surface water, and a rationale for re- <br /> charger to proceed with proposed actions, or lecting these levels. <br /> modify these actions to meet regulatory compli- <br /> ance for protection of water resources,health Note: Cleanup levels for leaking under- <br /> and safety, and sensitive ecological receptors ground storage tanks sites are based on <br /> until the FRP is successfully implemented and regulatory requirements as presented in <br /> no further action is required at the site. State Water Board Resolution 92-49, Poli- <br /> cies and Procedures for Investigation and <br /> 4.1 Problem Assessment Report(PAR) Cleanup and Abatement of Discharges <br /> under California Water Code Section <br /> The PAR summarizes the PIER and all addi- 13304, and Water Quality Control Plans <br /> tional investigations that characterize the site. of the Central Valley Region, including <br /> The PAR should include sufficient detail on the `Policy for Investigation and Cleanup of <br /> nature and extent of the contamination to pro- Contaminated Sites." <br /> vide a basis for future decisions regarding sub- <br /> sequent cleanup and abatement actions. The Cross sections based upon boreholes, <br /> discharger is to propose site-specific cleanup monitoring wells,trenches, and support- <br /> goals, and identify available remedial alterna- ing geological mapping logs. <br /> tives that have a substantial likelihood to <br /> achieve cleanup goals and objectives. A site map showing sensitive receptors <br />