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3212 North California Street <br /> Page 2 of 3 <br /> During the process of reviewing historical site data, EHD identified discrepancies <br /> between cross sections submitted over time and became concerned that MW-1 may be <br /> acting as a vertical conduit since the well's screened interval (45 to 75 feet bgs) may be <br /> connecting two sand layers. A site conceptual model (SCM) that incorporates findings <br /> from the last seventeen years of site characterization is needed to evaluate present site <br /> conditions, You are now directed to prepare and submit an SCM to the EHD. The <br /> general purposes for an SCM are to demonstrate where the contaminants came from, <br /> where they are at the present time, how they move through the subsurface, how they will <br /> respond to changes in the groundwater flow characteristics or to potential remediation <br /> efforts, what the contaminants' ultimate environmental fate will be, and to help evaluate <br /> the risk posed by the contaminants to groundwater supplies and sensitive receptors. In <br /> addition, the SCM may demonstrate data gaps, thereby illustrating where additional <br /> investigation is needed. To be sure that the SCM will adequately address the assessment, <br /> remediation and, ultimately, final closure requirements for this site, please include the <br /> following, as appropriate, in the SCM: <br /> • Local and regional plan view maps showing locations of sources, boring and <br /> monitoring well locations, lines of cross section, extent of conta3ninants in each <br /> media (i.e., an interpretive drawing — not merely a plot of laboratory results), <br /> direction and rate of groundwater flow, and receptor locations, including water <br /> supply wells within 2,000 feet of the site; <br /> • Cross sections showing subsurface geological features, depth to groundwater, <br /> man-made conduits, monitoring well construction and the interpreted vertical <br /> extent of soil and groundwater contamination; <br /> • Cross-plots of key chemical concentrations verses time for representative wells <br /> that demonstrate significant contaminant concentration trends; <br /> • Summary tables of contaminant concentrations in the different media; <br /> + Rose diagram showing directions of dominant groundwater flow; <br /> + Well and boring logs (including construction/screening); and ' <br /> f <br /> • Narrative description of the SCM that describes controls on contaminant i <br /> distribution; contaminant migration mechanisms, pathways and rates; plume <br /> disposition over time; and sorbed and dissolved contaminant masses. <br /> While not necessarily showing all data in diagrams and drawings, an adequate SCM can be <br /> utilized to account for most of the known data and to evaluate the fate of impacted <br /> groundwater with an estimate of when background conditions will be restored. All <br /> analytical data should be included in tables. Residual contaminant concentrations should <br /> be compared to Environmental Screening Levels (ESL) and California Human Health <br /> Screening Levels (CHHSLs) established by California Environmental Protection Agency <br /> San Francisco Bay Regional Water Quality Control Board. Methods and calculations of <br /> contaminant masses should be included in the SCM, and may be submitted as an appendix. <br />