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No Further Action Required Request Report <br /> US Can—Welty Road September 24,2013 <br /> The hydrocarbons in the subsurface are not very mobile. At least 40 years have passed since the <br /> pipelines were decommissioned; thus the extent of residual hydrocarbons in the subsurface is <br /> unlikely to increase. Significant changes of plume size or COPC concentrations, if measurable, <br /> would not be expected on a quarterly, semi-annual,or even an annual basis. The concentrations <br /> of COPCs do not pose a threat to human health or the environment, and it is expected that they <br /> will decrease to background levels over time. <br /> 12. Provide isoconcentration contour maps of contaminants of concern to define the lateral <br /> and vertical extent of contaminants remaining in soil and groundwater. The contour maps <br /> should present and estimated "zero zone"of contaminant concentrations both on site and <br /> off site. <br /> SAIC compared the sample analytical results for the COPCs to the lowest, most conservative <br /> ESLs and RSLs or WQOs, and concluded that the lateral extent of crude-oil affected soil and <br /> groundwater has been delineated as indicated on Figure 3. The investigation of off-site areas <br /> northwest of the former US Can property(including borings SB-38 through SB-41 and SB-43)is <br /> ongoing as part of the adjacent Ahern Road–Vernalis site. <br /> 13.Provide a summary of the remedial method(s) used to clean the site. Include the <br /> calculated zone of influence, assumptions used to design the remedial systems(s), and the <br /> duration of remedial activities. <br /> Soil was removed by WHF in 1996 as part of the waste/bum pit investigation. No remediation <br /> has been conducted as part of HPP-BTR investigation activities. <br /> 14.Provide a discussion of whether background is unattainable using best available <br /> remediation method(s). <br /> SAIC and Geomatrix Consultants, Inc. (Geomatrix)evaluated available remediation technologies <br /> for potential applicability to sites associated with former HPP-BTR operations,which is <br /> consistent with Section IIIA through C of SWRCB Resolution No. 92-49. SAIC prepared a <br /> report of findings(SAIC, 2005). Available removal technologies were compared to in-place <br /> management of SPO,using the evaluation criteria of effectiveness, implementability, and cost. <br /> The following removal technologies were evaluated: bailing; passive and active in-well <br /> skimming; belt skimmers; excavation; in situ flushing with surfactants and co-solvents; vacuum- <br /> enhanced recovery(bio-slurping); groundwater drawdown pumping; in situ heating at low and <br /> high temperatures; short-term, multi-phase extraction; and pressure-pulse technology. SAIC and <br /> Geomatrix found that very little of the SPO encountered at former OVP and TAOC sites can be <br /> recovered due to its high viscosity and the low hydraulic conductivity of fine-grained Central <br /> Valley soils. SAIC and Geomatrix also found that threats to water quality,human health, and the <br /> environment are essentially the same whether free product is actively removed or not; either <br /> way, significant percentages of free product will remain. SAIC and Geomatrix concluded that all <br /> of the remedial technologies—with the exception of excavation at some sites—are ineffective, <br /> not easily implemented, and/or disproportionately costly in comparison to benefits. Therefore, <br /> and in consideration of Section IIIA through C of SWRCB Resolution No. 92-49,active <br /> removal of the affected soil and groundwater is considered technologically and economically <br /> infeasible for this Site. <br /> Unlike removal technologies, natural attenuation in conjunction with an SGMP is a viable <br /> approach for the Site. Natural attenuation will degrade the residual crude oil and limit the lateral <br /> 9 SAIC. <br />