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9.3 Groundwater and Surface Water Monitorinq Schedule <br />The new wells were sampled in March and April 2007 for purposes of obtaining baseline <br />data and to evaluate the fate and transport of BTEX compounds in groundwater. E-21 <br />recommends resuming groundwater sampling in June 2007 and then performing future <br />sampling on a quarterly basis (i.e. June, September, December and March). <br />At this time, we propose to continue to sample all the existing mentoring wells and all <br />new wells proposed in the addendum. If a well is determined to be free of BTEX <br />compounds for four consecutive quarters and is not a downgradient wells, E-21 <br />proposes that sampling of such a well would be discontinued. However, we recommend <br />that the four surface water body sampling locations be performed on a quarterly basis <br />until remediation is completed. <br />E-21 proposes that closure monitoring may be initiated once BTEX concentrations in all <br />wells at the site are below the Colorado Maximum Contaminant Limits (MCLs). If the <br />wells remain below the MCLs for four consecutive quarters, E-21 will petition for "no <br />further action" and well decommissioning will be performed if closure is granted by <br />CDPHE. <br />10.0 Groundwater Remediation Plan <br />E-21 recommends performing air-sparge/ soil vapor extraction (AS/SVE) in the dissolved <br />phase plume to remediate petroleum impacts in groundwater. Based on the pilot testing <br />results, positive pressure (>0.10 inches of water) for sparging was generated up to 50 <br />feet from AS pilot test well. Vacuum was generated (>1.0 inches of water) over 50 feet <br />' from the SVE pilot test well. The location and radius of influence estimated by the <br />remediation wells is shown on Figure 9. The SVE wells will be 2-inch diameter and the <br />AS wells will be 1-inch diameter. <br />' Due to the construction activities at the site and changing nature of the landscape, we <br />recommend using one or two trailer-mounted remediation systems to allow for moving <br />' the remediation equipment if needed. The equipment would be supplied by a generator <br />for continuous operation and adjustments to the AS/SVE program could be made <br />relatively easily. Air flow to the wells will be conveyed by reinforced flexible hose, thus <br />eliminating the need for pipe trenching. <br />E-21 estimates the AS/SVE system will need to operate for at least six months to reduce <br />the dissolved phase plume. The quantity of VOCs will be measured weekly to confirm <br />' remediation progress. Soil pressure and vacuum will be measured by monitoring from <br />selected monitoring wells. Quarterly groundwater sampling will be performed during the <br />remediation phase to determine the progress of the groundwater cleanup and to allow <br />' adjustments. Initially, all the remediation wells are expected to be used. As the plume is <br />reduced, the system will be modified in the field to concentrate on areas containing <br />increasing or elevated BTEX concentrations. Once BTEX concentrations are reduced to <br />below the MCLs, the system will be removed from the site and closure monitoring will <br />' commence. <br />Based on the above described remediation program, E-21 estimates that the <br />' remediation phase of the project will require one year from initiation of remediation. If <br />remediation is successful, closure monitoring will require one additional year. Thus, if <br />remediation is successful, a petition for no further action may be submitted in <br />approximately two years from the initiation of remediation. <br />12