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I <br />' 13 April 2005 <br /> AGE-NC Project No 01-0827 <br /> Page 6 of 7 <br />' No additional analytes were detected at or above laboratory reporting limits in the samples analyzed <br /> The laboratory report (CTEL Project No CT214-0502035), QA/QC reports and chain of custody <br /> forms are included in Appendix F GeoTracker confirmation pages of the submitted laboratory EDF <br />' files are included in Appendix E <br />' 4.0. SUMMARY AND CONCLUSIONS <br /> Based on the data collected from the site, AGE finds <br />' • On 31 March 2005,ground water was encountered at a depth of approximately 22 feet btoc, <br /> an increase of approximately 2 5 feet since the December sampling event <br />' • The ground water flow direction was inferred to be towards the east, at a gradient of <br /> approximately 0 009 ft/ft on-site and 0 01 ft/ft west of the site <br />' • The detections of TPH-g and BTEX compounds in the ground water sample collected from <br /> deep vapor well VW-2d demonstrate a contamination trend increase (Appendix D) <br /> Detections of TPH-g m the deepest well(MW-6)confirms the vertical extent of the dissolved <br />' hydrocarbons Upward fluctuations in TPH-g and BTEX concentrations during the <br /> remediation period suggest continued desorption of hydrocarbons from soil into ground <br /> water,likely due to hydrocarbon mass attached to saturated soil re-mobilized faster than the <br /> ozone is capable of destroying hydrocarbons and now is dissolved in the ground water A <br /> trend of increasing TPH-g concentrations was also documented during the start of air <br />' sparging and ozone-enriched sparging at the site <br /> • MTBE was the only fuel additive detected in the sample from VW-2d The concentrations <br /> of MTBE and benzene are above their respective DHS Maximum Contaminant Levels <br />' (MCL) for drinking water <br /> • Low ORP values, detected in the source area, demonstrate the presence of a generally <br />' reduced environment in the saturated zone near the source area Ideally, the introduction of <br /> oxygen rich air (ozone air sparging) in the source area should produce an oxidizing <br /> environment which will lead to a reduction in contaminant levels Dissolved oxygen <br />' concentrations collected from wells at the site,since operation of the ozone air sparge system <br /> commenced, indicate an adequate migration of ozone-rich sparged air into the subsurface <br /> 1 <br /> 5.0. RECOMMENDATIONS <br /> Based on the findings of the remediation activities recounted in this report, AGE recommends <br /> • <br />' Advanced GcoEnvironmental,Inc <br />