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								        									S  E  C  ®  R
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<br />   •     	vicinity of the subject site  The well search was conducted within a '/-mile radius around the site
<br />      		Based on the available data supplied by the California Department of Water Resources (DWR),
<br />      		three municipal wells were identified within the '/-mile radius of the study area, the closest well is
<br />      		located approximately 1,000 feet north-northwest of the site   The depths of all three municipal
<br />      		wells were reported to exceed 550 feet bgs and contain screened intervals beginning at a
<br />      		minimum of 350 feet bgs  The SRS was conducted within a 500-foot radius centered around the
<br />      		subject site   The SRS involved distributing questionnaires to all residences and businesses
<br />      		within  the  study  area,  requesting  information  about  potential  groundwater  receptors    GR
<br />      		distributed 141 questionnaires via the U S  Post Office and a total of 49 questionnaires (35%)
<br />      		were returned to GR   None of the returned questionnaires identified the presence of a well within
<br />      		the SRS study area (GR, 2001)
<br />      		MONITORING AND SAMPLING
<br />      		TRC's  Groundwater Monitoring  Report dated  June 23,  2004  is  included  as Attachment A,
<br />      		including Tables 1- 3, Figures 1 - 5, and Graphs 1 - 8 plus field data sheets and groundwater
<br />      		analytical reports   The site has been monitored and sampled since 2nd quarter, 1990  Between
<br />      		1990 and 1991 the site was monitored/sampled semi-annually From 1992 to the present the Site
<br />      		has been monitoredlsampled quarterly Currently MW-1 and MW-3 through MW-13 are monitored
<br />      		and sampled quarterly each year Samples are analyzed for TPHg, BTEX, and fuel oxygenates
<br />      		During the second quarter 2004 groundwater flow was toward the north at a gradient of 0 002 ft/ft
<br />      		Maximum reported concentrations of MtBE and TBA during the second quarter 2004 were 28 ppb
<br />      		(MW-11) and  100,000 ppb (MW-7),  respectively    Concentrations of MtBE, TPHg,  and TBA
<br />      		continue to decline in site monitoring wells   MtBE concentrations in wells MWA, MW-3, MW-4,
<br />      		MW-5, MW-6, MW-7, MW-11, and MW-13 continue to decline (from a historical maximum of
<br />      		233,000 ppb to a current maximum of 28 ppb)   TBA concentrations in wells MW-1, MW-3, and
<br />      		MW-7 continue to decline from a historical maximum of 240,000 ppb to a current maximum of
<br />      		100,000 ppb   TBA concentrations in well MW-11 appear relatively stable   Based on MtBE and  			j
<br />      		TBA isoconcentration maps (Figures 5 and 6 in Attachment A), these constituents are not
<br />      		delineated to the northeast of the site (in the area of Shell well S-2)   SECOR recommends that
<br />      		during point sampling with Shell, ConocoPhillips' sampling contractor collect split samples from
<br />      		Shell wells S-2 and S-5 and analyze for fuel oxygenates to determine the delineation of MtBE and
<br />      		TBA
<br />      		REMEDATION STATUS
<br />      		The ozone infection system consists of a panel mounted KVA C-SpargeT"' System that produces
<br />      		4 grams per hour(0 009 pounds per hour) of ozone The system infects ozone to ten ozone wells
<br />      		SP-A through SP-H, SP-J, and SP-K  The system was placed into operation on December 20,   			`
<br />      		2001  During the current quarter the system operated for 1,309 hours, resulting in 75% runtime
<br />      		Ozone infection system operational data is included as Table B-1 in Attachment B
<br />      		The performance of the ozone infection system is evaluated based on the results of regular
<br />      		groundwater sampling  Monthly groundwater samples were collected from monitoring wells MW-3
<br />      		and  MW-4  on  April  23,  May  19,  and  June  21,  2004,  and  analyzed  for  total  petroleum  			,
<br />       		hydrocarbons as gasoline (TPHg), benzene, toluene, ethylbenzene, and total xylenes (BTEX
<br />      		compounds), methyl tert-butyl ether (MtBE), and tert-butyl alcohol (TBA)   Monthly sampling of  			q
<br />      		wells  MW-3 and  MW-4  indicate that  ozone  sparg+ng  continues to  be effective  in  reducing
<br />       		concentrations of dissolved petroleum hydrocarbons   Results of monthly groundwater sampling  			.i
<br />       		events are summarized in Table B-2  Concentration versus time graphs for dissolved TPHg,   			s
<br />       		benzene, MtBE, and TBA in monitoring wells MW-3 and MW-4 are provided in Figures B-1 and B-
<br />       		2   Remediation field data sheets and certified laboratory analytical reports and chain-of-custody
<br />       		documentation are provided in Attachment C
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