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								       • 	contained less than 1 foot of water are Interpreted to be dry and are indicated as "dry" on Figure 3  Since
<br />  		wells VW-1 and VW-6 are screened in a shallower interval than the other upper water bearing zone wells,
<br />  		these two wells were not used in contouring   The groundwater level in VW-3 appeared anomalous and
<br />  		this well was not used in contour construction   Groundwater flow was generally to the south-southeast at
<br />  		a gradient of 0 103 ft/ft   Groundwater flow in the upper water bearing zone has been to the south,
<br />  		south-southeast, and toward the southwest during previous quarters
<br />  		GRO, benzene, and MTBE were reported In well VW-6   GRO was also reported in well MW-8, GRO and
<br />   		benzene were reported in wells MW-13, VW-2, and VW-3, and GRO and MTBE were reported In well
<br />  		VW-5   The highest concentration of GRO (26,000 pg/L) was reported in well VW-2, and the highest
<br />   		concentrations of benzene (1,900 pg/L) and MTBE (170 jig/L) were reported in well VW-6   1,2-DCA was
<br />   		reported in wells MW-8 (70 µg/L), VW-5 (0 78 µg/L), and VW-6 (88 pg/L)   TBA, TAME, DIPE, ETBE,
<br />   		EDB, or ethanol were not reported in any of the upper zone wells   Analytical results for the first quarter
<br />   		2005 are generally consistent with previous quarters   GRO, benzene, and MTBE analytical data for the
<br />   		samples collected on March 15, 2005, are presented in Figure 5   Analytical data were submitted to the
<br />   		State Water Resources Control Board as required by AB2886  The electronic delivery receipt Is attached
<br />   		in Appendix C
<br />   		Lower Water Bearing Zone Sand Zone 2
<br />   		During the site visit conducted on March 3, 2005, free product was measured in well MW-1 at a thickness
<br />   		of 0 02 feet, and during the site visit on March 14, 2005, free product was measured in well MW-15 at a
<br />   		thickness of 0 02 feet  Approximately 2 gallons of product/water mixture were manually bailed on March
<br />   		14, 2005, and stored In a properly labeled DOT approved drum pending disposal  Approximately 200
<br />   		gallons of product/water mixture has been manually balled to date  Product thickness measurements and
<br />   		volumes of liquid bailed are summarized In Table 1
<br />   		At the time of the first quarter 2005 monitoring event, groundwater levels had decreased 0 04 feet in well
<br />   		MWA, and Increased between 0 05 and 0 18 feet In wells MW-10, MW-12, and MW-15 since the previous
<br />   		monitoring event (December 20, 2004)    Depth-to-water measurements were normalized to mean sea
<br />   		level (MSL) and used to construct a groundwater elevation contour map (Figure 4)   Wells that contained
<br />   		less than 1 foot of water are interpreted to be dry and are indicated as "dry" on Figure 4   Groundwater
<br />   		flow was  generally to  the  east at  a  gradient of 0 036  ft/ft    Groundwater flow  has  been  to  the
<br />   		east-southeast and east during previous quarters
<br />   		GRO and benzene were reported in wells MW-10 and MW-12   The highest concentrations of GRO
<br />    		(69,000 µg/L) and benzene (9,600 pg/L) were reported in well MW-12  MTBE, TBA, TAME, DIPE, ETBE,
<br />    		EDB, 1,2-DCA, or ethanol were not reported in any of the lower zone wells  Analytical results for the first
<br />   		quarter 2005 are generally consistent with previous quarters   GRO, benzene, and MTBE analytical data
<br />    		for the samples collected on March 15, 2005, are presented in Figure 5  Analytical data were submitted to
<br />    		the State Water Resources Control Board as required by AB2886   The electronic delivery receipt is
<br />    		attached in Appendix C
<br />    		Domestic Well
<br />    		GRO, BTEX, MTBE, TBA, TAME,  DIPE, ETBE,  EDB,  1,2-DCA, or ethanol were not reported in the
<br />    		domestic well   GRO, benzene, and MTBE analytical data are presented in Figure 5   These analytical
<br />    		results for the first quarter 2005 are consistent with historical data
<br />    		SVE System Operation and Maintenance
<br />    		During December 2004 and January 2005, Stratus replaced the two 200 cfm King, Buck, & Associates
<br />    		SVE systems which operated at the site between March 2004 and November 2004, with a 500 cfm
<br />    		Solleco thermal oxidizer   The performance and operation summary of the two 200 cfm King, Buck, &
<br />    		Associates SVE systems are Included in Appendix D
<br />    		K Wp-Arco for UR5161001Quarterly120051Arco_6100_1 Q05 doc							STRATUS
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