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KLEINFELDER <br /> 5 MONITORING RESULTS <br /> The depth to groundwater was measured in each monitoring well included in this event. The <br /> depth to groundwater data was converted to elevation in reference to mean sea level for the <br /> calculation of groundwater flow direction and gradient. <br /> The seven groundwater samples were submitted under chain-of-custody procedures to Sequoia <br /> Analytical Laboratories of Sacramento, California. Table 2 is a summary of the analytical results <br /> for groundwater. For a complete report of the analytical results please refer to the chain-of- <br /> custody forms and laboratory analytical reports included in Appendix C. <br /> I <br /> 5.1 WATER LEVELS <br /> On June 1, 2004, all twenty monitoring wells and three piezometers were sounded for depth to <br /> groundwater. The depth to groundwater ranged from 43.98 feet below the top of the well casing <br /> (MW-DIS-11s) to 55.80 feet below the top of the well casing (MW-DIS-15). <br /> The groundwater elevations ranged from —32.85 feet msl to —36.12 feet rnsl at the site. The <br /> groundwater gradient was calculated to be 0.006 feetifoot, with a general direction of flow <br /> towards the southeast, Plate 3 shows the interpreted groundwater contours. The reported <br /> groundwater flow direction has been consistent with the historical data collected at the site <br /> Please refer to Table 1 for the recorded groundwater elevations on June 1, 2004 and past <br /> monitoring events. <br /> I <br /> 5.2 ANALYTICAL METHODS AND REPORTED RANGES <br /> Each.of the groundwater samples collected were submitted for analysis. The following is a list of <br /> the requested analyses and the reported ranges for groundwater samples obtained from the <br /> monitoring wells sampled; <br /> 0 Total Petroleum Hydrocarbons as gasoline <br /> I by EPA Method 8015M/8021B [non-detect< 50 µg/1]; <br /> • Benzene by EPA Method 8015NU8021 B [non-detect <0.50 µg/11; <br /> • Toluene by EPA Method 8015MY8021B [non-detect< 0.50 [Lg/1]; <br /> • Ethylbenzene by EPA Method 8015M/8021B [non-detect< 0.50 µg/1]; <br /> • Xylene by EPA Method 8015NV8021B [non-detect<0.50 µg/1]; <br /> I • 1,2 DCA by EPA Method 8260B [non-detect <0.50 µg11 to 160 µg/]]; <br /> • EDB by EPA Method 8260B [non-detect <0.50 gg/1]; <br /> • TBA by EPA Method 8260B [non-detect<5.0 µg/1]; <br /> 12280.MONIST04R1092 Page 8 of 12 <br /> Copyright 2004 Kleinfelder,Inc. September 2,2004 <br />