Laserfiche WebLink
S <br /> I17 April 2001 <br /> i AGE-NC Project No 99-0624 <br />' Page 2 of 4 <br /> 22 COLLECTION AND,ANALYSIS OF GROUNDWATER SAMPLES <br />' Water samples were collected from each monitoring well using new disposable bailers after allowing <br />' the wells to achieve a minimum 80% recovery of the pre-purge water volume The samples were , <br /> transferred Into laboratory-supplied 40-m1 EPA-approved VOA vials containing 0 5 ml 18% <br /> hydrochloric acid as a sample preservative The sample vials were then labeled with the monitoring <br /> I well designation,date,time of sampling and the sampler's initials The samples were transported in <br /> a chilled container under chain of custody to McCampbell Analytical, Inc (MAI), a California <br /> Department of Health Services(DHS)-certified analytical laboratory for analysis The samples were <br />' analyzed for <br /> + Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br />' Method 5030/8015 Modified, <br /> • Volatile aromatic compounds - benzene, toluene, ethylbenzene, and total xylenes (BTEX) <br />' and methyl tertiary butyl ether(MTBE) in accordance with EPA Method 8020, and <br /> • Fuel oxygenates - tertiary butanol (TBA), di-Isopropyl ether (D1PE), ethyl tert-butyl ether <br /> (ETBE), tert-amyl methyl ether (TAME), and MTBE in accordance with EPA Method <br /> lie 8260M <br />' 30. FINDINGS <br /> The ground water elevation in each well was determined by subtracting the measured depths-to- <br /> water from the surveyed casing elevations and are presented in Table 1 Ground water flow direction <br /> was determined by contouring the ground water elevations on a scaled site plan (Figure 2) <br /> I Hydrocarbon-Impact and MTBE-impact to ground water were assessed from laboratory analysis of <br /> the ground water samples <br />' 3 1 GROUND WATER ELEVATION AND GRADIENT <br /> IDepths to ground water ranged from 50 29 feet to 51 39 feet below the tops of the well casings <br /> Ground water elevations at the site ranged from 11 89 feet (MW-4) to 12 09 feet (MW-1) below <br /> mean sea level The top of the saturated zone occurred,within the screened intervals*of all the <br /> monitoring wells _ <br />' The ground water flow direction was determined by contouring the ground water elevation data The <br /> ground water underlying the site was Inferred to have an average gradient of 0 002 ft/ft, the flow <br /> . direction varied radially from a more southwesterly direction at the western half of the site to a more <br /> IAdvanced GeoEnvironmentaI,Inc <br /> i <br />