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.may <br /> 10`0 <br /> Manna Pro Stockton 2 <br /> Cluarterly Groundwater Monitoring Report <br /> January 1992 <br /> GroundmMter MonitorIng Data <br /> On October 2,1991,the six existing groundwater monitoring wells were monitored for depth-to-water(DTW). <br /> The DTW measurements were taken from surveyed points on the top of each well casing, which are <br /> referenced to a common datum (designated as 100 feet above mean sea level). During this monitoring <br /> event the DTW in the sic wells ranged from 41.25 to 43.4 feet. This corresponds to static water level <br /> elevations ranging from 57.77 to 59.68 feet above mean sea level (MSL). The results of groundwater <br /> monitoring are presented In Table 1. A potentiometric surface map as interpreted from the data in Table <br /> 1 Is preoented as Figure 1. As shown In Figure 1,the average groundwater gradient Is approximately 0.03 <br /> ft/ft towards the west-southwest In the site vicinity. The groundwater flow pattern suggests hydraulic <br /> mounding near,and potentially related to,the tank excavation. <br /> GroundwWor Qualkv Data <br /> The six monitoring wells were sampled on October 2, 1991 following groundwater level monitoring. Prior <br /> to sampling, the welis were purged by balling to enable collection of samples representative of aquifer <br /> conditions. The standard protocol for sampling Is to purge 3 to 5 well casing volumes prior to collecting <br /> samples. However,when a well Is bailed dry before 3 to 5 casing volumes are removed,the water level in <br /> the well is allowed to recharge to approximately 80 percent of static water level prior to collecting samples. <br /> All six wells balled dry after bailing between 10 and 15 gallons of water from each well as shown in Table <br /> 2. <br /> + Samples were collected using a Teflon TM bailer and placed Into sample containers supplied by the laboratory <br /> performing the analyses.pe alyse . Sam lin <br /> p g equipment was cleaned between wells using an AlconoxT""and water <br /> wash and delonized water rinse. Samples were labeled and placed in an ice-chilled cooler for transport to <br /> GTEL Environmental Laboratories,Inc.In Concord,California,and were accompanied at all times by a chain- <br /> of-custody record. <br /> Samples from the October 2, 1991 sampling event were analyzed for the following parameters: <br /> • pH using Standard Method 4500 H <br /> • Specific Conductance using Standard Method 2510 <br /> • Aromatic Volatile Organics and Total Petroleum Hydrocarbons as Gasoline using EPA <br /> Methods 5030,8020 and Modified 8015. <br /> • Total Petroleum Hydrocarbons as Diesel Fuel using Modified EPA Methods 3510/8015 <br /> • Total Lead using EPA Method 7421 <br /> The results of laboratory analyses are presented In Table 3. The laboratory analytical reports are also <br /> Included as an attachment to this letter. As shown in Table 3, pH ranged from 7.1 to 7.9. Specific <br /> --- conductance ranged from 980 to 2,_4.00 micro-mhos per eentlmeterat 25 degrees Centigrade(umno/cm,25)..--- ------ —.---- — —.— -= <br /> --- ------ Because the results of pH and specific conduct=ance in the samples collected were generally similar, this <br /> suggests that the water Is from the same hydrologic zone. <br /> �.J <br /> ` =GROUNDWATER <br /> TECHNOLOcY,INC, <br />