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Ms. Linda Turkatte <br /> June 11, 1996 <br /> Page 4 <br /> feet above mean sea level(msl)from Texaco survey data. Well elevation data and calculated groundwater ' <br /> elevation data are included in Table 1. <br /> Groundwater monitoring well MW-1 was developed and-sampled on February 7, 1995. The well was <br /> developed by alternately bailing and surging. Well development continued until the groundwater was <br /> reasonably free of sediment. Ten casing volumes of water were removed during well development. During <br /> well development, measurements and observations of pH, electrical conductivity,temperature, color,and <br /> turbidity were recorded and are included on a Groundwater Sample Field Data Sheet(Attachment B). <br /> Following well development,SECOR collected a groundwater sample from the monitoring well MW-1 for <br /> chemical analysis. Prior to.sampling the well was allowed to recover to 80%of the initial water level prior <br /> to development. The groundwater sample was collected using a disposable PVC bailer and decanted.directly <br /> into laboratory-supplied sample containers.. Each of the sample containers was labeled, sealed in:plastic <br /> bags, and placed in an ice-filled.cooler. The sample was submitted to Superior,along with a completed <br /> chain-of-custody record and was analyzed for TPHg and BTEX by EPA;Methods 8015,modified and 8020,. <br /> respectively. <br /> Decontamination, and Material Containment <br /> To minimize the potential for cross-contamination,soil sampling and groundwater development,equipment <br /> were washed in a dilute trisodium phosphate (TSF') solution, rinsed in fresh water, and final rinsed:with <br /> distilled water or steam cleaned between each drilling or sampling location. Because groundwater,samples <br /> were collected with pre-cleaned dedicated bailers,decontamination between•groundwater sampling locations <br /> was not required. Downhole drilling equipment was steam-cleaned between'each borehole location in`a <br /> designated area prepared to contain rinsate. The water-level indicator was rinsed with deionized water <br /> between well,soundings to prevent cross-contamination. <br /> Soil cuttings generated during field activities were stockpiled on and covered with visqueen on-site pending <br /> appropriate.disposal. All water generated during well development, sampling, and decontamination was <br /> temporarily stored in 55-gallon drums at an on-site location pending appropriate disposal-. <br /> SUBSURFACE CONDITIONS <br /> Evaluation of subsurface conditions for this Site investigation is based on data collected from the four <br /> boreholes advanced in the vicinity of the former Site USTs(MW-1,VE-1, SB-1 and SB-2), soil chemical <br /> data collected during UST removal activities in February 1994; and from three Texaco groundwater <br /> monitoring wells(MW-6,MW-8,and MW-14)located on or adjacent to the Site(Figure 3). Groundwater <br /> quality data was collected for well MW-1 by SECOR on February 7, 1996 and for wells MW-6,MW-8, and <br /> MW-14 by Blaine Tech on February 27, 1996. <br /> HASUMDRILL.RYT <br /> 50090-011-02 <br />