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Monitoring Well Installation Report Page 3 <br /> „h Appendix A <br /> f Project No.336.2 <br /> November 13, 1995 <br /> j 2.5 Sample Analysis <br /> Samples will be analyzed for benzene, toluene,ethyl benzene and total xylenes(BTEX),EPA methods <br /> 8020 and 602,and for total petroleum hydrocarbons as diesel,EPA method 3540/8015 modified. The <br /> analyses will be performed by Sherwood Laboratories of Hilmar.,California State Certification#1400. <br /> 2.6 Data Reduction <br /> Analytical data will be integrated with the geological data gathered during field investigation. Cross <br /> sections will be prepared to illustrate the stratigraphy and the distribution of soil contamination. The <br /> cross sections may be used for interpreting the extent of contamination. <br /> -:i <br /> 2.7 Groundwater Sampling Procedure <br /> Groundwater sampling procedure is as follows: Arriving on site the stainless steel submersible <br /> pump/stainless steel bailer is assembled and the sampling equipment prepared. The wells are <br /> - unlocked,opened,and depth to water is measured from the top of casing. <br /> Ii <br /> As a matter of procedure,the following actions are taken to evaluate the presence of floating product, <br /> or third phase contaminant material on the groundwater. If field evidence suggests that floating <br /> product may be present(i.e., the well has a strong odor of hydrocarbons and gasoline is observed on <br /> the water meter probe), then either a bailer or product/water interface meter is used to measure the <br /> thickness of floating product on the surface of the groundwater. In the event that floating product is <br /> present, that well would not be sampled unless specifically requested. <br /> t;s <br /> The pump/bailer is inserted into the well,lowered, to a depth of 6 to 8 inches above the bottom and <br /> activated. Water flow is monitored visually for cloudiness and measured for flow rate, temperature, <br /> =:== conductivity,and pH. At least three well volumes are purged from the well prior to sampling until <br /> i==1 pH,conductivity,and temperature had stabilized to ensure sampling from representative formation <br /> water. <br /> After stabilization of water parameters, the well is allowed to recharge. Prior to sampling the well,a <br /> bailer blank is collected by pouring water provided by the laboratory into the bailer and emptying it <br /> into a sample vial. Sampling is accomplished by using a stainless steel bailer attached to a coated, <br /> stainless steel cable. The bailer is slowly lowered into the well and carefully allowed to fill with <br /> water. After filling, the bailer is carefully raised from the well taking precaution not to agitate the <br /> contained water. An emptying device was coupled to the bailer and the water was slowly transferred <br /> into I:- appropriate ro riate samP le containers (40 ml VOA vials/amber liters). The sample vials provided by <br /> the laboratory contain 4 to 5 drops of hydrochloric acid to retard possible biological degradation. The <br /> vial is capped,inverted,and tapped to check for air bubbles. <br /> After assuring that bubbles are not present, the vial is labeled and inserted into a closed-cell foam <br /> holder and placed in an ice chest, cooled to 4° Celsius, for transport to the laboratory. To monitor <br /> possible cross contamination from any source, a trip blank prepared from water provided by the lab, <br /> is carried throughout the sampling,storage,and shipping process. <br />