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4eologccat Rcknics Inc Page 3 <br /> ' GW Monitoring Report <br /> Ted Peters-AST <br /> Project No 7012 <br /> April 24,2002 <br /> ' 1999, and February 17, 2000 The northeasterly flow direction in February 2001 is <br /> anomalous to the dominant westerly direction observed for the other monitoring events <br /> ' The field technician noted that free product (approximately 0 2 inch) was present in well <br /> MW-5, which may have resulted in an anomalous water table level measurement in the well <br /> ' Well MW-5 data are anomalous for the March 2002 event and are omitted from the contour <br /> diagram included in Figure 2 <br /> A gradient was also calculated from the three wells installed at the front of the site to <br /> ' investigate the UST area The gradient in this area was 0 001 ft/ft flowing S570W This is <br /> anomalous to the other monitoring events completed during the investigation The gradient <br /> has consistently trended to west to northwest in the past <br /> ' An examination of the AST area indicates that for the last three events the gradient was <br /> northwesterly This suggests that previous calculations were affected by the spatial <br /> ' orientation of the AST wells, the presence of free product in MW-5, or a combination of <br /> both It is also possible the local domestic wells located west of this property are <br /> influencing the gradients at the site <br /> ' A domestic well survey within 2,000 feet of the site was completed on August 16, 2000 <br /> The survey efforts resulted in the identification of numerous domestic wells on the <br /> residential properties to the southwest, west and northwest of the site Ten wells were <br /> M located in the properties to the immediate west of the subject site and their locations are <br /> identified in our "Well Receptor Report" dated September 11, 2000, (submitted to the S]C- <br /> PHS/EHD and the CRWQCB-CVR) <br /> ' 2.2 Groundwater Sampling Procedure <br /> On March 18, 2002, Don Light of Del Tech Geotechnical Support arrived on-site, opened <br /> ' the wells and measured the depth to water with an electrically actuated sounding tape The <br /> water level reading was recorded to an accuracy of 0 01 foot <br /> The wells were then purged of at least 3 well volumes of stagnant water using a centrifugal <br /> ' pump Purging continued until the temperature, conductivity and pH of the groundwater <br /> had stabilized (c10% variation among three readings) indicating that formation water <br /> representative of aquifer conditions was entering the well These water quality parameters <br /> ' were measured at intervals of each well volume purged The logs are included in Appendix <br /> C <br /> ' A stainless steel bailer was used to collect a sample from each well Care was taken to <br /> minimize sample agitation from the initial filling of the bailer to the transfer of the sample <br /> to the VOA vial and glass amber liter bottles Once the sample container was filled and <br /> capped, the bottle was then inverted, tapped and checked for headspace bubbles The <br /> ' sample container was then identified and labeled with a unique designation, inserted into <br /> foam holders and placed in an ice chest cooled to 4°C for transport to the laboratory <br /> ' All non-disposable sampling equipment was decontaminated using a steam cleaner before <br /> and between uses Disposable gloves were used by the technician to collect all samples and <br /> were changed after each sample was collected <br /> r <br /> 1 <br />