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4.3 GROUNDWATER SAMPLING AND ANALYSIS <br /> 4.3.1 SAMPLING ACTIVITIES <br /> Groundwater elevations will be measured using an electronic water sounder. Prior to measuring <br /> groundwater at each well, the instrument will be decontaminated using a triple rinse process to <br /> ensure that no cross contamination between wells occurred. For each of the monitoring wells <br /> onsite, the groundwater level and the total depth of the well will be measured and recorded on <br /> well sampling forms. <br /> Groundwater will be sampled from each monitoring well based on the US EPA document titled <br /> Low-Flow (Minimal Drawdown) Ground-Water Sampling Procedures (EPA/540/S-95/504). This <br /> low-flow methodology will be used in order to prevent the following: mixing of the stagnant <br /> casing and fresh screen waters during insertion of sampling device; disturbance and re- <br /> suspension of settled solids at the bottom of the well when using high pumping rates and raising <br /> and lowering the pump and bailer; degassing from the bailer during sample handling and <br /> transfer; and introduction of the trace organics from the tubing and pump materials <br /> construction. <br /> A portable low-flow pump, with a pumping rate less than 0.5 Liters/minute, will be lowered into <br /> the monitoring well and placed approximately at the middle of the screened interval. To ensure <br /> that no cross contamination between wells occurs, the pump and any portable hosing will be <br /> decontaminated using a triple rinse process prior to purging each well. <br /> A low flow pump and flow-through cell will be used to monitor the stabilization of the field <br /> parameters. Using a water quality monitor (Hor(ba U-10 or equivalent) in combination with the <br /> flow-through cell device, the groundwater will be monitored in the field for the stability of pH, <br /> temperature, electrical conductance, and turbidity (in that order). These values will be <br /> recorded on well sampling logs. Well purging continues until stable values are obtained (+/-0.1 <br /> pH, +/-3% for conductivity, and +/- 10%for turbidity). Purged groundwater will be stored onsite <br /> in labeled, 55-gallon, Department of Transportation (DOT) approved drums. Once stability has <br /> been achieved, a water sample from each well will be pumped directly from the tubing into <br /> appropriate sample containers, supplied by the laboratory. In addition, trip blanks will be <br /> collected for quality assurance and quality control (QA/QC). After the samples are collected, <br /> they will be uniquely identified and placed into a cooler containing ice as described in the <br /> Sample Collection and Analysis Plan (Miller Brooks, 2007). The groundwater samples will be <br /> transported, by courier, to Calscience Environmental Laboratories (Calscience) in Garden <br /> Grove, California under chain of custody protocol. <br /> 4.3.2 LABORATORY ANALYSES <br /> A total of two samples will be collected from the newly installed off-site groundwater monitoring <br /> wells. All samples will be submitted to the laboratory for the following analyses: <br /> 7 M/LLER APAWOKS <br /> P:\707 Cove Contractors\WDR\Tech Report and WP 2008\Tech Report and WP_FINAL.doc <br />