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GENERAL FIELD PROCEDURES <br /> Groundwater Monitoring and Sampling Assignments <br /> For each site, TRC technicians are provided with a Technical Service Request (TSR) that specifies <br /> activities required to complete the groundwater monitoring and sampling assignment for the site. TSRs <br /> are based on client directives, instructions from the primary environmental consultant for the site, <br /> regulatory requirements, and TRC's previous experience with the site. <br /> Fluid Level Measurements <br /> Initial site activities include determination of well locations based on a site map provided with the TSR. <br /> Well boxes are opened and caps are removed. Indications of well or well box damage or of pressure <br /> buildup in the well are noted. <br /> Fluid levels in each well are measured using a coated cloth tape equipped with an electronic interface <br /> probe, which distinguishes between liquid phase hydrocarbon(LPH)and water. The depth to LPH(if it is <br /> present), to water, and to the bottom of the well are measured from the top of the well casing (surveyors <br /> mark or notch if present)to the nearest 0.01 foot. Unless otherwise instructed, a well with less than 0.67 <br /> foot between the measured top of water and the measured bottom of the well casing is considered dry, and <br /> is not sampled. If the well contains 0.67 foot or more of water, an attempt is made to bail and/or sample <br /> as specified on the TSR. <br /> Wells that are found to contain LPH are not purged or sampled. Instead, one casing volume of fluid is <br /> bailed from the well and the well is re-sealed. Bailed fluids are placed in a container separate from <br /> ;rr normal purge water,and properly disposed. <br /> Purging and Groundwater Parameter Measurement <br /> TSR instructions may specify that a well not be purged (no-purge sampling), be purged using low-flow <br /> methods, or be purged using conventional pump and/or bail methods. Conventional purging generally <br /> consists of pumping or bailing until a minimum of three casing volumes of water have been removed or <br /> until the well has been pumped dry. Pumping is generally accomplished using submersible electric or <br /> pneumatic diaphragm pumps. <br /> During conventional purging, three groundwater parameters (temperature, pH, and conductivity) are <br /> measured after removal of each casing volume. Stabilization of these parameters, to within 10 percent, <br /> confirm that sufficient purging has been completed. In some cases, the TSR indicates that other <br /> parameters are also to be measured during purging. TRC commonly measures dissolved oxygen (DO), <br /> oxidation-reduction potential (ORP), and/or turbidity. Instruments used for groundwater parameter <br /> measurements are calibrated daily according to manufacturer's instructions. <br /> Low-flow purging utilizes a bladder or peristaltic pump to remove water from the well at a low rate. <br /> Groundwater parameters specified by the TSR are measured continuously until they become stable in <br /> general accordance with EPA guidelines. <br /> Purge water is generally collected in labeled drums for disposal. Drums may be left on site for disposal <br /> by others, or transported to a collection location for eventual transfer to a licensed treatment or recycling <br /> facility. In some cases, purge water may be collected directly from the site by a licensed vacuum truck <br /> company, or may be treated on site by an active remediation system, if so directed. <br /> .,i <br />