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" Monitoring wells were protected with a traffic-rated, cast-aluminum utilit i uIpp%O*lthlJature <br /> PVC skirt. The box has a watertight seal to protect against surface-water infiltration and must be <br /> opened with a special wrench. The design of this box discourages vandalism and reduces the <br /> possibility of accidental disturbance of the well. <br /> Well Development <br /> We waited a minimum of 24 hours after well installation before developing the ground-water <br /> monitoring wells to allow the grout to seal. Before developing the monitoring wells, a water <br /> sample was collected for subjective analysis from near the water surface in the well with a Teflon <br /> bailer cleaned with a laboratory-grade detergent and deionized water. Floating product was not <br /> encountered. <br /> =; The wells were developed with a surge block and pump. Well development continued until the <br /> discharge water was clear of silt and sand. Clay-size sediments derived from the screened portion <br /> of the formation cannot be entirely eliminated by well development <br /> `' After the wells stabilized for a minimum of 24 hours, the wells were purged of stagnant water and <br /> a sample was collected for laboratory analysis. The well was purged of approximately 3 to 5 well <br /> s<_ volumes of water with a submersible pump, or until pH, conductivity, and temperature of the <br /> purged water had stabilized. Water purged from the wells was stored in labeled, 55-gallon, steel <br /> drums approved for this use by the Department of Transportation until suitable disposal options <br /> ._ were selected based on laboratory analysis. <br /> Ground-Water Sampling <br /> The static water level in each well was measured to the nearest 0.01 foot with a Solinst electric <br /> water-level sounder cleaned with a laboratory-grade detergent and deionized water before use in <br /> each well. A clean bailer was used to obtain a sample from the surface of the water in the well for <br /> subjective analysis of hydrocarbons. The sample was retrieved and examined for floating product, <br /> �-s sheen, color, and clarity. <br /> Approximately 3 well volumes (approximately 50 gallons) were purged from each well with a <br /> a stainless-steel electrical submersible pump to allow sampling of representative formation water. <br /> The pump, cables, and hoses were cleaned with a laboratory-grade detergent and water before use <br /> in each well. The wells were purged until pH, temperature, and electrical conductivity of the water <br /> stabilized, as measured by portable meters calibrated to a standard buffer and conductivity <br /> `rl standard. The water level was allowed to recover to at least 80 percent of the initial water level. A <br /> sample of the formation water then was collected from the surface of the water in each of the wells <br /> with the Teflon bailer and slowly transferred to laboratory-cleaned sample containers. The <br /> recovered fluids from sampling in each well were directed into type 17-E, steel, 55-gallon liquid <br /> waste drums approved for this use by the Department of Transportation. <br /> Water samples were stored in laboratory-cleaned, 40-milliliter glass vials or other appropriate <br /> containers that contained a preservative, such as hydrochloric acid. The water samples were sealed <br /> with Teflon-lined lids so that no air bubbles were detected. The sample containers were labeled in <br /> k_ - the field with the job number, sample location and depth, and date, and promptly placed in iced <br /> => storage for transport to the laboratory. Chain of Custody Records were initiated in the field by the <br /> geologist and accompanied the samples to a laboratory certified by the State of California for the <br /> analyses requested. Samples were transported promptly to an approved laboratory. <br />