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11 <br /> E-Z SERVE PETROLEUM MARUFTING COMPANY OF CALIFORNIA <br /> QUARTERLY GROUNDWATER MONITORING PROGRAM <br /> SAMPLING AND ANALYSIS PLAN <br /> I <br /> The following sections describe the procedures and protocols followed during this quarterly <br /> groundwater monitoring event at the subject site <br /> Depth-To-Water Measurements <br /> Prior to sampling the groundwater monitoring wells, the wells were opened to the atmosphere for <br /> approximately one-quarter of one hour, allowing the static water level well to adjust to the open <br /> barometric pressure The depth-to-groundwater was then measured, using an oil-water interface <br /> probe The interface probe was lowered slowly until free product or water was encountered At that <br /> point, the mark on the interface probe wire was read to the nearest 0 01 feet at the permanent reference <br /> point on the top of the well casing If free product was encountered, the probe was lowered until <br /> water was encountered The difference between the two depths corresponded to the thickness of the <br /> free product The total depth of the well was then measured using the same probe If the presence of <br /> free product was questionable, a second check for free-product was make using a disposable bailer <br /> The disposable banter was lowered into the water to approximately one-half the bailer length The <br /> bailer was then removed from the well and checked for the presence of free petroleum product or a <br /> product sheen <br /> . In the event a dedicated bailer or purge tubing existed in the well, the dedicated equipment was <br /> removed prior to sampling, and temporarily stored in a clean plastic garbage bag <br /> The depth-to-water and total depth measurements, and the presence or absence of free product, <br /> were recorded on the field sampling forms In addition, comments regarding the condition of the well <br /> and/or containment box were also noted on the field sampling sheet at that tune Wells observed to <br /> contain a product sheen or free product on top of the water column were purged but not sampled <br /> Groundwater Monitoring Well Purging <br /> The depth-to-water and bottom of well measurements were used to calculate the volume of <br /> purge water contained in one well volume The minimum purge volume was calculated to be three <br /> tunes the total well volume Once the minimum purge volume had been calculated, purging was <br /> started Purging was conducted using either a centrifugal pump connected to a dedicated Waterra® <br /> pump, a 2-inch diameter submersible pump, a bladder pump, or a disposable polyethylene bailer The <br /> type of equipment used to purge each well was selected based on the depth to water, the anticipated <br /> purge rate, the amount of sediment expected to be contained in the well, and the historical sampling <br /> records for each well The specific piece of equipment used was recorded on the Groundwater Sample <br /> Collection Record Temperature, pq and specific conductance of the purge water was monitored <br /> I during the purging process at regular intervals Purging was ceased when the monitored parameters <br /> stabilized (three consecutive reading not varying by more than 10-percent) and a minimum of three <br /> well volumes had been purged <br /> In the event a well dried out during purging, the well was allowed to recover to 80-percent of its I <br /> onguW well volume, or for 8-hours,whichever,was less, prior to collecting a groundwater sample ' <br /> I I <br /> I , <br /> ' I <br /> e SII I I' `I �I III � I <br /> II I <br /> 110 1 1 <br />