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MIN <br /> assessing sufficient purging. Purging is continued until all three physical parameters <br /> have stabilized. Specific conductance (conductivity) meters are read to the nearest±10 <br /> umbos/cm and are calibrated daiiy• pH read to the nearestmeters are read to the 0.1 °F.earest Calibration on of physI pH units ical <br /> are calibrated daily. Temperature is <br /> parameter meters will follow manufacturer's specifications. Collected field data during <br /> purging activities will be entered on the Well Sampling Field Data Sheet. <br /> In Ijw yield formations, the well is purged such that the "standing" water is removed <br /> and the well is allowed to recharge. (Normal field measurements will be periodically <br /> recorded during the purging process.) In situations where recoveryto 80% of static <br /> water level is estimated, or observed to exceed a two hour <br /> satnplenfoon e each parametere will . <br /> Attempts <br /> collected when sufficient volume is available for a <br /> Attempts will be made so the well is not purged dry such that the recharge rate causes <br /> the formation water to cascade into the well. <br /> In wells where free-phase hydrocarbons are detected, the free-phase portion will be <br /> bailed from the well and the estimated volume removed recorded. A groundwater <br /> sample will be collected if bailing reduces the amount of free-phase hydrocarbons to the <br /> point where they are not present in the well. Well sampling will be conducted using <br /> one of the aforementioned methods depending on the formation yield. However, if <br /> free-phase hydrocarbons persist throughout bailing, then a groundwater sample will not <br /> be collected. <br /> ir <br /> sage through the <br /> Volatile organic groundwater samples arecollected <br /> olatiles fromabeingsstripped from the does not occur or is minimal (to prevent <br /> samples): sample bottles are filled by slowly running the sample down the side of the <br /> bottle until there is a positive convex meniscus over the neck of the bottle; the teflon <br /> side of the septum(in cap) :s positioned against the meniscus, and the cap screwed o. <br /> tightly; the sample is inverted and the bottle lightly tapped. The absence of an air <br /> bubble indicates a successful seal; if a bubble is evident, the cap is removed, more <br /> sample is added, and the bottle is resealed. <br /> Chain-of-Custody <br /> Groundwater sample containers are labeled with a unique sample number, location, and <br /> date of collection. All samples are logged into a chain-of-custody form and placed in a <br /> chilled ice chest for shipment to a laboratory certified by the State of California <br /> Department of Health Services, <br /> RESNA INDUSTRIES, INC. <br /> Groundwater Sampling Protocol <br /> Latest Revision: October 23, 1991 <br /> I low <br /> — .�� <br />