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CA ARNG Field Quality Assurance Project Plan <br /> 9.1.5 Groundwater Sample Collection Procedures - - <br /> 9.1.5.1 Prior to initiating groundwater sampling,a water level survey may be conducted to measure <br /> groundwater flow directions and horizontal gradients.Figure 9-1 (at the end of the section)is an example <br /> of a water level log. All measurements will be taken from the north side of the casing or as indicated <br /> (notched mark).Water levels in all wells and piezometers will be measured to the nearest 0.01 foot using <br /> an electronic water level sounder. All water levels will be measured within 72 hours to provide an <br /> accurate view of groundwater flow direction.These measurements will be used to produce potentio- <br /> metric surface maps for each horizon.The sounder will be decontaminated as discussed in Section 9.3. <br /> Monitoring Well Samples <br /> 9.1.5.2 Newly installed wells will be sampled no sooner than two days after well development.After <br /> that,wells will be sampled in the order of least expected contamination to highest expected contamina- <br /> tion whenever possible to minimize the potential for any cross contamination. Prior to beginning <br /> sampling activities, the waterproof,expanding well cap on the well casing will be removed and the well <br /> will be checked for organic vapors with an organic vapor analyzer(OVA) or photoionization detector <br /> (PID) meter at the well head.The water level and the depth of the well will be measured and the values <br /> obtained will be used to calculate the required purge.volume. <br /> 9.1.5.3 A minimum of three submerged well casing volumes will be removed during purging of the <br /> monitoring well using a submersible pump.Water quality measurements, including pH,specific <br /> conductivity(SC), temperature, and turbidity,will be performed periodically on samples of the discharge <br /> water. These measurements are collected at a minimum of five times(unless well purges dry)over an <br /> evenly spaced time interval of the required purge.Results will be noted on a purge log(Figure 9-2 at the <br /> end of the section). <br /> 9.1.5.4 Once the well is sufficiently purged and the measured parameters have stabilized,the well will <br /> be considered ready for sampling.Field parameters will be considered ready for sampling. Field <br /> parameters will be considered stabilized when less than 10%change in SC; less than 0.2 unit change in <br /> pH;and less than 1°C change in temperature between consecutive measurements is recorded. If the water <br /> level in a well does not recharge to within 80%of the static water level within one hour,it will be <br /> considered impractical to purge the well of three well volumes and the well will be pumped dry once <br /> more and sampled as soon as 80% recharge has occurred. <br /> Portable Submersible Pump(Port-a-Reel System) <br /> 9.1.5.5 An electric submersible pump(2-inch Grundfos®pump) or stainless steel bailer and/or a <br /> Teflon®bailer are used to purge water and collect samples at wells not equipped with dedicated systems. <br /> The pump is typically used to purge the groundwater while the Teflon®bailer is used for groundwater <br /> sample collection.A flow control valve attachment at the bottom of the bailer is used to transfer the <br /> sample to the sample containers.The equipment required to purge and collect groundwater samples are: <br /> • Submersible pump(2-inch Grundfos®pump attached to a portable hose reel); <br /> • Water level, PID or OVA,pH,temperature,specific conductivity,and turbidity meters; <br /> • Electrical generator; <br /> • Wastewater container; <br /> field QAPP.DOC 94 May 2000 <br />