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6. Extractable organics <br /> 7. Total metals <br /> 8. Dissolved metals <br /> 9. Phenols <br /> 10. Cyanide <br /> The specific analytical methods to be utilized for the common <br /> volatile/semivolatile to analyses are shown on Table 2. <br /> Groundwater samples will be collected with a Teflon bailer <br /> equipped with a bottom emptying device. Duplicate samples <br /> will be transferred to vials or containers that meet Regional <br /> Board specifications (Table 1) . Groundwater from the bailer <br /> will be transferred to the sample container by allowing the <br /> fluid to flow slowly along the sides of the vessel. All <br /> containers will be filled above the top of the opening to <br /> form a positive meniscus. No head space should be present in <br /> the sample container once it is sealed. If it is not possi- <br /> ble to collect a sample without head space, the problem will <br /> be noted on the field technician's sampling log. <br /> Immediately following sample collection, samples will be <br /> labeled and stored in an ice chest containing crushed ice <br /> sealed in plastic bags . Sample labels will contain the <br /> following information: date, time, project ID, sample ID, <br /> name of sampler and type of analysis. All samples will be <br /> transported under chain-of-custody protocol to a state certi- <br /> fied laboratory within 48 hours, or whenever possible. <br /> Samples will be transported either by site personnel or by <br /> private carrier. Analytical holding times will be considered <br /> in determining sampling and shipping schedules. Friday ship- <br /> ment/ Saturday laboratory receipt of samples will be coordi- <br /> nated in advance with the laboratory. <br /> QAQC2 <br />