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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 with <br /> bottom emptying devices. Duplicate samples will be transferred <br /> to vials or containers that meet Regional Board specifications <br /> ( Table 1 ) . Groundwater from the bailer will be transferred to <br /> the sample container by allowing the fluid to flow slowly along <br /> the sides of the vessel. All containers will be filled above the <br /> top of the opening to form a positive meniscus. No head space <br /> should be present in the sample container once it is sealed. If <br /> it is not possible to collect a sample without head space, the <br /> problem will be noted on the field technician' s sampling log. <br /> Immediately following sample collection, samples will be labeled <br /> and stored in an ice chest containing frozen "blue ice" sealed in <br /> plastic bags . Sample labels will contain the following <br /> information: date, time, project ID, sample ID, name of sampler <br /> and type of analysis. All samples will be transported under <br /> chain-of-custody protocol to a state certified laboratory within <br /> 24 hours. A sample container filled in the laboratory with <br /> organic free water and carried unopened during the sampling trip <br /> will also be provided (Trip Blank) . A "high-low" temperature <br /> recording thermometer will accompany sample shipments to ensure <br /> proper sample temperature maintenance. <br /> Samples will be transported either by WaterWork personnel or by <br /> private carrier. Analytical holding times will be considered in <br /> determining sampling and shipping schedules. Friday shipment/ <br /> Saturday laboratory receipt of samples will be coordinated in <br /> advanced with the laboratory. <br /> QAQC1 <br />