Laserfiche WebLink
Project No. 034-98081 1 <br /> Page No. 8 <br /> ;I <br /> 7. During the drilling process, snit samples will be! subjectively analyzed for odor <br /> and discoloration. Additionally, soils will be field screened with h a portable <br /> photoionization detector (PID). The PID readings will be recorded on soil <br /> boring.logs. The PID is a direct reading real-time analyzdr capable of detecting- <br /> most <br /> etectingmost of the volatile hydrocarbon constituents present in the vapor phase of <br /> petroleum-affected soils. 1 ?I <br /> 8. Following sample retrieval from the soil borings, Teflon® film will be placed <br /> over both ends of each sleeve. Each sleevewill be sealed with tight fitting <br /> plastic caps that were secured with adhesiveless tape. <br /> it <br /> 9. Samples will be labeled witl the project number, the sampler's initials, the <br /> boring number, and the time and depth at which the sample was obtained. � <br /> 10. Following sample labeling, each sample will be.placed into an ice chest and <br /> maintained at a temperature of approximately 4° Celsius, to limit the <br /> volatilization of any PHCs present. <br /> 11. The soil borings will be backfilled with neat cement. <br /> I3; <br /> LI 12. Soil samples from 20, 30, and'40 feet bgs will be collected and submitted for <br /> analysis of PHCs. Soil samples will be collected, maintained, and transported <br /> under chain-of-custody protocol to a state-certified laboratory for chemical <br /> analysis. Selected soil samples will be analyzed for the presence and <br /> concentration of benzene, toluene, ethylbenzene xylenes, (BTEX), and total <br /> petroleum hydrocarbons as gasoline(TPH-G). <br /> 13. Groundwater samples will be collected by pushing a Hydropunch® sampling <br /> device to the target depth (gz45 feetbgs) and retracting the drill rod to allow <br /> groundwater to enter the sampling device. A water sample will be bailed from <br /> the device and transferred'to appropriate containers for delivery to the analytical <br /> Llaboratory. If groundwater isI slow to recharge�j the Geoprobe® rod will be <br /> completely removed and a PVC casing with screen will be inserted into the <br /> borehole to allow groundwater recharge while other Geoprobe holes are <br /> advanced. Sample analyses and handling will follow the methods stated above <br /> for soil samples. <br /> i� <br /> Phase II <br /> i� <br /> 14. Three groundwater monitoring wells will be installed during this assessment. <br /> The proposed locations of the wells are shown on-Figure 3. The total depths of <br /> the wells will be based on the existing depth to groundwater, which is assumed <br /> to be approximately 40 feet bgs, and on the 'anticipated vertical seasonal <br /> fluctuations of the water table. It is anticipated that the wells will be <br /> approximately 55 feet in depth. The wells will be constructed of 2-inch <br /> diameter Schedule 40 PVC water well casing and:screen. The screen interval <br /> KRAZAN&,ASSOCIATES,INC. <br /> Offices Serving the Western United States <br /> a!I 3498081.WP ' <br /> -• - ._.. _ .. � it <br />