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. The augers and sampling equipment were steam cleaned prior to drilling the boring and the <br /> sampling equipment was washed with a TSP solution and rinsed in clean water between each <br /> sampling interval <br /> PRESERVATION OF SOIL SAMPLES <br /> The ends of the brass sleeves containing the soil samples were sealed with a teflon film and further <br /> protected with plastic caps Each sleeve was labeled with site name, date, time, sample location, <br /> and analyses to be performed Each labeled soil sample was placed in a separate zip lock bag, <br /> deposited in and ice chest, and cooled to 4° C The soil samples and accompanying chain of <br /> custody documentation were delivered to North State Environmental Analytical Laboratory (NSE), <br /> DHS# 1753, on March 27, 1998 <br /> COLLECTION OF GROUNDWATER SAMPLES FROM TH1 <br /> Two groundwater samples were collected during the drilling of TH1 using "hydropunch" <br /> techniques The water samples were collected from the two foot screened interval of the <br /> hydropunch tool at the depths of 33-35 feet bgs and 43-45 feet bgs <br /> The auger and bit were advanced to three feet above the top of the desired sampling interval at <br /> which point a hydropunch tip and screen was inserted through the hollow stem auger at the end of a <br /> hollow rod and driven five feet into the formation at the base of the test hole The covering of the <br /> screened interval of the hydropunch tool was then retracted two feet to allow groundwater to enter <br /> the tool Groundwater samples were collected from the screened tip of the hydropunch tool with a <br /> mini bailer through the hollow rod The water samples were decanted into 4 VOA vials with no <br /> airspace and preserved with 0 5 ml of HCL The water samples were labeled and preserved as <br /> described above for the soil samples <br /> Groundwater inside the hollow stem auger had risen to approximately 15' bgs at the time of the first <br /> hydropunch water sample collection at 33-35 feet bgs Groundwater inside the hollow stem auger <br /> was measured at 25 feet bgs when the second hydropunch water sample was collected at 43-45 feet <br /> bgs This suggests that the clay and silt drill cuttings generated between 25 and 40 feet bgs <br /> partially sealed off further entry of groundwater into the borehole after its initial entry when the <br /> boring was advanced to 25 feet bgs <br /> CERTIFIED LABORATORY ANALYSES OF SOIL AND GROUNDWATER SAMPLES <br /> NSE analyzed the four soil samples and two groundwater samples for concentrations of Total <br /> Petroleum Hydrocarbons as Gasoline (TPH-G) using EPA method 8015 modified and BTEX <br /> (Benzene, Toluene, Ethylbenzene, and Xylenes) and MTBE (Methyl Tert-Butyl Ether) using EPA <br /> method 8020 NSE also analyzed both groundwater samples and soil sample TH1-25 5' (exhibiting <br /> highest TPH-G concentration) for concentrations of the oxygenants TBA, MTBE, DIPS, ETBE, <br /> and TAME using EPA method 8260 <br /> DESTRUCTION OF TH1 DISPOSITION OF CUTTINGS AND RINSATES <br /> Following soil and groundwater collection, Woodward Drilling Co grouted the soil boring TH1 to <br /> surface by tremae with neat cement and < 5% bentonite The displaced groundwater in the boring <br /> was captured before it reached the surface and pumped into two 55-gallon DOT approved drums <br /> . The approximately one half cubic yard of soil cuttings generated by the drilling of TH1 were stored <br /> on a base and under a covering of 6-mil visquine in a fenced compound at the rear of the site <br /> 3 SANCHEZ SRPT 5/11198 <br />