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' <br /> Mr Nuel Henderson <br /> Page 3 of 9 <br /> ' approximately 4*C for transport to Argon under chain of custody protocol The samples were <br /> analyzed for total petroleum hydrocarbons as gasoline (TPHg) by EPA Method 8015, for <br /> ' benzene, toluene, ethylbenzene and xylenes (BTEX) by EPA Method 8020 and for gasoline <br /> oxygenate additives including 1,2-DCA and EDB using EPA Method 8260 <br /> ' Discrete Groundwater Sampling <br /> Discrete groundwater samples were collected from bonngs MW15A and MW15B during drilling <br /> ' to determine if contamination was present These data would determine whether or not the <br /> deeper well (MW15C) would be drilled with mud-rotary equipment and completed with <br /> conductor casing Samples were collected by driving a Hydropunch® groundwater sampler to the <br /> desired depth, and exposing the screen to the bed within the formation Small diameter Teflon <br /> tubing equipped with a stainless steel check valve was inserted into the rods to the bottom of the <br /> sampler Groundwater was brought to the surface by creating a positive displacement effect, and <br /> ' dispensed into labeled VOA vials containing hydrochloric acid preservative Subsequently the <br /> vials were placed into an ice chest refrigerated to approximately 4° Centigrade, and transported <br /> under chain of custody to Argon for analysis <br /> ' The groundwater samples were analyzed on 24-hour turnaround for TPH , BTEX and <br /> g p Y 8 <br /> • oxygenates using the appropriate EPA methodologies <br /> ' A Zone and B Zone Well Construction <br /> A Zone wells MW15A and MW16A were screened from approximately 35 to 55 feet below <br /> ground surface (bgs) B Zone wells MW13B, MW15B and MW16B and were screened from <br /> approximately 70 to 80 feet bgs The wells were constructed with 2-inch diameter, Schedule 40 <br /> ' PVC casing and 0 020 inch slotted screen The filter pack consisted of #3 silica sand The <br /> annular seals contained two to four feet of bentonite overlain by neat cement/bentonite grout to <br /> ' the ground surface The monitoring wells were secured at the ground surface with flush mount <br /> watertight well boxes and locking well caps Well construction details are depicted on the boring <br /> logs contained in Attachment A and summarized in Table 1 <br /> ' Mud Rotary Drilling <br /> Due to the presence of contaminants in discrete groundwater samples collected from wells <br /> MW15A and MW15B, it was decided that MW15C would be drilled using mud-rotary <br /> equipment in order to provide the highest degree of protection from cross-contamination From <br /> January 17 to January 21, 2003, V&W advanced one soil boring using a mud-rotary drilling ng <br /> The location of the well is shown on Figure 2 The surface hole was drilled with a 12 1/4 inch <br /> diameter rockbrt to a depth of 90 feet At this point a 6 % inch diameter steel conductor casing <br /> fitted with centralizers and lead by a grout shoe was cemented in place After the cement cured, <br /> the boring was deepened to a total depth of 121 feet bgs with a 6 inch diameter rockbrt <br /> ' 11GZA FSIVOL_11DATA1GROUNDZE-ROEKICLOSUREXRepofts\Add_HSA Mud wells doe <br />