Laserfiche WebLink
S E C 0 R <br /> a, <br /> . On August 8, 9 and 10, 2001, GR installed four groundwater monitoring wells, three offsite and <br /> one deep onsite (MW-8 through MW-11) The three shallow offsite wells were installed to depths a <br /> ranging from 28 to 29 feet bgs The deep well, MW-11, was installed to a total depth of 79 feet <br /> bgs Soil samples collected from well borings MW-8, MW-9 and MW-10 were reported as ND for <br /> all analytes Sod sample MW-11-14, collected at 14 feet bgs, contained 1 7 parts per million ; <br /> (ppm) of MtBE Groundwater samples collected from wells MW-8, MW-9 and MW-10, were <br /> reported as ND for all analytes The only analyte detected in groundwater from well MW-11 was <br /> r <br /> MtBE at a concentration of 110 ppb (EPA Method 8260) <br /> On December 3 through December 7, 2001, SECOR International Incorporated (SECOR) <br /> performed a dual-phase extraction (DPE) event at the site The DPE was performed on wells <br /> MW-3 and MW-7, and operated for a total of 110 hours Flow rates during the test varied from <br /> 10 90 to 33 41 cubic feet per minute (cfm) and vacuum rates varied from 24 to 25 inches of <br /> mercury (in Hg) Over the course of the five day event, SECOR reportedly removed a total of 0 <br /> pounds (lbs) of TPHg, 0 01 lbs of benzene, and 6 64 lbs of MtBE The amount of hydrocarbons <br /> removed is based on laboratory samples collected during the test SECOR determined that the <br /> vacuum radius of influence was between 36 and 60 feet Approximately 20,830 gallons of <br /> groundwater were extracted during the DPE event Based on the low mass removal achieved <br /> with this test, SECOR concluded that DPE is not an effective remedial alternative for this site <br /> In December 2002, GR installed monitoring wells MW-12 and MW-13, and sparge points SP-A <br /> through SP-H, SP-J, and SP-K, and installation of two CPT probes (CPT-2 and CPT-3) to a <br /> maximum depth of approximately 140 feet bgs The CPT rig was equipped with an onboard G n <br /> computer system that provided a real time analysis of the subsurface conditions The CPT <br /> device creates a lithologic log of the boring by comparing the CPT tip resistance to sleeve friction <br /> on the CPT cone <br /> After collection of lithologic data, a groundwater sampling probe was advanced in a separate <br /> location (approximately 3 feet from the original probe) to obtain depth discrete groundwater <br /> samples The target depths of the discrete samples were determined utilizing lithologic <br /> information obtained from the advancement of the CPT At the target depth for groundwater <br /> sample collection, the sampling device retracts to expose disposable PVC screen allowing <br /> groundwater to enter the device Each groundwater sample was collected using a precleaned <br /> teflon bailer and then decanted into laboratory supplied containers Samples were handled as <br /> described in Appendix A CPT-2 had groundwater samples collected at depths of 75, 101, and <br /> 120 feet bgs, and CPT-3 was sampled at depths of 74, 100, and 125 feet bgs TPHg and BTEX <br /> constituents were not detected above laboratory detection limits in the groundwater samples <br /> analyzed from select depths in the CPT borings CPT-2 and CPT-3 Of the fuel oxygenates, MtBE <br /> and methanol were detected in the groundwater sample CPT-2 75 at concentrations of 2 0 and <br /> 2,700 ppb, respectively MtBE was detected in CPT-3 100 at a concentration of 6 8 ppb MtBE r <br /> and TBA were detected in CPT-3 125 at concentrations of 290 and 88, respectively <br /> In December 2002, an ozone sparge system was installed, connected to sparge wells, and <br /> brought online <br /> Groundwater has been monitored and sampled on a quarterly basis from 1991 to the present <br /> During the year of 1997, groundwater was not monitored or sampled During the second quarter <br /> groundwater flow was toward the north at a gradient of 0 002 ft/ft Maximum reported <br /> concentration of MtBE and TBA during the second quarter 2004 were 28 ppb (MW-11) and <br /> 100,000 ppb (MW-7), respectively Concentrations of MtBE, TPHg, and TBA continue to decline <br /> in site monitoring wells Further discussion of quarterly sampling is discussed below <br /> SENSTIVE RECEPTORS <br /> Also in April of 2001, GR conducted a well search and Sensitive Receptor Survey (SRS) in the '� <br />