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' • .NVIRONMENTAL.INC. <br /> February 24, 2012 <br /> Page 2 of 3 <br /> ' Based on existing onsite monitoring wells and hydrogeology beneath the site, the screened <br /> intervals will extend from approximately: <br /> ' 45 to 65 feet bgs for the A-zone <br /> • 95 to 110 feet bgs for the B-zone <br /> The wells will be installed using rotary sonic drilling technology. Telescopic conductor casing will <br /> be used during the drilling of B-zone wells to minimize communication between the water- <br /> bearing zones. The conductor casing will be advanced to the total depth of drilling <br /> (approximately 110 feet bgs) and removed in stages as the well is constructed. Neat cement will <br /> be placed in the well annulus as the conductor casing is removed during installation of the wells <br /> ' to maintain a seal between the water bearing zones. <br /> Each monitoring well will be constructed of 2-inch diameter schedule 40 PVC blank casing with <br /> ' 0.010-inch slotted screen. The annular space between the borehole wall and well screen will be <br /> back-filled with a silica sand filter pack to approximately two feet above the screen. A two-foot <br /> thick bentonite seal will be completed above the filter pack. The annular space above the <br /> bentonite seal will be sealed with neat cement to approximately two feet bgs. The wells will be <br /> completed with a traffic-rated metal well vault and a concrete pad installed flush to the <br /> surrounding surface. Wells not in vehicle traffic areas will be completed with a five-foot steel <br /> riser with locking lid installed approximately two feet bgs and secured in a concrete pad. Well <br /> design details are presented in Figure 2. <br /> ' Development, Purging and Sampling <br /> ' The wells will be developed by a combination of surging and bailing or pumping at least 48 hours <br /> after placing the annular seal. Development will continue until a minimum of five casing volumes <br /> of water have been removed and water quality parameters have stabilized. The water quality <br /> parameters will include oxidation-reduction potential, temperature, electrical conductivity, <br /> dissolved oxygen and pH. The newly installed monitoring wells will be gauged and sampled <br /> approximately 48 hours after development. The depth to water and total well depth will be <br /> ' gauged and low flow methodology will be used to purge and sample the wells. The water quality <br /> parameters will also be monitored and recorded during purging at a frequency of five minute <br /> intervals or greater during purging. Purging will continue until the field parameters have <br /> ' stabilized. Stabilization is considered to be achieved when three consecutive readings are <br /> within the following limits: <br /> t Parameter Stability Limit <br /> Dissolved Oxygen no greater than 20% saturation or t 10% <br /> Turbidity < 20 NTU or t 10% <br /> ' Temperature: t 0.2 °C <br /> pH: t 0.2 Standard Units <br /> Specific Conductance: t 10% of reading <br /> Once readings above have stabilized, samples will be collected using the peristaltic pump and <br /> tubing. Samples will be collected in individual sample containers provided by Calscience <br /> Environmental Laboratories (Calscience) of Garden Grove, California labeled, logged onto a <br />