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CAMBRIA <br /> STANDARD FIELD PROCEDURES FOR MONITORING WELL INSTALLATIONS <br /> This document describes Cambria Environmental Technology's standard field methods for drilling,Installing, <br /> developing and sampling groundwater monitoring wells These procedures are designed to comply with <br /> Federal,State and local regulatory guidelines Specific field procedures are summarized below <br /> Well Construction and Surveying <br /> Groundwater monitoring wells are installed in soil borings to monitor groundwater quality and determine the <br /> groundwater elevation,flow direction and gradient Well depths and screen lengths are based on groundwater <br /> depth, occurrence of hydrocarbons or other compounds in the borehole, stratigraphy and State and local <br /> regulatory guidelines Well screens typically extend 10 to 15 feet below and 5 feet above the static water level <br /> at the time of drilling However,the well screen will generally not extend into or through a clay layer that is at <br /> least three feet thick <br /> Well casing and screen are flush-threaded,Schedule 40 PVC Screen slot size varies according to the sediments <br /> screened,but slots are generally 0 010 or 0 020 inches wide A rinsed and graded sand occupies the annular <br /> space between the boring and the well screen to about one to two ft above the well screen A two feet thick <br /> hydrated bentonite seal separates the sand from the overlying sanitary surface seal composed of Portland type <br /> I,II cement <br /> Well-heads are secured by locking well-caps inside traffic-rated vaults finished flush with the ground surface A <br /> stovepipe may be installed between the well-head and the vault cap for additional security The well top-of- <br /> casing elevation is surveyed with respect to mean sea level and the well is surveyed for horizontal location with <br /> respect to an onsite or nearby offsite landmark <br /> Well Development <br /> Wells are generally developed using a combination of groundwater surging and extraction Surging agitates the <br /> groundwater and dislodges fine sediments from the sand pack After about ten minutes of surging,groundwater <br /> is extracted from the well using bailing,pumping and/or reverse air-lifting through an eductor pipe to remove <br /> the sediments from the well Surging and extraction continue until at least ten well-casing volumes of <br /> groundwater are extracted and the sediment volume in the groundwater is negligible This process usually <br /> occurs prior to installing the sanitary surface seal to ensure sand pack stabilization If development occurs after <br /> surface seal installation, then development occurs 24 to 72 hours after seal installation to ensure that the <br /> Portland cement has set up correctly <br /> All equipment is steam-cleaned prior to use and air used for air-lifting Is filtered to prevent oil entrained in the <br /> compressed air from entering the well Wells that are developed using air-lift evacuation are not sampled until <br /> at least 24 hours after they are developed <br /> Groundwater Sampling <br /> Depending on local regulatory guidelines,three to four well-casing volumes of groundwater are purged prior to <br /> sampling Purging continues until groundwater pH, conductivity, and temperature have stabilized <br /> Groundwater samples are collected using bailers or pumps and are decanted into the appropriate containers <br /> supplied by the analytic laboratory Samples are labeled,placed in protective foam sleeves,stored on crushed <br /> ice at or below 4°C,and transported under chain-of-custody to the laboratory Laboratory-supplied trip blanks <br /> accompany the samples and are analyzed to check for cross-contamination An equipment blank may be <br /> • analyzed if non-dedicated sampling equipment is used <br /> F\PROCEDURES\TEMPLATE\VECTOR WORKS TEMP1_ATES\SOPSIGWMONW£4[S CORRECTED FONT VERSION Doc Page 1 of 1 <br />