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.. ..... . <br /> AAMKA. <br /> STANDARD PROCEDURE FOR GROUNDWATER MONITORING WELL <br /> CONSTRUCTION FOR WELLS SCREENED ACROSS THE PHREATIC SURFACE <br /> HOLLOW STEM AUGER METHOD <br /> Groundwater monitoring wells are constructed by inserting or tremming well materials <br /> through the annulus of the hollow stem auger. In general, the groundwater monitoring wells <br /> are constructed with 10 feet of screen below groundwater and 10 feet above groundwater, <br /> for a total screen length of 20 feet. Where shallow groundwater is encountered or perched <br /> water dictates otherwise, the screen is adjusted, as appropriate, to maintain a proper seal <br /> at the surface (minimum three feet) and to avoid penetrating low permeable horizons or <br /> aquicludes. Groundwater wells are installed in accordance with the conditions of the well <br /> construction permit issued by the regulatory agency exercising jurisdiction over the project <br /> site. <br /> Once the borehole has been drilled to the desired depth, approximately six inches of filter <br /> sand are tremmied to the bottom of the boring. The well screen (consisting of Schedule 40 <br /> PVC casing with 0.020-inch machine slots) and blank well casing are then inserted through <br /> the annulus of the hollow stem augers. The well screen is sandpacked by tremming the <br /> appropriate filter sand (Lonestar 2112 or No. 3 Sand) through the annulus between the <br /> casing and augers while slowly retracting the augers. During this operation, the depth of <br /> the sand pack in the auger is continuously sounded to make sure that the sand remains in <br /> the auger annulus during auger retraction to avoid short-circuiting the well. The sand pack <br /> is tremmied to approximately two feet above the screen, at which time pre-development <br /> surging is performed to consolidate the sand pack. Additional sand is added as necessary <br /> to assure that the sand pack extends a minimum of two feet above top of screen. Following <br /> construction of the sand pack, a two foot thick bentonite seal is tremmied over the sand and <br /> hydrated in place. The remainder of the borehole is backfilled with neat cement grout. The <br /> well head is then capped with a locking cap and secured with a lock to protect the well from <br /> surface water intrusion and vandalism. <br /> The well head is further protected from damage with traffic-rated well box in paved areas or <br /> locking steel riser in undeveloped areas. The protective boxes or risers are set in concrete. <br /> The details of well construction are recorded on well construction logs. <br /> Following well construction, the wells are developed in accordance with agency protocols <br /> by intermittently surging and bailing the wells. Development is determined to be sufficient <br /> once pH, conductivity and temperature stabilize to within the 10 percent of the previous two <br /> readings. <br /> Wastewater collected during development is contained in 55-gallon, DOT-approved drums <br /> and stored on-site pending laboratory results and disposal. A label is affixed to the drums <br /> indicating the contents of the drum, suspected contaminants, date of generation and the <br /> monitoring well number from which the waste water was generated. <br /> 4 <br /> F <br />