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Kennedy/Jenks Consultants <br /> downwards toward the valleys. The thickness of the clay liner on the bottom of the ponds is a <br /> minimum of 24 inches at the valley positions and 36 inches at the ridge positions. <br /> 2.2.3 Leachate Collection and Recovery System <br /> The floor of each surface impoundment was constructed with ridges and valleys to form the <br /> base for the LCRS. The ridges and valleys traversing the short dimension of the impoundment <br /> base are sloped at 0.4 percent to allow any liquid to drain toward northeast side of the <br /> impoundments as part of the LCRS design. Four-inch-diameter perforated polyvinyl chloride <br /> (PVC) pipes were installed on top of the clay liner within the valleys and were surrounded with <br /> filter gravel and a geotextile filter fabric wrap. The four-inch perforated pipes drain to a six inch <br /> perforated collector pipe that transports liquid to one of four LCRS sumps. <br /> Two sumps were constructed for each impoundment; one in the northwest corner and one in the <br /> southeast corner. Each sump is equipped with a ''/2-horsepower submersible pump to convey <br /> collected liquid back into the surface impoundment. Small diameter perforated pipes connected <br /> to vertical piping was installed under the synthetic liner layer to allow air to be vented to <br /> atmosphere. <br /> A free-draining granular media was placed on top of the clay liner and leachate collection piping <br /> to a depth of six inches at the ridge positions and 12 inches at the valley positions. A <br /> geomembrane drainage mat with a geo-fabric backing was placed on the clay liner of the side <br /> slopes to direct potential leakage from the side slopes to the leachate collection piping system. <br /> The LCRS system of each surface impoundment was tested at the time of installation. For the <br /> first surface impoundment constructed in 1986, testing was performed by introducing water into <br /> the air venting pipes and monitoring collection of the water in the sumps. For the second <br /> impoundment constructed in 1991, water was sprinkled onto the surface of the granular media <br /> prior to installation of the synthetic liner and retrieved from the sumps. <br /> 2.2.4 Synthetic Liner <br /> Both surface impoundments were entirely lined with a Hypalon reinforced chlorosulfonated <br /> polyethylene synthetic liner. The synthetic liner forms an impenetrable layer over the LCRS and <br /> was secured by burying the ends in an anchor trench at the top of the embankments. According <br /> to KSA, "Extensive testing conducted on Hypalon liners for use in salt gradient solar ponds <br /> indicate that Hypalon is very compatible with brine solutions and will perform very well in this <br /> application." (Kjeldsen, Sinnock&Associates 1986a). <br /> Several features are incorporated in the impoundment design to minimize the potential for <br /> leakage at the influent points. A 45-mil shroud was clamped to the inlet pipe and bonded to the <br /> liner to protect against leaking at the pipe penetration of the synthetic liner. A concrete pad four <br /> feet wide and four inches thick was constructed below the pipe inlet as a splash pad to prevent <br /> scouring. A 45-mil splash pad liner was bonded to the concrete and joined with the synthetic <br /> liner. <br /> Page 4 Work Plan for Improved Detection Monitoring Program <br /> Musco Family Olive Company, Tracy, California <br /> a -,o�o,ammpbnznzo�oam_m��r�,es.,e,"W_27_dmp�pai da..mlreporttext-09-26.doc <br />