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' . k` ■ KLEINFELDER <br /> 1 EXECUTIVE SUMMARY <br /> ' Musco Olive Products, Inc. has a year-round olive processing and packaging facility on <br /> approximately 320 acres of land at 17950 Via Nicolo in Tracy, California (Plate 1). Process <br /> ' water from the production of olives generates non-hazardous waste streams of water. <br /> Approximately 400,000 to 500,000 gallons per day (gpd) of wastewater are generated from the <br /> facility processes. Depending on the level of salinity of the wastewater, the facility currently <br /> applies the wastewater onto crop/grazing fields, approximately 150-acres (Plate 2), or stores the <br /> wastewater in an existing one million-gallon storage pond. The wastewater generated is <br /> ' currently regulated by two separate waste discharge requirements. Order No. 96-075 regulates <br /> the Class II Surface Impoundment which stores concentrated brine waters, and Order No. 97-037 <br /> ' regulates the land application of the less concentrated process water. A 72 million-gallon surface <br /> impoundment will be constructed for storage of the wastewater. <br /> ' Kleinfelder prepared a workplan for Musco Olive Inc. in response to requests from the Central <br /> ' Valley Regional Water Quality Control Board (RWQCB) Cleanup and Abatement Order No. 5- <br /> 00-717 (C&A 5-00-717) dated November 17, 2000. The Cleanup and Abatement Order <br /> addressed violations of Order 97-037 regarding land applications of wastewater. The exploratory <br /> ' soil borings proposed in the workplan were intended to evaluate subsurface conditions at the <br /> existing one million-gallon storage pond, the proposed 72 million-gallon storage pond(s), and the <br /> ' land application disposal fields. <br /> ' Kleinfelder drilled two soil borings, one near the one-million pond, and one near the area of the <br /> proposed seventy-two million gallon pond to assess soil and groundwater. Soil samples collected <br /> ' from the observed aquitard layers were analyzed for hydraulic conductivity and grain size <br /> analysis. Groundwater samples were analyzed for sodium, chloride, total dissolved solids, <br /> -�.... <br /> dissolved inorganic solids, and e ec nca conductance. <br /> Soil samples were collected from the deep soil borings from what was interpreted to be clay <br /> ' material. The soil samples were analyzed for hydraulic conductivity using a falling head <br /> permeameter. The soil samples collected from the deep soil boring near the 1 million gallon <br /> ' pond (TW-1) had a permeability ranging from 8.0 x 10-8 cm/sec to 9.60 x10-8 cm/sec. The soil <br /> samples collected from the proposed 72 million gallon pond (TW-2) showed a permeability of <br /> ' 9.0 x 10-6 to 4.14 x 10-7 cm/sec, typically an engineered clay liner for a pond will required a <br /> permeability of 10-6 magnitude. The clays encountered in the deep soil borings are <br /> 20-2594-03.004/2011 R447 Page I of 16 <br /> ' Copyright 2001 Kleinfelder,Inc. June 8,2001 <br />