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Mr. Alan Fetters and Mr. Bud -,-;nOuden -2- 17 February 2010 <br /> Aquifer Test <br /> The deep well at the former location of the supply well shall also be used to develop an <br /> estimate of horizontal and vertical hydraulic conductivity. The scope of the pump test needs to <br /> be expanded to include an extraction test from this deeper well. The location of this deep well <br /> also provides an opportunity to pilot test the extraction of polluted groundwater from the <br /> deeper groundwater zone. <br /> Therefore, in order to maximize the information obtained from this deep well, and to minimize <br /> future investigative capital expenses, this well shall be designed and installed as an extraction <br /> well and shall be included in the aquifer pump test. <br /> Shallow Soil Cleanup Objectives <br /> The cleanup objective for nitrogen in shallow soil needs to be protective of groundwater <br /> through the leaching mechanism. The objective therefore depends primariy on the depth to <br /> groundwater, the intervening soil type, and the mobility of nitrogen. Site soils are <br /> predominately silts and sands, nitrogen is expected to be distributed in the soil column from <br /> the surface to first groundwater(about 20 feet bgs) at the bulk liquid storage locations and <br /> sumps, and nitrate is miscible in water. Therefore, a cleanup goal of 100 mg/kg for nitrate (as <br /> nitrogen) in soil would be protective of groundwater quality. More site specific information <br /> regarding the vertical distribution of nitrogen and its mobility in these soils at this site could <br /> result in a less conservative soil cleanup goal for these specific areas. <br /> For example, if the vertical profile shows that nitrogen in the soil matrix is not contributing to <br /> shallow groundwater pollution, or if it is shown through leachability tests (the Waste Extraction <br /> Test using de-ionized water as the extractant) that nitrate bound on soil surfaces is not <br /> expected to completely partition to the aqueous phase, then a higher cleanup goal for nitrogen <br /> could be considered. <br /> The leachability test is described in the Central Valley Water Board Staff Report, The <br /> Designated Level Methodology for Waste Classification and Cleanup Level Determination <br /> published in October 1986, updated in June 1989. This is available on the Water Board <br /> website at http://www.waterboards.ca.gov/centralvalley/plans_policies/guidance/dlm,pdf. <br /> If the responsible parties choose to follow the Designated Level Methodology to refine the soil <br /> cleanup goal, they should propose to collect a sufficient number of soil samples to include a <br /> range of nitrogen concentrations in soil and each sample should be analyzed for both total <br /> nitrogen and for the leachable nitrogen concentrations. <br /> Summary <br /> Central Valley Water Board staff are hereby directing the responsible parties to complete the <br /> assessment, close the data gaps, and prepare for remedial design. RF Land, Inc. and Ripon <br /> Farm Service, LLC need to install an extraction well near the old supply well, expand the <br /> scope of the aquifer test to include evaluation of the horizontal and vertical hydraulic <br /> conductivity, and obtain a vertical nitrogen profile near the concrete-lined ponds. <br /> Central Valley Water Board staff conditionally concur with the revisions displayed in the <br /> 1 February 2010 Revised Addendum (attached) provided the following additions are included <br /> in the work plan: <br /> The deep monitoring well proposed at the location of the former supply well shall be <br /> designed and installed as an extraction well. <br />