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Mr. Benson Cuthbertson - 2 - 19 March 2013 <br /> PNA submitted the 30 March 2011 Soil Investigation Report which reported the results of <br /> 12 additional soil borings, installed to a maximum depth of 12 feet bgs, along with the <br /> results of inspection and pressure testing all remaining fuel supply lines. The Soil <br /> Investigation Report concluded that there was no on-going release of TPH, the TPH on <br /> the water table was residual from the 1996 spill, and that approximately 5,300 gallons of <br /> TPH remain in site soil and groundwater. <br /> In February 2012 PNA submitted the Light-non-aqueous Phase Liquid(LNAPL) <br /> Remedial Feasibility Study(Feasibility Study) in response to a 15 April 2011 Regional <br /> Water Board letter requesting assessment of further remedial options to enhance the <br /> rate of LNAPL recovery. The Feasibility Study reviewed existing site data and <br /> stratigraphic and hydrogeologic information obtained from a remedial investigation <br /> occurring on the former Occidental Chemical site, approximately 1000 feet to the east <br /> and downgradient of the PNA site. Although the Feasibility Study identified the <br /> Occidental remedial investigation, it did not identify the operating groundwater extraction <br /> and treatment system that is likely controlling groundwater gradient in at the PNA site. <br /> In a 5 June 2012 letter, Regional Water Board staff rejected the FS recommendation for <br /> making Monitored Natural Attenuation the preferred remedy at this site because Water <br /> Quality Objectives would not be met in a reasonable time period, and directed PNA to <br /> continue its program of skimming diesel fuel (TPHd) from the water table along with <br /> semi-annual groundwater monitoring. <br /> Free Product Removal <br /> Section 3.1.4 of the Closure Report states that free product has been removed to the <br /> maximum extent practicable. Regional Water Board staff do not concur. Since 1999, <br /> PNA has been attempting to recover diesel fuel from six 4-inch recovery wells by bailing <br /> approximately every one to two weeks. The data show that diesel was recoverable from <br /> only two to four of the wells at any time. The data also show that as recently as <br /> December 2011 over a foot of diesel fuel would accumulate in recovery wells on a <br /> weekly basis. The most recent data submitted from September 2012 shows that several <br /> inches of diesel was still present in recovery well RW-2. <br /> Regional Board staff letter of 23 April 1998 recommended using at least 6-inch diameter <br /> wells with a larger .06-inch slot size because it is more efficient to recover fuel from <br /> larger infiltration galleys. However, PNA installed 4-inch wells with a .02-inch slot size. It <br /> is Regional Water Board staffs opinion that diesel recovery could be substantially <br /> enhanced by installing larger-diameter recovery wells, installing additional recovery wells <br /> within the LNAPL plume, and either continuing the bailing program or installing <br /> automatic low flow recovery pumps. <br /> Incomplete Conceptual Site Model <br /> Section 3.1.5 of the Closure Report states that a Conceptual Site Model has been <br /> developed. Regional Water Board staff do not concur that the Conceptual Site Model is <br /> complete for the following reasons: <br /> 1. The maximum depth of investigation at the site is 17 feet bgs. Investigations to <br /> date have not defined the vertical extent of the contamination. <br />