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Mr. David Johnson • -2- . 20 May 2011') <br /> Herman and Helen's Marina <br /> Monitoring well MW-2 contained the greatest concentrations of total petroleum hydrocarbons <br /> as diesel (TPHd) at 3,700,000 micrograms per liter (pg/L), a concentration that is indicative of <br /> liquid phase hydrocarbons (LPH, i.e., "free product"), and TPH as gasoline (TPHg) at 110,000 <br /> pg/L. The MRP requires "Monitoring wells with free phase petroleum product or visible sheen <br /> shall be monitored, at a minimum, for product thickness and depth to water." Based on our <br /> review of AGE's Monitoring and Sampling Procedures and field logs in the Fourth QMR, it <br /> does not appear that AGE is monitoring for LPH. Extraction well EW-1 contained the greatest <br /> concentration of tertiary butyl alcohol (TBA) at 43,000 ug/L and MW-4 contained the greatest <br /> concentration of methyl tertiary butyl ether (MTBE) at 24 pg/L. Fourth quarter TBA <br /> concentrations in EW-1 increased compared to the previous quarter. <br /> AGE performed first quarter monitoring on 30 March 2011 and depths to groundwater ranged <br /> from less than 1 foot to about 24 feet with the flow to the southeast and gradient ranging from <br /> 0.012 ft/ft under the flat portion of the Site to 0.24 ft/ft beneath the levee. AGE could not <br /> sample four wells due to a damaged well casing at MW-9; inaccessibility of MW-8 and MW-10; <br /> and insufficient groundwater in MW-13. <br /> Monitoring well MW-2 contained the greatest concentrations of TPHg and TPHd at 4,400 pg/L <br /> and 7,900 pg/L, respectively, and contained elevated concentrations of ethylbenzene, toluene, <br /> and total xylenes. Extraction well EW-1 contained the greatest concentration of TBA at <br /> 16,000 pg/L, the third consecutive quarter that H&H has detected TBA in this well. Historically, <br /> it has been absent. Monitoring well MW-4 contained the greatest concentration of MTBE at <br /> 16 pg/L. <br /> I contacted AGE to inquire whether the surface seal at MW-9 had been compromised, and for <br /> additional information regarding inaccessibility at MW-8, MW-10 and MW-12. AGE informed <br /> me by email that they do not believe the seal had been compromised when it sustained <br /> damage during construction activities. They have a flush surface completion at MW-9 but <br /> continued access requires installation of a stove-pipe completion. Alternatively, they <br /> recommend abandoning this well, which is presently covered in sediment and weeds. Wasps <br /> have infested MW-8 and MW-10 making them inaccessible. Someone parked a car over <br /> MW-12 but AGE could not find the owner to remove it before completing the monitoring event. <br /> The MRP requires H&H to sample two drainage ditch locations (DDN and DDS) quarterly, to <br /> evaluate the impact of discharge from the IRM on surface water. However, H&H discontinued <br /> use of the IRM in June 2009 and has only sampled the surface water locations sporadically. <br /> During the first quarter, AGE collected surface water samples DDN and DDS for the first time <br /> since April 2010 and the analyzed constituents were below detection limits. Both the Fourth <br /> and First QMRs recommend meeting with Central Valley Water Board staff to discuss <br /> reducing the groundwater monitoring frequency, and accelerating site closure. The First QMR <br /> recommends discontinuing surface water sampling. <br /> We have the following comments. <br /> 1. We are willing to arrange a meeting with H&H. However, our primary concern is H&H's <br /> lack of progress toward performing the ORC pilot study as discussed during our 18 May <br /> 2010 meeting and not reducing the groundwater monitoring frequency and accelerating site <br /> closure. While we may be able to revise the monitoring schedule at some sampling <br />