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Velma Masterson <br /> 749 E. Charter Way, Stockton <br /> Page 2 of 3 <br /> be inadequate and cannot concur with the recommendation in the FS or lack of <br /> recommendation in the AFS . <br /> EHD also considers WP-SVE to be inadequate and cannot approve it. CGG proposes <br /> purging the wells of three pore-volumes of vapor prior to sampling. Provide EHD with <br /> details on the size of the area to be purged of three-pore volumes and how long the <br /> purging will take . The calculations should be submitted for review. It has been EHD's <br /> experience that it is common practice to collect several soil vapor samples during an <br /> extended test to analyze concentration trends over time; but a rational for collecting only <br /> one soil vapor sample per well was not provided by CGG . A consistently increasing <br /> contaminant concentration trend would be interpreted differently than stable or <br /> decreasing trends. The proposed analytical method utilizing Summa canisters and EPA <br /> Method TO-3 may be more accurate than previous results , but using historically utilized <br /> methods for sampling and laboratory analysis methods may provide data more <br /> comparable to the historical data collected from the SVE system . In reviewing our file <br /> information , EHD found only one lab report for vapor samples taken in 1997. There was <br /> no description of SVE system protocols for monitoring and sampling , or calculations <br /> showing the amount of removed contaminant mass. Submit a report to EHD by <br /> 01 March 2006 on the operation of the SVE system that includes a description of the <br /> vapor sampling protocol utilized for the SVE system , copies of all laboratory results for <br /> vapor samples and some example removed mass calculations . <br /> The WP-MW is also inadequate and not approved . The purpose of this work plan was to <br /> install a deep monitoring -well to verify the results from the CPT groundwater samples <br /> and to hopefully delineate the vertical extent of impacted groundwater. EHD had pointed <br /> out in the 27 September 2005 letter that an unsampled sand/gravel interval was <br /> identified in the CPT log at 132 to 135 feet below surface grade (bsg), which CGG did <br /> not address in the WP-MW ; the sand unit may be the deepest significant soil unit that <br /> may serve as a lateral migration pathway for contaminants. EHD considers the silty <br /> clay, clayey silt, silt and 'stiff fine grained' soil in the proposed 150 to 160 feet bsg <br /> interval to be a less likely significant lateral migration pathway for contaminants . Other <br /> potential lateral migration pathways above 100 feet bsg and below the currently <br /> monitored depths can be identified on the CPT log . The selected interval , based on the <br /> data , should be picked to optimize the value of the data to be collected from it, i .e. , <br /> delineating the vertical extent of the plume and checking a potential migration pathway, <br /> rather than merely selecting the deepest point sampled to date . It is possible that some <br /> of the analytical results for the deeper CTP groundwater samples may be the result of <br /> cross contamination of the samples . The proposed well should be located in the <br /> presumed down-gradient direction from the suspected main source area — the former <br /> UST pit. <br /> A very major problem with the WP-MW is the confusing proposed well construction <br /> details without a clarifying well diagram provided as part of the work plan . According to <br /> the WP-MW , the well is to be screened from 150 to 160 feet bsg (which would be a 10- <br /> foot screen), with "0 . 02 slotted casing in the bottom 20 feet of the well (which would be <br /> a 20400t screen ) and blank casing from 30 feet to the surface" (a 30400t blank <br /> casing? ). The work plan further states "a transitional seal will be placed from 25 to 22 <br /> feet which will consist of hydrated bentonite and that from 148 feet to the surface the <br />