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2900 - Site Mitigation Program
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PR0508387
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/26/2021 1:26:37 PM
Creation date
5/26/2021 11:23:49 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508387
PE
2960
FACILITY_ID
FA0008052
FACILITY_NAME
CONNELL MOTOR TRUCK
STREET_NUMBER
2219
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
11736029
CURRENT_STATUS
01
SITE_LOCATION
2219 N WILSON WAY
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Ms. Kerry Heckman - 2 - 4 December 2006 <br /> 2211 N. Wilson Way, Stockton <br /> groundwater to 100 feet below ground surface (ft bgs) and 80 feet laterally to the west from <br /> the Source. Another component of the Plume involves the gasoline lead scavenger <br /> 1,2-Dichloroetbane (1,2-DCA) emanating from the same Source, which has traveled deeper <br /> and farther than the gasoline and diesel-range components in the Plume, to 150 ft bgs and <br /> over twice the distance laterally than TPHg, in excess of 160 feet from the source (Figures 6 <br /> through 8) under the Site building. <br /> Maximum 302006 Report groundwater concentrations included: Total Petroleum <br /> Hydrocarbons as Gasoline (TPHg, vapor well VW-14B), 1,900,000 micrograms per Liter or <br /> ug/L; TPH as Diesel (TPHd, localized around MW-16 and near Stoddard spill location west of <br /> the Site building), 160,000 ug/L; Benzene (B), 7,400 ug/L; Toluene (T), 4,200 ug/L; <br /> Ethylbenzene (E) 810 ug/L; Xylenes (X), 5,900 ug/L; and 1,2-DCA, 330 ug/L. <br /> The results of the water levels taken from the monitoring wells in September 2006 showed that <br /> groundwater generally appeared to flow across the Site towards the west and north-northwest, <br /> from the shallow (60 ft bgs) to the deep (150 ft bgs) zones, respectively, in the aquifer. The <br /> two monitoring well sample results in the deepest monitored zones (195 and 245 ft bgs) were <br /> non-detect for all petroleum constituents. <br /> The 3Q2006 Report states that 74.5 gallons of gasoline was removed by SVE from the soil in <br /> the Source area from June through September of 2006. The SVE has removed approximately <br /> 3,088 gallons of gasoline since startup in July 2005. The SVE soil remediation and natural <br /> attenuation appear to be responsible for a reduction in the vertical and lateral extent of the <br /> groundwater plume; however the higher concentrations of pollution are persisting in the <br /> shallow zones near the Source. Air sparging near the Source, in conjunction with SVE, will be <br /> tested in a pilot study as discussed above. <br /> Monitoring and Reporting Program No. R5-2005-0827 (MRP) states in part that: <br /> "The Dischargers shall not implement any changes to this MRP unless and until a revised <br /> MRP is issued by the Executive Officer or until Regional Board staff approve those changes in <br /> writing." The 3Q2006 Report recommends continued groundwater monitoring with <br /> modifications to the MRP, which would result in a cost savings of fifty percent for analyses <br /> currently not required to monitor the groundwater plume. Specifically, the 3Q2006 Report <br /> recommends the following analyses reduction- <br /> 1. <br /> eduction:1. Sample for only 1,2-DCA in wells where other petroleum constituents have not been <br /> detected after multiple sampling events; <br /> 2. Removal of TPH as Stoddard Solvent (TPH-ss) from the list of analyses for all wells <br /> (TPHd analyses to continue as stated in number 3 below). Note that this reduction is <br /> already authorized as Footnote 2 of the Table on Page 3 of the MRP, and <br /> 3. Removal of TPHd from the list of analyses in wells that have not reported TPHd after <br /> multiple sampling events. <br /> Data from 16 quarters of groundwater monitoring show that the proposed reductions would not <br /> affect the data quality or produce data gaps that might require an additional investigation prior <br /> to completion of remedial action. Regional Board staff agrees with the recommendation and <br /> approves the changes in the MRP effective immediately, to be followed by a new MRP with a <br /> revised table on page 3 for sample analyses at a later date. <br />
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