Laserfiche WebLink
I <br /> Work Plan for Additional Assessment S E C O R <br /> ARCO Service Station 2130 <br /> Stockton, California <br /> Page 4 o 15 <br /> SOIL EVALUATION <br /> Prior to conducting a soil vapor extraction test, the residual soil contamination was <br /> evaluated for all routes of exposure in order to protect human health , safety, and the <br /> environment. Table 5 presents a comparison of the soil concentrations to San Francisco <br /> Bay Regional Water Quality Control Board Environmental Screening Levels for residential, <br /> commercial, and construction workers. None of the soil concentrations appear to pose a <br /> risk via the indoor air pathway to any of the potential populations. The only potential <br /> residential risk is dermal contact to TPH. However, this comparison does not consider <br /> degradation . These soil sample results are from 1993 and have likely declined from the <br /> original concentrations. <br /> Soils deeper than 10 feet below ground surface (bgs) impacted with xylenes and TPH could <br /> potentially pose a risk to construction workers via dermal contact. However, the cited <br /> concentrations are from 1993 and 1995 and have likely declined . <br /> PROPOSED SCOPE OF WORK <br /> The scope of work outlined in this work plan includes the installation of additional <br /> groundwater monitoring wells and the procedures for conducting a bench scale study of the <br /> potential leachability of metals as a result of oxygen injection . The objective of the <br /> additional site assessment is to provide lateral and vertical delineation of the petroleum <br /> hydrocarbon plume. The following sections describe the installation of seven groundwater <br /> monitoring wells (MW- 14 through MW-20) . <br /> Recommendations in the Site Conceptual Model included the use of periodic oxygen <br /> injection to treat the petroleum hydrocarbons in the groundwater. The January 12, 2007 <br /> SJCHED letter requested a bench scale pilot test prior to approval of this remediation <br /> technology. As requested by the SJCEHD, SECOR contacted Jim Barton with the Regional <br /> Water Quality Control Board (RWQCB) regarding procedures for conducting this test. <br /> The objective of this bench scale study is to address concerns about the possible <br /> mobilization of general minerals in soils and the creation of degradation byproducts from <br /> the chemical oxidation petroleum hydrocarbon and fuel oxygenate. The specific objective <br /> of the study is to evaluate the efficiency of oxygen injection on methyl tert butyl ether <br /> (MtBE) , benzene, toluene, ethylbenzene, and xylenes (BTEX) and total petroleum <br /> hydrocarbons as gasoline (TPHg) . <br /> Task 1 - Preliminary Field Activities <br /> Prior to conducting the subsurface investigation , a site-specific Health and Safety Plan <br /> (HASP) for use by personnel during implementation of this work plan will be prepared. The <br /> HASP will address the proposed subsurface investigation activities, and a copy of the <br /> HASP will be available on-site during field work. Subcontractors performing field activities <br /> will also be provided a copy of the HASP prior to initiating work. <br /> The required monitoring well installation permits will be obtained from San Joaquin County <br /> Environmental Health Department (SJEHD) . All locations will be marked and Underground <br /> Service Alert (USA) will be notified at least 48 hours in advance of drilling . In addition , <br /> proposed boring locations will be cleared by a private utility locator and boring locations will <br /> be cleared by hand to approximately 5-feet bgs before machine drilling is initiated. <br /> Task 2 — Soil Boring Advancement , Soil Sampling and Groundwater Monitoring Well <br /> Installation <br /> In order to evaluate the current lateral extent of fuel- related hydrocarbons, MtBE , and 1 ,2- <br /> DCA four shallow zone (screen interval 30 to 50 feet bgs) and two deeper zoned (screen <br /> interval 60 to 75 feet bgs) groundwater monitoring wells (MW-14 through MW- 19) are <br /> proposed at the approximate locations shown on Figure 3. In addition , in order to delineate <br />